DSHW-2024-007121

ATTACHMENT 10A

THERMAL TREATMENT UNIT
ECOLOGICAL RISK ASSESSMENT

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Contents
ACRONYMS AND ABBREVIATIONS 10A-4
1.0 Introduction ............................................................................................................ 10A-6
1.1 Project Background ............................................................................................ 10A-6
1.2 Approach ............................................................................................................ 10A-6
1.3 Current Evaluation ............................................................................................. 10A-7
2.0 Problem Formulation ............................................................................................ 10A-7
2.1 Environmental Setting ........................................................................................ 10A-7
2.2 Fate and Transport ............................................................................................. 10A-8
2.3 Mechanisms of Ecotoxicity ................................................................................ 10A-8
2.4 Complete Exposure Pathways ............................................................................ 10A-8
2.5 Summary of Available Site-Specific Data ......................................................... 10A-9
2.6 Identification of Contaminants of Potential Ecological Concern ...................... 10A-9
2.7 Measures of Exposure and Effects ..................................................................... 10A-9
2.7.1 Assessment Endpoints ............................................................................ 10A-9
2.7.2 Testable Hypotheses ............................................................................ 10A-12
2.7.3 Measurement Endpoints ....................................................................... 10A-13
3.0 Exposure Assessment ........................................................................................... 10A-13
3.1 Exposure Estimates for Receptors Exposed in Lower Order
Trophic Guilds .............................................................................................. 10A-14
3.2 Exposure Estimates for Higher Order Trophic Guilds ..................................... 10A-14
4.0 Ecological Effects Assessment ............................................................................. 10A-16
4.1 Screening for Ecological Effects from Direct Exposure
to Contaminated Soil ..................................................................................... 10A-16
4.2 Screening Toxicity Reference Values for Wildlife .......................................... 10A-16
5.0 Initial Risk Characterization .............................................................................. 10A-17
5.1 Terrestrial Plants .............................................................................................. 10A-18
5.2 Soil Invertebrates ............................................................................................. 10A-19
5.3 Mammals .......................................................................................................... 10A-20
5.4 Birds ................................................................................................................. 10A-21
6.0 Refined Risk Characterization ........................................................................... 10A-23
6.1 Risk Characterization Refinements .................................................................. 10A-23
6.1.1 Background Screen .............................................................................. 10A-23
6.1.2 Lowest Observed Effect Concentrations and Levels ........................... 10A-23
6.1.3 Point-by-Point Exceedance Evaluation ................................................ 10A-24
6.1.4 Exposure Point Concentrations ............................................................ 10A-25
6.1.5 Samples from Within Habitat .............................................................. 10A-25
6.1.6 Area Use Factors .................................................................................. 10A-25
6.1.7 Bioaccumulation Factors ...................................................................... 10A-26
6.2 Refined Risk Characterization ......................................................................... 10A-26
6.2.1 Background Screen .............................................................................. 10A-26
6.2.2 Terrestrial Plants .................................................................................. 10A-27
6.2.3 Soil Invertebrates ................................................................................. 10A-28
6.2.4 Mammals .............................................................................................. 10A-30
6.2.5 Birds ..................................................................................................... 10A-33
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7.0 Uncertainties ......................................................................................................... 10A-35
7.1 Chemical Uncertainties for Plants ................................................................ 10A-37
7.2 Chemical Uncertainties for Soil Invertebrates .............................................. 10A-37
7.3 Uncertainties for Mammals ........................................................................... 10A-37
7.4 Uncertainties for Birds .................................................................................. 10A-38
8.0 Conclusions ........................................................................................................... 10A-38
8.1 Background Comparison .............................................................................. 10A-38
8.2 Plants ............................................................................................................. 10A-38
8.3 Soil Invertebrates .......................................................................................... 10A-39
8.4 Mammals....................................................................................................... 10A-40
8.5 Birds .............................................................................................................. 10A-41
8.6 Possible Actions to Reduce Potential Risks ................................................. 10A-42
9.0 References ............................................................................................................. 10A-44

Tables
1 Environmental Fate and Transport of Detected Chemicals
2 Mechanisms of Ecotoxicity
3 Summary Statistics for Combined Historical and Current Surface Soil Samples from
the TTU at the UTTR
4 Linkage Between Assessment and Measurement Endpoints
5 Rationale for Selection of Wildlife Receptors of Concern
6 Exposure Parameters for Selected Wildlife Receptors of Concern
7 Area Use Factors for Selected Receptors
8 Chemical Uptake for Dietary Items
9 Regression Equations for Chemical Biotransfer Factors
10 Ecological Screening Benchmarks for Terrestrial Plants Exposed to Soil
11 Ecological Screening Benchmarks for Invertebrates Exposed to Soil
12 Toxicity Reference Values Considered for Mammalian Wildlife Receptors
13 Toxicity Reference Values Considered for Avian Wildlife Receptors
14 Direct Toxicity Screening for Plants Exposed to Soil Using Maximum Detected
Concentrations
15 Direct Toxicity Screening for Invertebrates Exposed to Soil Using Maximum
Detected Concentrations
16 Initial Risk Estimation for Wildlife Exposed to Site Soils
17 Summary of Chemicals of Potential Concern after the Screening Risk Assessment
18 Sample Designations for Surface Soil Collected from the TTU at the UTTR
19 Summary Statistics for Combined Historical and Current Surface Soil Samples from
Potential Habitat Locations at the TTU at the UTTR
20 Refined Chemical Biotransfer Factors for Inorganics and Selected Organics
21 Wilcoxon Rank Sum Comparison of Inorganics in TTU Soils to the Background
Concentrations
22 Summary of the Refined Screening Evaluation for Plants
23 Summary of the Refined Screening Evaluation for Plants within Ecological Habitat
24 Summary of the Refined Screening Evaluation for Soil Invertebrates
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25 Summary of the Refined Screening Evaluation for Soil Invertebrates within
Ecological Habitat
26 Refined Risk Estimates for Wildlife Exposed to Site Soils
27 Refined Risk Estimation for Wildlife Exposed to Site Soils Within Habitat Areas
28 Summary of Chemicals of Potential Concern after the Refined Screening Risk
Assessment
Figures
1 Terrestrial Food Web Model
2 Ecological Conceptual Site Model
3 TTU Site Map
Appendices
A Descriptions of Studies Used to Calculate NOAELs and LOAELs
B Background Soils Analysis
C 2022 Ecological Risk Screen Evaluation
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Acronyms and Abbreviations
AUF area use factor
BAF bioaccumulation factor
BCF bioconcentration factor
COPEC contaminant of potential ecological concern
EPA U.S. Environmental Protection Agency
EPC exposure point concentration
ERA ecological risk assessment
HAFB Hill Air Force Base
HI hazard index
HQ hazard quotient
LD lethal dose
LOAEL lowest observed adverse effect level
LOEC lowest observed effect concentration
NOAEL no observed adverse effect level
NOEC no observed effect concentration
OB/OD open burn/open detonation
ORNL Oak Ridge National Laboratory
PAH polycyclic aromatic hydrocarbon
PCB polychlorinated biphenyl
RCRA Resource Conservation and Recovery Act
SLERA screening-level ecological risk assessment
SVOC semi-volatile organic compound
TCE Trichloroethylene
TPH total petroleum hydrocarbons
TRV toxicity reference value
TSD Treatment, Storage, and Disposal
TTU Thermal Treatment Unit
UCL upper confidence limit
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UTTR Utah Training and Test Range
VOC volatile organic compound
WRS Wilcoxon Rank Sum

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ECOLOGICAL RISK SCREEN
1.0 Introduction
In 1987, Hill Air Force Base (HAFB) applied for a Treatment, Storage, and Disposal (TSD)
facility permit for the Thermal Treatment Unit (TTU) located at the Utah Test and Training
Range (UTTR). The Utah Department of Environmental Quality (UDEQ) issued the final
permit February 13, 2003, and reissued the permit September 13, 2013. Several attachments
listed in the permit are to be updated and resubmitted to the State. An ecological risk
assessment (ERA) is one of those required attachments. This risk assessment must be
reviewed every fifth calendar year after issuance of the Permit (Section II.F.2 of the Permit)
and updated if needed. A screening-level ecological risk assessment (SLERA) was completed
and submitted in 2005 (CH2M HILL, 2005) with subsequent evaluations in 2007, 2009,
2011, 2013, and 2018 (CH2M HILL, 2007, 2009, 2011, 2013, and 2018).
The screening-level ecological risk assessment (SLERA) uses procedures outlined in the
Ecological Risk Assessment Guidance for Superfund: Process for Designing and Conducting
Ecological Risk Assessments (U.S. Environmental Protection Agency [EPA], 1997) and
incorporates site data collected in 2019 and 2021.
The risk assessment is conducted in two parts. The first is an initial, conservative screen
using maximum concentrations and no-effect levels (to differentiate between analytes that
clearly present no risk and analytes that may present a risk). The second is a refined screen in
which more realistic exposure and effects assumptions are employed to better define whether
analytes that failed the initial screen require additional evaluation. Where the potential for
risks could not be excluded for contaminants of potential ecological concern (COPECs) in
the refined analysis, a further step was made where only the samples collected from
ecological habitat areas, excluding the open burn/open detonation (OB/OD) areas, were
characterized. All other assumptions and calculations remained the same as in the refined
analysis.
1.1 Project Background
The Integrated Natural Resources Management Plan, Hill Air Force Base (Blood, 2001) was
used as a reference document during the development of the SLERA for the TTU. Marcus
Blood (primary author of Integrated Natural Resources Management Plan, Hill Air Force
Base) reviewed and approved the Draft Ecological Screening Evaluation for the Utah Test
and Training Range-North before it was sent to the State for comment. In addition, Marcus
Blood accompanied CH2M HILL staff on a site visit to discuss receptor selection and site
goals.
1.2 Approach
The primary guidance utilized in completing the SLERA is the Ecological Risk Assessment
Guidance for Superfund (EPA, 1997). The initial assessment of the SLERA is consistent with
and focuses on the first two steps outlined in the guidance, and the refined risk evaluation
begins the initial part of Step 3 as outlined in the guidance. This SLERA is also consistent
with the following guidance documents:
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● Framework for Ecological Risk Assessment (EPA, 1992)
● Ecological Risk Assessment Guidance for Superfund: Process for Designing and
Conducting Ecological Risk Assessments (EPA, 1997)
● Final Guidelines for Ecological Risk Assessment (EPA, 1998)
● ECO Updates, Volume 1, Numbers 1 through 5 (EPA, 1991a; 1991b; 1992a; 1992b;
and 1992c)
● ECO Updates, Volume 2, Numbers 1 through 4 (EPA, 1994a; 1994b; 1994c; and
1994d)
● ECO Updates, Volume 3, Numbers 1 and 2 (EPA, 1996a and 1996b)
● Final Guidelines for Ecological Risk Assessment (EPA, 1998)
● Ecological Risk Assessment and Risk Management Principles for Superfund Sites
(EPA, 1999)
● The Role of Screening-Level Risk Assessments and Refining Contaminants of Concern
in Baseline Ecological Risk Assessments (EPA, 2001a)
Ecological risks were evaluated based on conservative assumptions, utilizing the maximum
media concentration. Maximum non-detected concentrations were also screened to determine
the potential for risk due to analytes with concentrations below detection limits. Failure to
pass the screening assessment does not indicate the presence of risk. Rather, these results
indicate that available data are insufficient to support a conclusion that ecological risks are
absent and further evaluation may be required.
The results of this SLERA are intended for use to determine whether treatment activities at
the TTU site have the potential to adversely affect ecological receptors at the site. Soil data
collected from set locations on an annual basis at the completion of each set of
burns/detonations (i.e., at the end of each sampling season) will continue to be added to the
existing SLERA data. These combined data will be used to update the SLERA as required by
the Permit. As the monitoring database develops, concentrations in soil and site activity (i.e.,
volume of material destroyed) can be associated to estimate future contaminant levels, and
predictive models of risks may be developed based on previously existing trends.
1.3 Current Evaluation
This SLERA was originally completed in 2005 and incorporated into the Permit in 2006.
Evaluations of the SLERA were conducted in 2007, 2009, 2011, 2013, 2018, and 2022. The
2022 Ecological Risk Screen Evaluation is attached as Appendix C. It summarizes the
findings of the previous evaluations and incorporates new sampling data acquired since the
initial SLERA was conducted.
2.0 Problem Formulation
2.1 Environmental Setting
The TTU is strictly an arid upland site, and no wetlands are present at the location. In
addition, no state or federal special status species are known to use the site. Two soil types
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exist at the TTU. The majority of the soils at the TTU are comprised of the Timpie-Tooele
complex. Outlying areas near the southeast corner of the TTU contain the Amtoft-Rock
outcrop complex. Further discussion of land use and the location of areas for those uses are
presented in the Integrated Natural Resource Management Plan for Hill AFB (Blood, 2001).
Specific details regarding the ecological resources at the site are also provided in the same
document.
Samples were collected from within OB/OD areas that do not contain plants or wildlife
habitat in addition to areas surrounding the OB/OD areas that do contain potential habitat for
wildlife.
2.2 Fate and Transport
Analytes may be mobile in the environment through various pathways that are dependent on
individual chemical properties. A summary of the fate mechanisms and transport processes
for detected chemicals at the TTU is presented in Table 1.
2.3 Mechanisms of Ecotoxicity
The potential for adverse effects to ecological receptors in the environment is a function of
the chemical exposure (dose) and the mechanism of toxicity for each chemical or class of
chemicals with similar modes of action. The mechanisms of toxicity for inorganic, organic
analytes, and explosives detected in on-site soils are summarized and presented in Table 2.
2.4 Complete Exposure Pathways
An exposure pathway is the course that an analyte takes from a source to an organism
(receptor). For an exposure to occur, complete exposure pathways must exist. Ecological
resources at the TTU site could potentially be exposed to analytes through different exposure
routes. Several trophic guilds have been identified as having complete exposure pathways to
site-related contaminants in soil. Eight of these guilds were identified for evaluation in this
screening assessment. Figure 1 presents a food web diagram indicating complete exposure
pathways for the site. The primary exposure pathways consist of the following:
● Direct exposure to contaminants in site soils
● Ingestion of prey items that have accumulated site contaminants
● Incidental ingestion of soil

Direct exposure occurs primarily for plants, insects, and burrow-dwelling birds and
mammals. Second-order guilds and higher receive exposure primarily through ingestion of
prey and incidental soil. Figure 2 is a conceptual model indicating the exposure pathways
evaluated for each receptor guild. Samples originating within OB/OD areas do not represent
media with a complete exposure pathway for wildlife, as the surface is barren and provides
no habitat for ecological receptors. However, all samples collected from the TTU area,
including those from the OB/OD areas, were evaluated in this SLERA as a conservative
measure of exposure.
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2.5 Summary of Available Site-Specific Data
Data used for this risk assessment included historical data and data collected in 2019 and
2021. Summary statistics for the site data used in this screening assessment are shown in
Table 3. As part of the initial, conservative screen, the maximum detected concentration from
this data set was used as an exposure point concentration (EPC), the representative
concentration for exposure estimates to plants, soil invertebrates, birds, and mammals. Half
of the maximum detection limit was evaluated as the EPC for analytes with concentrations
below detection limits in all samples. In the refined screen, exposure for plants and soil
invertebrates was evaluated on a point-by-point basis, whereas exposure for wildlife was
calculated as the best statistical estimate of an upper bound on the average exposure
concentrations, in accordance with EPA guidance for statistical analysis of monitoring data
(EPA, 1989; EPA, 2002).
2.6 Identification of Contaminants of Potential Ecological Concern
COPECs in soil were identified following guidance presented in the Ecological Risk
Assessment Guidance for Superfund (EPA, 1997). All inorganic and organic chemicals
detected in soil were retained as COPECs for the initial conservative screen. In addition, to
determine the adequacy of analytical detection limits, the maximum non-detected
concentration of any analyte that was not detected in any sample was screened. Analytes
(either detected or not detected) that lacked screening values were retained as uncertainties.
Chemicals considered to be essential nutrients (calcium, chloride, potassium, and sodium)
were excluded from the risk evaluation because these essential nutrients have low toxicity,
especially by the dermal and inhalation intake routes. Additionally, general chemical
parameters used for the nature and extent of contamination evaluation (e.g., sulfate) were
excluded from the risk evaluation due to a lack of toxicity values and expected low toxicity
associated with exposures to these chemicals.
2.7 Measures of Exposure and Effects
Evaluation of ecological risks requires the definition of measures that will be considered.
These are termed measures of exposure and effects (EPA, 1998) and consist of assessment
and measurement endpoints.
2.7.1 Assessment Endpoints
Assessment endpoints describe the environmental resources to be protected and help to focus
the SLERA on the most relevant trophic guilds and receptors for evaluation. Assessment
endpoints for the site are described below and presented in Table 4. At this site, they are
developed to protect ecological resources, i.e., plants (primary producers) in the terrestrial
environment and the prey of wildlife communities that might come in contact with
contamination on the site.
Assessment endpoints and representative receptors for the TTU were selected based on one
or more of the following criteria:
● Receptor is a special-status species (e.g., federally listed as threatened or endangered)
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● Receptor has a small home range
● Receptor is representative of an ecological guild
● Receptor is susceptible to bioaccumulation or biomagnification of COPECs (e.g.,
higher trophic-level predators)
● Receptor is likely to be exposed to contaminants
● Receptor occurs at the site
● Receptor is known or suspected to be sensitive to contaminants
● Receptor has a small body size such that food ingestion (and exposure) is maximized
● Receptor has a diet composition representing high proportions of food types
representing specific bioaccumulation pathways (i.e., plants, soil invertebrates, or
vertebrates) such that pathway-specific exposure and risk are maximized
For purposes of this screening-level assessment, current conditions are assumed to continue
into the future and assessment endpoints apply under current and future scenarios. Eight
assessment endpoints were identified to protect the following components of terrestrial
habitats at the site:
1. Terrestrial plant community
2. Soil invertebrate community
3. Herbivorous mammals
4. Insectivorous mammals
5. Carnivorous mammals
6. Herbivorous birds
7. Insectivorous birds
8. Carnivorous birds
Table 5 documents the applicable selection criteria for each of the eight assessment endpoints
(and their associated representative receptor), which are also listed below. No resident special
status or federal sensitive species were identified at the site (Blood, 2001) and are, therefore,
not specifically considered in this SLERA. The eight assessment endpoints are discussed
below.
1. Protection of the terrestrial plant community from direct toxic effects on survival,
reproduction, and growth due to chemicals in soil.
The first assessment endpoint reflects the potential presence of elevated concentrations of
chemicals in site soils and the bioavailability, accumulation, and direct toxicity of chemicals
to plants. The plant community is important as a component of habitat (cover and breeding
sites) and as a food source for wildlife.
2. Protection of the soil invertebrate community from direct toxic effects on survival,
reproduction, and growth due to chemicals in soil.
The second assessment endpoint is based on the potential presence of elevated concentrations
of chemicals in site soils, and the bioavailability, accumulation, and direct toxicity of
chemicals to the soil invertebrate community. The soil invertebrate community is an
important component of the terrestrial ecosystem at the site. It contributes to soil conditions
that promote plant growth and maintenance of the terrestrial plant community and provides
food for wildlife.
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3. Protection of populations of herbivorous small mammals from toxic effects on
survival, reproduction, and growth due to chemicals in soil and plants.
The third assessment endpoint addresses the exposure of herbivorous small mammal
populations to elevated concentrations of chemicals in site soils and waste materials and
indirectly through consumption of plants. These animals are important components of the
wildlife community, and serve as prey for higher trophic-level carnivorous birds and
mammals. They may be sensitive to adverse effects on survival, reproduction, and growth
from exposure to contaminants in soil and plants that live in site soils.
4. Protection of populations of insectivorous small mammals from toxic effects on
survival, reproduction, and growth due to chemicals in soil and invertebrates.
The fourth assessment endpoint addresses the exposure of insectivorous small mammal
populations to elevated concentrations of chemicals in site soils and waste materials and
indirectly through consumption of terrestrial invertebrates. These animals are important
components of the wildlife community, and serve as prey for higher trophic-level
carnivorous birds and mammals. They may be sensitive to adverse effects on survival,
reproduction, and growth from exposure to contaminants in soil and invertebrates that live in
site soils.
5. Protection of populations of upper trophic-level species of carnivorous mammals
from toxic effects on survival, reproduction, and growth due to chemicals in soil and
prey.
The fifth assessment endpoint addresses the exposure of top-level carnivorous mammals to
elevated concentrations of contaminants in site soils and indirectly through consumption of
invertebrates and lower trophic-level vertebrate prey organisms that live on the site. These
mammals are susceptible to uptake and direct toxic effects on survival, reproduction, and
growth from exposure to contaminants in soil and bioaccumulation and related toxic effects
of contaminants in invertebrates, small mammals, and birds that live on the site.
6. Protection of populations of herbivorous birds from toxic effects on survival,
reproduction, and growth due to chemicals in soil and plants.
The sixth assessment endpoint addresses the exposure of herbivorous bird populations to
elevated concentrations of chemicals in site soils and waste materials and indirectly through
consumption of plants. These animals are important components of the wildlife community
and serve as prey for higher trophic-level carnivorous birds and mammals. They may be
sensitive to adverse effects on survival, reproduction, and growth from exposure to
contaminants in soil and plants that live in site soils.
7. Protection of populations of insectivorous birds from toxic effects on survival,
reproduction, and growth due to chemicals in soil and prey.
The seventh assessment endpoint addresses the exposure of insectivorous birds to elevated
concentrations of site contaminants in soils and indirectly through consumption of
invertebrates and other material. These animals are primarily insectivorous, but may
consume some plant material, and are important components of the wildlife community.
They serve as prey for higher trophic-level carnivorous birds and mammals. They may be
sensitive to toxic effects on survival, reproduction, and growth from exposure to
contaminants in soil, invertebrates, and plants that live in site soils.
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8. Protection of populations of wide-ranging carnivorous birds from toxic effects on
survival, reproduction, and growth due to chemicals in soil, plants, and prey.
The eighth assessment endpoint addresses the exposure of carnivorous birds to elevated
concentrations of contaminants in site soils and indirectly through consumption of small
mammals and reptiles and lower that live on and adjacent to the site. These vertebrates are
susceptible to uptake and direct toxic effects on survival, reproduction, and growth from
exposure to contaminants in soil and sediment, and bioaccumulation and related toxic effects
from exposure to contaminants.
Reptiles were not selected as assessment endpoints for the TTU. Although they are present at
the site, of interest and worthy of protection, both data and methods to estimate exposure and
to evaluate toxicity are limited. As a consequence, reptiles are assumed to be protected if
other vertebrate wildlife assessment endpoints are protected. In addition, no special status
species were present at the TTU site; thus, they are not included among the final assessment
endpoints.
2.7.2 Testable Hypotheses
The following paragraphs present the testable hypotheses for the assessment endpoints
described above and the refined measurement endpoints described below. The benchmarks
mentioned here represent measures of effects and refer to promulgated standards and
published ecological screening benchmark values that, when available, represent the no-
effect level and lowest-effect level for the representative ecological receptors.
The following hypotheses are related to exposure to COPECs in soils at the site:
● The concentrations of COPECs in soil are not greater than soil benchmarks protective
of plants (Assessment Endpoint No. 1).
● The concentrations of COPECs in soil are not greater than soil benchmarks protective
of soil invertebrates (Assessment Endpoint No. 2).
● The concentrations of chemicals in soil and biota are not sufficient to cause direct
toxic effects, reduced growth, or reproductive impairment in populations of
herbivorous small mammals that inhabit or forage at the site (Assessment Endpoint
No. 3).
● The concentrations of chemicals in soil and biota are not sufficient to cause direct
toxic effects, reduced growth, or reproductive impairment in populations of
insectivorous small mammals that inhabit or forage at the site (Assessment Endpoint
No. 4).
● The concentrations of chemicals in soil and biota are not sufficient to cause direct
toxic effects, reduced growth, or reproductive impairment in populations of
carnivorous mammals that inhabit or forage at the site (Assessment Endpoint No. 5).
● The concentrations of chemicals in soil and biota are not sufficient to cause direct
toxic effects, reduced growth, or reproductive impairment in populations of
herbivorous birds that inhabit or forage at the site (Assessment Endpoint No. 6).
● The concentrations of chemicals in soil and biota are not sufficient to cause direct
toxic effects, reduced growth, or reproductive impairment in populations of
insectivorous birds that inhabit or forage at the site (Assessment Endpoint No. 7).
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● The concentrations of chemicals in soil and biota are not sufficient to cause direct
toxic effects, reduced growth, or reproductive impairment in populations of
carnivorous birds that inhabit or forage at the site (Assessment Endpoint No. 8).
2.7.3 Measurement Endpoints
Measurement endpoints are ecological characteristics related to an assessment endpoint by
the route of exposure and mechanism of toxicity; they are used in the evaluation of testable
hypotheses developed for each assessment endpoint (EPA, 1997). Measurement endpoints
for the site are described below and presented in Table 4.
Measures of exposure can be an EPC of a chemical in an environmental medium or food
item, or a related dose estimate. In the initial screening assessment, maximum detected or
non-detected (if all samples were non-detects) concentrations were used as the EPC for all
receptors. A point-by-point evaluation of all analytes retained from the initial screen was
conducted for immobile receptors in the refined screening assessment. For mobile receptors
(i.e., birds and mammals), the EPC was represented by the upper confidence limit (UCL) 95
(UCL95) for each retained analyte.
Measures of effects include media-specific ecological benchmarks and toxicity reference
values (TRVs). Because site-related chemicals can induce ecotoxicological effects in
exposed receptors if present at sufficiently high concentrations, ecotoxicity-based
benchmarks and TRVs are also measurement endpoints. In the initial screen, TRVs were
represented by literature-based, no observed effect concentrations (NOECs) and no observed
adverse effect levels (NOAELs). In the refined screen, NOECs and NOAELs as well as
lowest observed effect concentrations (LOECs) and lowest observed adverse effect levels
(LOAELs) were used.
Direct comparison of the EPC of a chemical to an ecotoxicity-based benchmark for plants
and invertebrates provides a measure of the possible effects attributable to direct exposure. If
the EPCs fall below the concentration benchmarks estimated to be protective of direct
toxicity, and if chemicals are not bioaccumulative, then it can be inferred that no adverse
ecological effect is likely to occur. For mammals and birds, a food-chain exposure is
calculated and compared to exposure dose-based TRVs. If the food-chain exposure doses fall
below the NOAEL-based TRVs, then it can be inferred that no adverse effect is likely to
occur through indirect (food-chain) exposure. If the calculated doses fall above the NOAEL-
based TRV but below the LOAEL-based TRV, it is uncertain whether individuals would be
adversely affected, and population-level effects are unlikely.
3.0 Exposure Assessment
This section provides the assumptions and equations used for developing initial exposure
estimates for the receptors selected to represent the trophic guilds potentially exposed at this
site. These estimates are used in the risk calculations developed for identifying contaminants
requiring further evaluation.
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3.1 Exposure Estimates for Receptors Exposed in Lower Order Trophic Guilds
Less mobile, lower trophic-level organisms (plants and invertebrates) are exposed to more
localized concentrations of contaminants than are higher trophic-level receptors. As a
measure of conservatism for the initial screen, potential toxicity of site-related chemicals to
these receptors was evaluated by using the maximum detected concentration as the EPC, the
concentration to which receptors are assumed to be exposed. The EPC used for plants and
soil invertebrates included data from the top 6 inches. The highest concentrations of COPECs
are expected to reside at or near the soil surface due to aerial deposition of potential
contaminants at the TTU. Precipitation at the site is limited, resulting in limited infiltration.
Assuming exposure for plants to be represented by concentrations in the top 6 inches of soil
is both representative and protective. For these trophic guilds, it was also conservatively
assumed that chemicals in sampled media are 100 percent bioavailable and that they remain
at a steady concentration (i.e., decomposition rates are not considered).
3.2 Exposure Estimates for Higher Order Trophic Guilds
Selected receptor species were chosen to represent the bird and mammal feeding guilds that
are expected at the site. These include the Ord’s kangaroo rat (Dipodomys ordii),
Townsend’s ground squirrel (Spermophilus townsendii), black-tailed jackrabbit (Lepus
californicus), Northern grasshopper mouse (Onychomys leucogaster), pronghorn
(Antilocapra americana), coyote (Canis latrans), sage sparrow (Amphispiza belli),
loggerhead shrike (Lanius ludovicianus), western meadowlark (Sturnella neglecta), and
burrowing owl (Speotyto cunicularia). The species-specific exposure parameters used to
estimate wildlife exposure doses include EPCs, body weight, food intake rate, diet
composition, and percent of diet as soil. The exposure factor parameters and dietary
compositions used for each bird and mammal receptor are provided in Table 6. The sources
of these parameters for each of the selected endpoint species for the site include the Wildlife
Exposure Factors Handbook (EPA, 1993), Oak Ridge National Laboratory's Toxicological
Benchmarks for Wildlife (Sample et al., 1996), Oak Ridge National Laboratory's Methods
and Tools for Estimation of the Exposure of Terrestrial Wildlife to Contaminants (Sample et
al., 1997), and other available studies (as cited). In some cases, dietary compositions were
simplified by lumping comparable food types to facilitate calculation of exposure estimates.
Lumping allows for the use of existing bioaccumulation models to estimate COPEC
concentrations in food items. Data from the top 6 inches were used to calculate the EPC for
incidental media ingestion of all receptors and for exposure to prey items. Assuming
exposure for burrowing animals is represented by concentrations in the top 6 inches of soil is
both representative and protective because the release mechanism at the TTU is aerial
deposition and precipitation is limited. Thus, infiltration will be limited, resulting in the
highest concentrations remaining at the surface.
For the initial screen, the most conservative exposure assumptions were used. These
assumptions included the use of maximum exposure concentrations, 100 percent site use, and
100 percent bioavailability of analytes. As a conservative measure of dietary exposure to
contaminants, it was also assumed that 100 percent of the receptor diet was obtained from the
primary food group.
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For the refined screen, biologically more realistic assumptions were employed. These
included the use of the 95 percent UCL as the EPC and area use factors (AUFs—weighting
site use as a fraction of home-range size). AUFs based on species-specific average home
range values are presented in Table 7. Allometric equations based on average body weights
were used to estimate food ingestion rates. The taxonomically most specific allometric
equation that was appropriate was used in all cases (e.g., the equation for passerines was used
for the northern shrike instead of the equation for all birds).
Site-specific concentrations of contaminants in wildlife foods were not available for the TTU
site. Bioaccumulation values and models derived from published literature were therefore
used to estimate concentrations in food items based on media concentrations
(Tables 8 and 9). Because bioaccumulation is a non-linear process, log-linear regression
models were used if available. These log-linear bioaccumulation regression models for
wildlife (Sample et al., 1998a), soil invertebrates (Sample et al., 1998b), and plant tissues
(Bechtel Jacobs, 1998) were used to estimate the uptake of several metals into invertebrate
tissues (Table 9). Calculated bioconcentration factors (BCFs) for each analyte were
considered representative for all prey items from that food group. In the absence of these
models, the 90th percentiles of bioaccumulation factors (BAFs) were used for determining
uptake of inorganic contaminants into receptors from these or other sources (Oak Ridge
National Laboratory [ORNL], 2000; Beyer and Stafford, 1993; and CH2M HILL, 2001). For
organic contaminants, BAFs from the peer-reviewed literature were selected preferentially to
calculating BAFs. In the absence of BAFs in the literature, they were calculated from log
Kow-based models (EPA, 2003 and 2005).
Soil-to-invertebrate transfer factors were derived using:
BTF=10(logKow - 0.6)/[foc*10(0.983logKow + 0.00028)]
Soil-to-mammal transfer factors for organics were derived using:
BAF=10(0.338-0.145*logKow)
Soil-to-plant (rinsed foliage) transfer factors for organics were derived using:
BTF=10(1.781-0.4057*logKow)
To be conservative, and in the absence of site specific data, the fraction of organic carbon
(foc) used in these equations was 1 percent (EPA, 2005). If a BAF or other bioaccumulation
model was unavailable from the literature or databases, a value of 1.0 was assumed for the
screening calculations.
Exposure estimates were generated for the COPECs for each receptor species using the
following exposure model:


+=
=
FIRPBRFIPSoilEi
N
i
ist
1
where:
Et = total exposure (mg/kg/d)
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Soil = chemical concentration in soil (mg/kg dry weight)
Ps = soil ingestion rate as proportion of diet
FIR = food ingestion rate (kg food/kg body weight/d)
Bi = chemical concentration in biota type (i) (mg/kg wet weight)
Pi = proportion of biota type (i) in diet

The following additional assumptions were incorporated into the exposure modeling:
● Exposure to total petroleum hydrocarbons (TPH) is only from abiotic media (soil and
water); thus, there is no food component associated with exposure to TPH (Albers,
1995).
● In contrast, exposure to polycyclic aromatic hydrocarbons (PAHs) may be from both
abiotic and biotic sources.
4.0 Ecological Effects Assessment
This section focuses on the ecological effects of COPECs found in site soils.
4.1 Screening for Ecological Effects from Direct Exposure to Contaminated Soil
Ecological benchmarks are used to evaluate the potential for direct toxicity of contaminants
to ecological receptors but do not account for bioaccumulation potential and consequent
exposure of higher trophic-level animals.
Soil screening values representing NOECs and LOECs in soil were extracted from multiple
published literature sources (Tables 10 and 11). In the absence of a chemical-specific soil
screening value, values for a similar, related chemical were used as a surrogate. Instances
where a surrogate value was used are noted in Tables 10 and 11.
4.2 Screening Toxicity Reference Values for Wildlife
A literature review of toxicity information for COPECs was conducted to identify
appropriate TRVs for mammals and birds. TRVs that represent doses for mammals and birds
have been selected in accordance with the guidelines presented in EPA (1997). TRV
evaluation included consideration of ecological relevance, study duration, effect level, study
endpoints, test species, form of chemical, whether effect concentrations are bounded, and
exposure routes. When available, studies representing NOAELs were selected over LOAELs
and lethal dose to 50 percent of the test population (LD50s). LOAELs and LD50s were
normalized to NOAELs through the use of uncertainty factors if no suitable NOAEL existed.
When available, chronic studies were selected over subchronic and acute studies. In addition,
chronic studies were selected that represented oral exposure routes because the oral route is
being quantitatively evaluated in the effects assessment.
The endpoints for the TRVs for both the mammals and birds were not always population-
level effects. When TRVs were not available for population-level effects, studies with
behavioral endpoints (avoidance response, activity levels, impaired response, etc.) were used.
Population-level NOAELs, had they been available, would likely present higher values for
NOAELs and LOAELs.
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Table 12 presents a matrix of the different TRVs for mammals, by chemical, that were
reviewed, and shows the NOAEL and LOAEL (if available) TRVs that were selected for
each chemical. Table 13 presents a similar matrix of TRVs for birds. Uncertainty factors
were applied as needed. In the absence of chemical-specific bird or mammal toxicity values,
values for a similar, related chemical were used as a surrogate. Instances where a surrogate
value was used are summarized in Tables 12 and 13.
Appendix A presents summaries of the toxicity studies, including uncertainties and
assumptions used to develop NOAEL and LOAEL reference values used in this SLERA.
5.0 Initial Risk Characterization
This section presents the initial characterization of risks at the TTU. In the risk
characterization, exposure and effects data are compared to draw conclusions concerning the
presence, nature, and magnitude of effects that may exist at the site. Risks were evaluated
based on the ratio of exposure doses to TRVs, resulting in hazard quotients (HQs), and are
described by the following equation:

HQ = ED/TRV or C/TRV
where:
HQ = Ecological hazard quotient (unitless)
ED = Maximum estimated chemical intake (dose) by receptor (mg/kg-day)
C = Maximum soil concentration (mg/kg)
TRV = Toxicity reference value (soil concentration-based effect level [mg/kg] or
measured or estimated dietary dose [mg/kg-day] both representing no-effect
levels)
An HQ value less than 1.0 indicates that adverse effects associated with exposure to a given
analyte are unlikely (EPA, 1997). These analytes were not considered to present any risk and
were excluded from further evaluation. If the estimated daily intake for any COPEC equals
or exceeds the TRV, the HQ will equal or exceed unity. An HQ greater than or equal to 1.0
indicates data is insufficient to exclude the potential for risk, but does not indicate that
risks are actually present. Chemicals where the HQ exceeded 1.0 were retained for a more
detailed evaluation in the refinement stage. Thus, the outcome of the initial step was to
generate a list of preliminary COPECs for each media or a conclusion of no unacceptable
risk.
When cumulative effects to a receptor are expected due to exposure to more than one
chemical with similar toxicological effects, an ecological hazard index (HI) was calculated
for detected analytes within a chemical class. An ecological HI is the sum of all hazard
quotients from detected COPECs with similar toxicological mechanisms. This was based on
the assumption that the effects are additive for COPECs that have the same toxic mechanism,
which is typically only considered true for PAHs and polychlorinated biphenyls (PCBs).
However, HIs were also calculated for total detected energetics, inorganics, petroleum
products, semi-volatile organic compounds (SVOCs), and volatile organic compounds
(VOCs) for each receptor as a conservative measure of potential risk. Only HQs for detected
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analytes were summed in the HI calculation. This excluded the uncertainty associated with
non-detected concentrations contributing to this estimation of potential for risk. If an HI
exceeded 1.0 then all detected COPECs within the HI class were retained for the refined
screening evaluation.
The risk characterization was conducted in two phases: an initial conservative phase and a
refined phase. The initial phase employed maximum concentrations, no effect levels, and
conservative assumptions to differentiate analytes that may present a risk from those that
clearly do not. The refined phase evaluated the analytes retained in the initial phase in more
detail using biologically more realistic assumptions and lowest effect levels in addition to no
effect levels. Results of the initial and refined screens are presented below.
5.1 Terrestrial Plants
Table 14 presents a summary of the comparison of site soil data to NOEC-based media
screening benchmarks for direct toxicity to plants. Screening values were found for 38 of the
87 analytes detected in at least one sample at the site, and for 40 of the 64 analytes below
detection limits in all samples. No screening values could be identified for 49 detected
analytes and 24 non-detected analytes. Consequently, these analytes were retained as
uncertainties.
HIs, the sum of all HQs for chemicals within each chemical class (energetics, inorganics,
PAHs, petroleum products, SVOCs, and VOCs), were based only on detected analytes, and
ranged from 0.013 for VOCs to more than 14,700 for inorganics. HIs did not exceed 1.0 for
the energetic, VOC, and SVOC contaminant classes. Five energetics exceeded their
respective NOEC-TRVs, although these exceedances were also based on detection limits
(i.e., analytes were not detected in any samples). Eleven non-detected SVOCs also had HQs
greater than 1.0. In the VOC chemical class, only non-detected 2-chlorophenol (HQ=15) and
non-detected phenol (HQ=1.5) concentrations exceeded their NOEC-TRVs. The remaining
11 energetics, three SVOCs and eight VOCs with screening values did not exceed their
TRVs and were determined to pose no risk to terrestrial plants. All non-detected analytes
with HQs greater than 1.0 and all detected analytes from the inorganic, PAH, and petroleum
product classes (HQs greater than 1.0) were retained for further analysis in the refined
screening assessment.
NOEC-TRVs were exceeded for 17 of 20 inorganic COPECs with available TRVs. Only
beryllium, cobalt, and perchlorate did not have HQs greater than 1.0 and were determined to
not pose a risk to terrestrial plants at the site. Six analytes (carbon disulfide, iron,
magnesium, nitrate, phosphorus, and strontium) did not have screening values; thus, they
were retained as uncertainties. The NOEC-based HQ for aluminum was the greatest at
10,800. NOEC-based HQs for antimony (330), chromium (550), copper (1,800), lead (436),
vanadium (129), and zinc (460) were also high. Barium, manganese, molybdenum, nickel,
selenium, and silver all had NOEC-based HQs that ranged from 10 to 100. The remaining
four inorganics (arsenic, cadmium, mercury, and thallium) had HQs greater than 1.0, but less
than 10.
Fifteen of 17 PAHs exceeded their NOEC-TRVs for a HI sum of 851. The greatest HQs were
for 2-methylnaphthalene (567) and naphthalene (177), while only two others (fluorene and
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phenanthrene), both detected, had HQs between 10 and 100. Only detected fluoranthene and
non-detected acenaphthene did not exceed their screening values.
The HI for petroleum products (5.9) was only comprised of TPH. This detected COPEC was
retained for further analysis in the refined screening assessment.
Analytes that exceeded their NOEC-TRV, or those that contributed to an HI exceeding 1,
could not be excluded from presenting a potential risk to terrestrial plants at the site, and
were retained as COPECs for the refined screening assessment. This included all detected
inorganics, PAHs, and petroleum products. The analytes not exceeding the NOEC-based
TRVs, and where the contaminant class HI did not exceed 1, included 11 non-detected and
12 detected chemicals that are not considered to pose a potential risk to terrestrial plants at
the HAFB – TTU site.
5.2 Soil Invertebrates
Table 15 presents a summary of the comparison of site soil data to NOEC-based media
screening benchmarks for direct toxicity to invertebrates. Screening values were found for
53 of the 87 analytes detected at the site, and for 39 of the 64 analytes not found at
concentrations greater than the detection limit. The remaining 34 detected analytes and
25 non-detected analytes without screening values were retained as uncertainties.
The HI for energetic compounds was 16. This was driven by the one detected analyte in this
class (HMX) that exceeded its NOEC screening value. Two of the four detected analytes did
not have screening values for soil invertebrates (picric acid and nitroguanidine), and were
retained as uncertainties. The remaining detected energetic (2,4-dinitrotoluene) did not
exceed its NOEC screening value (HQ=0.06). Only four of the 13 non-detected analytes with
TRVs exceeded their respective NOECs, with HQs ranging from 2.6 (nitrobenzene) to 71 (4-
nitrophenol and 2,4-dinitrophenol).
The highest HI score (5,150) was for the inorganic class of COPECs. There were 25 of 26
detected analytes in this chemical class. Only selenium was not detected in any sample
(n=48), and concentrations did not exceed the NOEC. Eleven did not have screening values
and, therefore, were retained as uncertainties. Screening values were exceeded by 10 of the
remaining 14 detected analytes, with a NOEC-HQ of 3,600 (copper) driving the HI above 1.
HQs were also high for chromium (1,383), zinc (115), and lead (28) while HQs for antimony,
arsenic, barium, mercury, nickel, and perchlorate were less than 10. Screening values for
beryllium, cadmium, cobalt, and thallium were not exceeded by detected analytes.
Five of the six detected PAHs (2-methylnaphthalene, anthracene, fluorene, naphthalene, and
phenanthrene) exceeded their NOEC screening values and had HQs ranging from 7.2
(anthracene) to 57 (2-methylnaphthalene). These exceedances contributed to an HI of 177 for
PAHs. Detected fluoranthene did not exceed its screening value. Two of the 10 non-detected
PAHs also exceeded their respective screening values, with NOEC-based HQs of 4.6
(acenaphthylene) and 8.1 (pyrene).
The HI for petroleum products (67) was only comprised of TPH. This detected COPEC was
retained for further analysis in the refined screening assessment.
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A total of 14 SVOCs were evaluated against NOEC-TRVs for soil invertebrates. Only two of
these were detected analytes (bis[2-ethylhexyl]phthalate and dibenzofuran) and only the
dibenzofuran HQ exceeded 1.0 (8.6), to drive an HI greater than 1.0. Thus, both detected
SVOCs were retained for the refined screening assessment. Seven of the 12 non-detected
analytes that were screened against NOEC values had HQs greater than 1.0 and were also
retained.
HIs exceeded 1.0 for all chemical classes except for VOCs. HQs did not exceed 1.0 for any
of the 28 VOCs that were detected and had screening values. NOEC-TRVs were not found
for the other 20 detected VOCs. Only two of eight non-detected VOCs with TRVs had
potential soil concentrations that exceeded their NOEC screening values, although 2-
chlorophenol (10.5) was the only one where the HQ exceeded 10.
Analytes that exceeded the NOEC-TRV could not be excluded from presenting a potential
risk to soil invertebrates at the site and were retained as COPECs for the refined screening
assessment. This included all detected energetics, inorganics, PAHs, petroleum products, and
SVOCs in addition to non-detected analytes where the HQ exceeded 1. The analytes not
exceeding the NOEC-based TRVs included nine non-detected energetics, selenium, five non-
detected PAHs, nine non-detected SVOCs, and 28 detected VOCs that are not considered to
pose a potential risk to soil invertebrates at the HAFB – TTU site.
5.3 Mammals
Table 16 presents initial screening evaluation HQs calculated for mammalian wildlife
receptors foraging across the site. Analytes found to exceed NOAEL-based TRVs in the
initial screening assessment were retained for additional analysis in the refined screening
assessment. NOEC-TRVs were found for 65 of the 87 detected COPECs at the site, and for
39 of the 64 non-detected COPECs at the site. The remaining 22 detected analytes and 25
non-detected analytes without TRVs were retained as uncertainties. Analytes were divided
into six classes, of which there were 24 energetics, 26 inorganics, 17 PAHs, one TPH, 27
SVOCs, and 56 VOCs. All detected analytes within a class of analytes were also retained for
the refined screening assessment when the HI exceeded 1.0. A summary of these results for
all receptors is presented in Table 17.
All mammalian receptors (Ord’s kangaroo rat, Townsend’s ground squirrel, black-tailed
jackrabbit, pronghorn, grasshopper mouse, and coyote) had NOAEL-based TRV exceedances
for energetics, inorganics, and PAHs that led to HIs greater than 1.0 for these classes of
COPECs. All mammalian receptors, except for the coyote, also had maximum estimated
exposures to detected VOCs greater than NOAEL-based TRVs, driving HIs above 1.0. Only
the grasshopper mouse had an HI for TPH greater than 1.0. No receptors had any detected
COPECs that exceeded the NOAEL-based TRVs for SVOCs; thus, these compounds were
determined not to pose a risk to mammalian wildlife receptors at the site.
All mammalian wildlife receptors had HIs for energetics that exceeded 1. Exposures
exceeded TRVs for 1,3-dinitrobenzene, 2,4-dinitrotoluene, 2,6-dinitrotoluene, HMX, RDX,
and tetryl, with HQs ranging from 1.0 (1,3- dinitrobenzene; pronghorn) to 13 (1,3-
dinitrobenzene; grasshopper mouse); however, HMX and 2,4-dinitrotoluene were the only
energetic analytes with detected concentrations in soil. HMX doses were greater than the
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NOAEL-based TRVs for all receptors, ranging from 2.5 (coyote) to 9.8 (kangaroo rat). Only
grasshopper mouse exposure to 2,4-dinitrotoluene exceeded the NOAEL (HQ=1.3).
Inorganic HIs ranged from 90 (pronghorn) to 6,580 (grasshopper mouse). Aluminum,
antimony, copper, and lead doses exceeded the NOAEL-based TRVs for each receptor within
the inorganic class of contaminants. Lead and aluminum contributed greatest to each HI.
NOAEC-based HQs also exceeded 1.0 in at least one receptor for all other metals except
beryllium, cobalt, manganese, nitrate, and strontium. Except for non-detected selenium
exposure to the ground squirrel, pronghorn, and coyote where HQs were less than 1.0, all
inorganics were evaluated further in the refined screening evaluation for all mammalian
receptors due to HIs greater than 1.0.
Similarly, all mammalian wildlife receptors had HIs for PAHs that exceeded 1.0. The only
PAH that failed the NOEC-based TRV screen for all receptors was 2-methylnaphthalene.
However, NOAEL-based HQs for 2-methylnaphthalene were generally less than 10, and
ranged from 1.0 (coyote) to 7.1 (kangaroo rat) for all receptors except the grasshopper mouse
(250). All detected PAHs and eight non-detected were retained for further evaluation in the
refined screening assessment.
Only the grasshopper mouse had a TPH HQ greater than 1.0 (1.5), and it was retained for
further characterization in the refined screening assessment. Petroleum products were
determined not to pose a risk to all other mammalian wildlife receptors at the site.
Five of the six mammalian wildlife receptors (all except coyote) had HIs for VOCs that
exceeded 1.0. In all cases, these HIs were driven by exposure to acetone exceeding the TRV
doses. HQs for acetone ranged from 6.2 (pronghorn) to 20 (kangaroo rat). The exposure dose
for phenol also exceeded the TRV for the grasshopper mouse (HQ=4.4); however, this was
driven by non-detects.
Overall, HIs exceeded 1.0 in all species for energetics, inorganics, and PAHs; VOC HIs were
also greater than 1.0 for all receptors except the coyote; and, only the grasshopper mouse had
an HI greater than 1.0 for petroleum products. Detected COPECs from these classes were
retained for further characterization in the refined assessment. The black-tailed jackrabbit,
grasshopper mouse, and Ord’s kangaroo rat were the most sensitive showing the highest
HQs, while the pronghorn and coyote were less sensitive with lower HQs. A total of 21 non-
detected COPECs with available TRVs had HQs greater than 1.0. These were also retained
for further characterization in the refinement.
5.4 Birds
Table 16 also presents HQs calculated for avian wildlife receptors foraging across the site.
NOAEL-TRVs were found for 62 of the 87 detected COPECs at the site, and for 34 of the 64
non-detected COPECs at the site. The remaining 25 detected analytes and 30 non-detected
analytes without TRVs were retained as uncertainties. COPECs were divided into six classes
of compounds and there were 24 energetics, 26 inorganics, 17 PAHs, one TPH, 27 SVOCs,
and 56 VOCs. All detected analytes within a class were retained for the refined screening
assessment when the HI exceeded 1.0 for the class, in addition to non-detected analytes
where exposures exceeded the TRV. A summary of these results is presented in Table 17.
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The only detected energetic compound that exceeded its TRV was 2,4-dinitrotoluene.
Exceedances of 2.9 (western meadowlark), 3.3 (loggerhead shrike), and 3.5 (burrowing owl)
were drivers for HIs greater than 1.0 for these three receptors. Several non-detected energetic
compounds also exceeded their NOAEL-based TRVs, ranging in HQs from 1.0 (2-amino-
4,6-dinitrotoluene; sage sparrow) to 99 (nitrobenzene; loggerhead shrike); however, these
exceedances were all based on detection limits and have a high uncertainty.
All avian receptors (sage sparrow, loggerhead shrike, western meadowlark, and burrowing
owl) had NOAEL-based TRV exceedances for inorganics that led to HIs exceeding 1.0 for
this class. All detected inorganics, and non-detects greater than TRVs, were retained for
further characterization in the refined screening evaluation. Inorganic HIs for each avian
receptor ranged from 850 (sage sparrow) to 4,600 (owl). Lead and phosphorus were the
dominant drivers for these high exceedances (greater than or equal to 98 percent of the HI)
with phosphorus accounting for up to 80 percent of the inorganic HI score (sage sparrow)
and lead contributing up to 50 percent (meadowlark). Other inorganics that exceeded their
NOAEL-based TRVs included perchlorate in the sparrow (HQ=1.3). Aluminum, cadmium,
chromium, and zinc in the shrike, meadowlark, and owl, and copper in the owl, also had HQs
between 1.0 and 20.
Only one detected PAH (2-methylnaphthalene) exceeded its NOAEL-based TRV and was
the primary HI driver. Exceedances ranged from 3.6 (meadowlark) to 4.1 (shrike). The
sparrow did not exceed any single TRV for PAHs, but the HI still exceeded 1.0. Thus, all
detected PAHs for these three receptors were retained for analysis in the refined screening
assessment. PAH exposure to the owl did not exceed any TRV or HI. No non-detected PAHs
had HQs greater than 1.0.
None of the receptors had any detected COPECs that exceeded the NOAEL-based TRVs in
the petroleum product class of chemicals; thus, TPH was determined not to pose a risk to
avian wildlife receptors at the site.
Shrike exposure to bis(2-ethylhexyl)phthalate was the only detected SVOC to exceed a
NOAEL-based TRV (HQ=1.0). None of the other avian receptors had detected COPEC
exposures greater than TRVs, and SVOC HIs for the sparrow, meadowlark, and owl were
less than 1.0. Individual chemical HQs for non-detected SVOCs that also exceeded the
NOAEL-based TRVs ranged from 1.1 for butyl benzylphthalate (owl) to 83 for butyl
benzylphthalate (shrike). These non-detected COPECs were retained for further
characterization in the refined screening assessment.
Sparrow exposure to acetone was the only detected VOC to exceed a NOAEL-based TRV
(HQ=1.2). None of the other avian receptors had detected COPEC exposures greater than
TRVs, and VOC HIs for the shrike, meadowlark, and owl were less than 1.0. Individual
chemical exposures for non-detected VOCs were all less than their NOAEL-based TRV.
Therefore, exposure to the sage sparrow from all detected VOCs was evaluated further in the
refined screening assessment. All other COPECs were determined to pose no potential for
risk to avian wildlife in the TTU site.
The HIs for inorganics exceeded 1.0 for all avian receptors. Lower-magnitude HIs were also
calculated for energetics (shrike, meadowlark, and owl), PAHs (sparrow, shrike, and
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meadowlark), SVOCs (shrike), and VOCs (sparrow). Thus, all detected COPECs from these
classes were evaluated further in the refined screening assessment, in addition to non-
detected COPECs with exposures greater than their TRV. The burrowing owl was the most
sensitive avian receptor showing the highest HQs.
6.0 Refined Risk Characterization
COPECs in soil that were retained following the initial screening evaluation were evaluated
further in the refined screening assessment. The refined screen was conducted to better
clarify which analytes retained following the initial screen are present at concentrations that
may present potential risks to ecological receptors. Refinements to the risk characterization
take into account background concentrations, frequency of detection, frequency of
exceedance, lowest effects levels, and more realistic exposure assumptions to provide a more
detailed evaluation. Analytes retained at the conclusion of the refined screen may be the
focus of risk management activities or may be subject to further, more definitive risk
evaluation.
6.1 Risk Characterization Refinements
Multiple refinements to the exposure and effects analyses were incorporated. These are
described below.
6.1.1 Background Screen
Soil data from the TTU were compared to background soil data collected in 1997, 1998,
2000, and 2004 for the purpose of excluding inorganic COPECs whose concentrations are
not elevated due to on-site activities. COPECs with concentrations that do not exceed
background are not likely to be site-associated, and are, therefore, unlikely to present a risk to
ecological receptors. Background data for the TTU (URS, 2001) represent two soil
formations that exist in the UTTR-North area (which includes the TTU): the combined
amtoft, skumpah, and timpie-tooele soil formations and the playa-salt air soil formation. In
accordance with EPA guidance (EPA, 2002), data from these soil formations were
statistically compared to site concentrations using the non-parametric Wilcoxon Rank Sum
(WRS) test. If the null hypothesis was accepted (i.e., there was no significant [p>0.05]
difference between background and site data), then it was concluded that the analyte was not
elevated relative to background and it was dropped from further consideration as a COPEC
for all receptors. COPECs significantly greater than background concentrations were retained
for further characterization in the refined screening evaluation.
6.1.2 Lowest Observed Effect Concentrations and Levels
In the initial evaluation, no-effect levels were conservatively assumed as the effect endpoints
for plant, soil invertebrate, and wildlife HQ calculations. No-effect levels do not clearly
indicate the lowest level of exposure at which effects are evident and, therefore, do not
necessarily indicate that risks are present or impacts are occurring. In this refined evaluation,
LOECs and LOAELs were identified or derived for plants, soil invertebrates, and wildlife for
all COPECs where available (Tables 10 through 13).
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6.1.3 Point-by-Point Exceedance Evaluation
In the initial site-wide evaluation for plants and soil invertebrates, the maximum site-wide
concentrations in soil were evaluated against NOEC-based TRVs. This approach serves to
eliminate those chemicals that clearly do not present risks, but does not address specific areas
or the nature of potential risks associated with retained analytes. In the refined screen, a
point-by-point evaluation of concentrations of retained analytes was conducted. The relative
risk presented by each retained analyte was judged based on the frequency of detection of the
analyte and the frequency and magnitude of exceedances of available TRVs. Depending on
the screening value(s) exceeded, each exposure point estimate was grouped into one of the
following three HQ categories:
HQNOEC<1: no adverse effect
HQNOEC >1> HQLOEC: possible adverse effect
HQLOEC >1: probable adverse effect
Because the NOEC represents the highest dose at which no effects were observed and the
LOEC is the lowest dose at which effects were evident, there is uncertainty regarding
whether adverse effects will occur when the exposure concentration falls between the NOEC
and LOEC. In this situation, the potential for risk cannot be excluded but is not considered
likely.
The frequency with which environmental concentrations exceeded toxicity values
(percentage of HQs in each HQ category for each media-receptor combination for each
location) provides an estimate of the likelihood of adverse effects in the point-by-point
analyses. The maximum acceptable adverse effect level generally selected for the assessment
endpoints is a 20 percent reduction in the measured attribute (Suter et al., 2000). Thus, if 80
percent or more of a population is not affected, then the risk is not considered biologically
significant. This level is consistent with current EPA regulatory practices (e.g., development
of the National Ambient Water Quality Criteria [NAWQC] and effluent discharges regulated
by the National Pollutant Discharge Elimination System [NPDES]) and measurement limits
for many field and laboratory tests. For example, aquatic subchronic toxicity tests are not
reliable at detecting reductions at less than 20 percent adverse effect responses of the test
organism; LOECs for avian reproduction tests correspond to a 20 percent reduction; and
20 percent reduction in community is the limit of detection for assessing aquatic
communities using EPA rapid bioassessment procedures (Suter et al., 2000). Using available
methods, changes in natural populations of less than 20 percent cannot generally be
differentiated from “noise” measurements.
Consequently, an effect level of 20 percent was selected for plants and soil invertebrates.
Assuming that the total samples provided an adequate spatial representation of the area, if
fewer than 20 percent of samples possess concentrations that exceeded the LOEC-based
TRV, it was assumed that adverse effects to the assessment endpoint were not significant.
Both detected and non-detected concentrations retained for additional evaluation after the
initial risk characterization were evaluated based on this criterion. However, the potential for
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adverse effects indicated by TRV exceedances from non-detected concentrations suggest
insufficiently low detection limits and represent uncertainties.
6.1.4 Exposure Point Concentrations
Maximum, site-wide concentrations were used as the EPCs in the initial evaluation for
wildlife receptors. However, birds and mammals are mobile organisms and it is over-
protective to consider that they are exposed to the maximum detected concentrations at all
times. In addition, each area of the site provides a different set of potential exposures.
Therefore, the EPCs were refined to the 95th percent UCL of the mean environmental media
concentrations (UCL95) for each analyte (Table 3). The maximum detected concentration
was used as the EPC when the calculated UCL95 was greater than the maximum detected
value. All EPCs were calculated using the most recent version of ProUCL (Version 3.0; EPA
2004) and the distributional basis for calculating each UCL95 are reported in Table 3. One-
half the detection limit was used as a surrogate for non-detects in calculating the UCL95.
This EPC refinement provides a more realistic estimate of COPEC exposures to wildlife. For
these trophic guilds, it was also conservatively assumed that chemicals in sampled media are
100 percent bioavailable and that they remain at a steady concentration (i.e., decomposition
rates were not considered).
6.1.5 Samples from Within Habitat
The entire area of the TTU does not provide habitat suitable for ecological receptors. Open
Burning and Open Detonation (OB/OD) of missile motors and waste munitions results in the
disturbance and elimination of habitat in the immediate vicinity. Land cover immediately
adjacent and within operational areas (labeled as OB/OD areas) are barren and devoid of
habitat and, therefore, represent an incomplete exposure pathway for ecological receptors.
Consequently, a further refinement was developed in which only data from samples collected
within areas that provide habitat at the site were considered. Samples falling within habitat
and OB/OD areas are listed in Table 18 and are displayed in Figure 3. New summary
statistics and EPCs were calculated based only on the habitat dataset (i.e., all OB/OD
samples were excluded) and are presented in Table 19. Additional refined screening analyses
were performed for all receptors for the purpose of evaluating relative contribution of
samples from OB/OD areas and habitat areas to overall risks within the TTU.
6.1.6 Area Use Factors
In the initial screening assessment it was conservatively assumed that the area each wildlife
receptor was exposed to was equal to the home range of each receptor. However, wildlife
may forage over distances that exceed the exposure area offered by the site. Home-range
information for each receptor was evaluated against each area of potential exposure in the
refined exposure analysis. These foraging ranges were compared against the areas of each
potential exposure location at the site as a conservative measure of the potential for use at
these locations. The resulting ratio of site area (220 acres) to home range area for each
receptor (Table 7) was used to determine the proportion of diet and media exposure that
would be derived from each area of concern.
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6.1.7 Bioaccumulation Factors
Bioaccumulation models for retained COPEC metals were based on log-linear regression
models for all metals except iron. The BAF regression models used to estimate the
concentration of COPECs in prey were updated to be based on the refined EPCs instead of
maximum detected concentrations. The conservative use of 90th percentile uptake factors for
inorganic COPECs without log-linear regression calculations for calculating uptake factors
were replaced with more ecologically relevant median uptake factors in the refined wildlife
exposure analysis (Table 20). BAFs for most organic COPECs were calculated based on log
Kow equations and remained the same as in the initial screening assessment.
6.2 Refined Risk Characterization
The refined risk characterizations for all retained COPECs are described below.
6.2.1 Background Screen
The result of background comparison statistics are summarized in Table 21, and detailed in
Appendix B. Nine analytes had concentrations in all samples that were not significantly
different from background (aluminum, beryllium, chromium, iron, manganese, mercury,
nickel, phosphorus, and thallium). In the case of aluminum, not only were concentrations
within the background range, but the pH of TTU soils is neutral to basic (7.4 to 8.9; Table 3).
At these pHs, aluminum is unlikely to be in a bioavailable form (EPA, 2003). An additional
six inorganic analytes were significantly greater in concentration in background samples than
on-site samples (arsenic, barium, cobalt, magnesium, strontium, and vanadium). These 15
analytes were not considered to be site-associated COPECs and were eliminated from further
characterization and analysis.
Phosphorus is of special consideration due to differences between forms. Pure elemental
phosphorus (white phosphorus) is used as an incendiary in munitions. Burned phosphorus
products, containing very little white phosphorus, remain after munitions are spent.
Munitions containing white phosphorus are minimal at the TTU. White phosphorus also does
not persist in soil (3-7 day half-life) (ATSDR, 1997e). Screening level NOAEL-HQs for
avian wildlife were high (>500) based on the maximum detected phosphorus concentration in
soil (990 mg/kg). An uncertainty associated with this exposure calculation is that the TRV
was based on test species (mallard duck) exposure to white phosphorus (Sparling et al. 1997).
Another uncertainty is that the total phosphorus measured in soil is likely comprised of forms
other than pure elemental phosphorus. Ultimately, it is not considered a site-related
contaminant because site concentrations were not significantly different from background.
The remaining eight metals (antimony, cadmium, copper, lead, molybdenum, selenium,
silver, and zinc) were retained through the refined risk characterization to determine if they
posed a potential for risk in the screening assessment.
Further evaluation of the data for COPECs where the site concentrations were greater than
background revealed that the samples driving these differences were generally driven by
samples collected from operational areas (OB/OD) within the TTU site (Appendix B). This
bias is discussed as part of an additional component of the refined risk characterization. This
component differentiates between samples collected within habitat areas and those from the
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OB/OD areas, and determines which samples from which area are responsible for estimates
of potential for risk over the TTU site.
6.2.2 Terrestrial Plants
A point-by-point evaluation of the frequency of exceedance of NOAC- and LOEC-TRVs for
plants by concentrations of retained analytes in TTU soils is presented in Table 22. Detected
concentrations of analytes in the energetics, SVOCs, and VOC chemical classes did not
exceed NOEC- or LOAC-TRVs for any analyte. Multiple exceedances of NOEC- or LOEC-
based plant screening values were observed for non-detected concentrations. These
exceedances indicate insufficiently low detection limits and represent uncertainties. The
frequency of these non-detected concentrations exceeding either NOECs or LOECs never
exceeded 12 percent among energetics, SVOCs, and VOCs. Even if it is assumed that
reanalyses with lower detection limits would still result in NOEC or LOEC exceedances for
all of these analytes (a conservative assumption), the frequency of exceedances are
insufficient to suggest the potential for adverse effects (i.e., less than 20 percent).
Consequently, it was concluded that all analytes in the energetics, SVOC, and VOC chemical
classes pose no risk to terrestrial plants at the site.
Seven of the nine retained inorganic COPECs had concentrations (detected or not detected)
in at least one sample that exceeded their LOEC-TRV. Only two inorganic COPECs did not
have concentrations in excess of LOEC-TRVs (cadmium and perchlorate) and NOEC
exceedances (cadmium) were infrequent (2 percent). Thus, neither cadmium nor perchlorate
pose risks to plants at the TTU. Antimony, copper, lead, molybdenum, and silver all had
samples with concentrations that exceeded LOECs; however, these COPECs are not
considered likely to present risks to plants because the frequency of LOEC exceedances were
low for each (less than 10 percent). Antimony, copper, molybdenum, and silver had high
frequencies of detected or non-detected concentrations exceeding the NOEC, and the
potential for adverse effects at these concentrations is possible, but uncertain because NOEC
exceedances represent concentrations lower than those where adverse effects are initially
observed. These NOEC exceedances indicate that adverse effects are possible, but the lack of
LOEC exceedances in samples from ecological habitat areas suggests the absence of adverse
effects to the plant community (Table 23). Selenium exceeded the LOEC with high
frequency (66 percent). Because these exceedances were due to inadequate detection limits
(i.e., all were due to non-detected concentrations), actual presence of selenium risks to plants
are uncertain. Only one inorganic, zinc, had detected concentrations that exceeded the LOEC
with a high frequency (67 percent). Consideration of only those samples from within areas
that provide habitat within the TTU reduces the frequency of LOEC exceedances by zinc to
57 percent (Table 23), a value that still exceeds the probable risk threshold. Zinc did not
exceed the LOEC by a high magnitude (LOEC-HQmax = 1.3), but these elevated
concentrations were consistently found at five locations in 1991 (SS-16 to SS-20), five
sample locations in 2002 (NR-229, NR-230, NR-232, NR-234, and NR-235), and two
locations in 2004 (NR-527 and NR-529), as shown in Figure 3. Consequently, potential for
risks to plants from zinc cannot be excluded.
Only five of 16 PAHs (2-methylnaphthalene, anthracene, fluorene, naphthalene, and
phenanthrene) had detected concentrations that exceeded NOECs or LOECs (Table 22). The
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frequency of exceedances for both NOECs and LOECs by detected and non-detected
concentrations never exceeded 15 percent. Therefore, these analytes were not considered to
present any significant risks to the terrestrial plant community. Among the remaining 11
PAHs, no detected concentrations exceeded TRVs, and because non-detected concentrations
in only four of 28 samples (14 percent) exceeded LOECs, the likelihood of potential adverse
effects is considered negligible. Consideration of the habitat area of the TTU indicates the
lack of NOEC exceedances for any PAH (Table 23). Consequently, there is no risk to plants
in ecological habitat areas of the site from PAHs.
TPH was detected in all six TTU soil samples in which it was analyzed, and exceeded the
LOEC-TRV in three of these (50 percent). Despite the small sample size and uncertainty
concerning the applicability of the toxicity data to the TPH form at the site, the high
frequency of exceedances suggests that the potential for adverse effects to plants from TPH
cannot be excluded. TPH was analyzed in one sample from outside the OB/OD areas and
representing potential habitat for plants. This sample did not exceed the plant NOEC and
indicates samples driving the potential for risk were mostly associated with OB/OD areas and
do not represent the potential for risks in the surrounding habitat areas of the site. Therefore,
there is no potential for risk to plants from TPH in habitat areas at the TTU.
6.2.3 Soil Invertebrates
A summary of the point-by-point refined soil invertebrate screen is presented in Table 24.
Similar to plants, there were no exceedances of LOEC-TRVs by detected concentrations for
any analytes in the VOC chemical class. The few and infrequent LOEC exceedances
(13 percent of samples) that did occur (2-chlorophenol) were based on insufficient detection
limits. Therefore, the potential for risks from VOCs to soil invertebrates at the site are
unlikely.
Only one of six retained energetics (HMX) had detected concentrations that exceeded the
NOEC or LOEC (Table 24). Although 20 percent of samples had detected concentrations that
exceeded the NOEC, only one of 42 samples exceeded the LOEC (2 percent). Non-detected
concentrations of 2,4-dinitrophenol, 2-nitrophenol, and 4-nitrophenol also exceeded the
LOEC with low frequency (less than or equal to 14 percent). Non-detected concentrations of
nitrobenzene exceeded the NOEC-TRV in fewer than 7 percent of the samples. Neither the
single detected concentration, nor any non-detected concentrations, exceeded the NOEC for
2,4-dinitrotoluene. Because all exceedances of NOECs and LOECs by energetics, whether
detected or not, did not exceed 20 percent, potential risks from energetics to soil invertebrates
at the site are not considered significant. Further, when only samples from within habitat
areas of the TTU are considered, no energetic LOEC exceedances were observed (Table 25),
and NOEC exceedances for HMX are low (11 percent). This indicates that samples driving
any potential for risk were mostly associated with OB/OD areas and do not represent the
potential for risks in the surrounding habitat areas of the site. Therefore, the conclusion is
that there is no significant potential for risk to soil invertebrates from energetics at the TTU.
Cadmium was the only inorganic that did not exceed the NOEC or LOEC in any samples
(detected or non-detected). Therefore, the potential for risks to soil invertebrates from this
COPEC is excluded. Antimony and perchlorate had single detected concentrations greater
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than the NOEC and are not considered to pose any significant risk. The potential for adverse
effects from copper, lead, and zinc were considered low due to the low frequency of LOEC-
TRV exceedances (19, 2, and 8 percent, respectively). Copper and zinc, however, did have
high frequency of NOEC exceedances by detected concentrations (85 and 100 percent,
respectively). The potential for adverse effects at these concentrations is possible, but
uncertain because these NOEC exceedances represent concentrations lower than those where
adverse effects are initially observed. When only samples from within habitat areas of the
TTU are considered, no LOEC exceedances are observed for lead and zinc, and only one of
21 (5 percent) samples exceeded the copper LOEC (Table 25). This indicates that samples
driving the potential for risk were mostly associated with OB/OD areas and do not represent
any potential for risks in the surrounding habitat areas of the site. Therefore, the conclusion is
that there is no significant potential for risk to soil invertebrates from inorganics at habitat
areas of the TTU.
Four of eight retained PAHs (2-methylnaphthalene, fluorene, naphthalene, and phenanthrene)
had detected concentrations that exceeded LOECs (Table 24). The frequency of exceedances
of LOECs for these PAHs was low (less than or equal to 14 percent). Non-detected or
detected concentrations of the remaining four PAHs (acenaphthylene, anthracene,
fluoranthene, and pyrene) also exceeded the NOEC or LOEC with low frequency (less than
or equal to 14 percent). Because all exceedances of LOECs by PAHs, whether detected or
not, did not exceed 20 percent, risks from PAHs to soil invertebrates at the site are unlikely
to be significant. Further, when only samples from within habitat areas of the TTU are
considered, no PAH NOEC or LOEC exceedances were observed (Table 25). This indicates
that samples driving any potential for risk were mostly associated with OB/OD areas and do
not represent the potential for risks in the surrounding habitat areas of the site. Therefore, the
conclusion is that there is no potential for risk from PAHs at habitat areas of the TTU.
TPH, detected in all six TTU soil samples in which it was measured, exceeded the LOEC-
TRV in four. Despite the small sample size and the uncertainty concerning the applicability
of the toxicity data to the TPH form at the site, the high frequency of exceedances
(67 percent) indicates that the potential for adverse effects to soil invertebrates from TPH
cannot be excluded. TPH was analyzed in one sample from outside the OB/OD areas and
representing potential habitat for invertebrates. This sample did not exceed the NOEC and
indicates no potential for risk to soil invertebrates from TPH in habitat areas of the TTU.
Only one of nine retained SVOCs (dibenzofuran) had detected concentrations that exceeded
NOECs or LOECs (Table 24). The frequency of LOEC exceedance for dibenzofuran was low
(11 percent). Non-detected concentrations of 2,4,5-trichlorophenol, 2,4,6-trichlorophenol,
and 2,4-dichlorophenol also exceeded the LOEC with low frequency (less than or equal to
14 percent). Non-detected concentrations in few (less than 14 percent) samples of the
remaining five SVOC COPECs exceed the NOEC-TRV. Because all LOEC exceedance by
SVOCs, whether detected or not, did not exceed 20 percent, significant risks from SVOCs to
soil invertebrates at the site are unlikely. Further, when only samples from within habitat
areas of the TTU are considered, no SVOC LOEC exceedances were observed (Table 25).
Only one sample concentration exceeded a NOEC (2,4,5-trichlorophenol) in samples from
habitat areas. This indicates that samples driving any potential for risk were mostly
associated with OB/OD areas and do not represent the potential for risks in the surrounding
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habitat areas of the site. Therefore, the conclusion is that there is no potential for risk to soil
invertebrates from SVOCs at habitat areas of the TTU.
6.2.4 Mammals
The refined screening assessment for wildlife resulted in a reduced number of COPECs that
pose a potential risk to mammals at the TTU (Tables 26 and 27). Table 28 shows a summary
of the refined screening evaluation results. Analyte groups considered in the refined screen
included energetics, inorganics, PAHs, petroleum products, SVOCs, and VOCs.
Refined estimates of exposure to five energetic compounds exceeded NOAELs for at least
one receptor: 1,3-dinitrobenzene, 2,6-dinitrotoluene, HMX, RDX, and tetryl (Table 26).
These NOAEL-HQs were generally of low magnitude and only exceeded 10 for the
grasshopper mouse (1,3-dinitrobenzene and RDX). With the exception of HMX, these
exceedances were also based on non-detected concentrations, indicating significant
uncertainty regarding the possible potential for risk from these energetic COPECs. LOAELs
were exceeded for only two of the six species, Ord’s kangaroo rat and the grasshopper
mouse. These exceedances were for four analytes: detected concentrations of HMX for the
kangaroo rat (HQ=1.1) and non-detected concentrations of RDX, 1,3-dinitrobenzene, and
2,6-dinitrotoluene for the grasshopper mouse (HQs less than 3.0). When only samples from
the habitat area of the TTU are considered (Table 27), HMX and 2,6-dinitrotoluene no longer
drive estimated exposures in excess of the LOAEL for the kangaroo rat and grasshopper
mouse, respectively. However, LOAEL exceedances based on non-detected RDX (HQ=1.1)
and 1,3-dinitrobenzene (HQ=2.7) for the grasshopper mouse remain. The potential for risk
from non-detected COPECs is uncertain and cannot be excluded, but the low magnitude of
LOAEL exceedances suggests that the likelihood of adverse effects to mammals from
energetic COPECs is low. LOAEL HIs for energetics were less than 1.0 for all receptors
except the kangaroo rat (HI = 1.1). There is low confidence that this HI indicates a potential
for risk because the mode of toxic action for this class of contaminants is not known to be
additive. Therefore, the conclusion is that energetics present no risk to five of six mammal
species at the TTU. Risks to insectivorous mammals from RDX and 1,3-dinitrobenzene
cannot be definitively excluded because they are based on non-detects, and are retained as
uncertainties.
Refined exposure estimates resulted in exceedances of NOAELs or LOAELs for seven
inorganics for at least one receptor: antimony, cadmium, copper, lead, molybdenum,
perchlorate, and selenium (Table 26). All except selenium were detected and represent
possible potential for risks to mammalian wildlife. The greatest number of inorganic LOAEL
exceedances was for the grasshopper mouse (five: antimony, cadmium, copper, lead, and
selenium), followed by the kangaroo rat (three: lead, perchlorate, and selenium) and
jackrabbit (three: copper, lead, and perchlorate). Lead and perchlorate were the only
inorganics to produce exposure estimates in excess of the LOAELs for ground squirrels and
pronghorn (HQs less than 3.0), driving HIs above 1.0 for these receptors. Cadmium, copper,
and lead EPCs were driven by a few very high concentrations collected within OB/OD areas.
There were no LOAEL exceedances for coyotes, and the low magnitude of NOAEL-HQs for
antimony (3.3) and lead (1.2) indicates the potential for adverse effects to mammalian
carnivores is unlikely.
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When only samples from the habitat area of the TTU are considered (Table 27), no exposure
estimates for any inorganic exceed NOAELs for the ground squirrel, pronghorn, or coyote.
NOAELs were only exceeded for non-detected selenium (kangaroo rat, jackrabbit, and
grasshopper mouse) and detected antimony, cadmium, lead, and molybdenum for the
grasshopper mouse. NOAEL-HQs for all inorganics in ecological habitat were less than 5.0.
These differences between exposure modeling with all site data and wildlife habitat data
indicate that samples driving any potential for risk were mostly associated with OB/OD areas
and do not represent the potential for risks in the surrounding wildlife habitat areas of the
site. LOAELs were only exceeded for cadmium (HQ=1.8) and selenium (HQ=2.8) for the
grasshopper mouse, and selenium (HQ=1.0) for the kangaroo rat. The selenium LOAEL
exceedances are based on non-detected concentrations, and the potential for risk from these
selenium values is uncertain. Cadmium was detected in 62 percent of samples collected from
habitat areas. The magnitude of this exposure exceeding the LOAEL is low, but even
excluding a sample with a concentration three times higher than the others, collected at the
roadside near Site 3 (sample SS-16) in 1991 (shown in Figure 3), does not reduce the
cadmium exposure below the LO AEL (HQ=1.01). Therefore, the potential for risk to
insectivorous mammals is low, but cannot be excluded due to cadmium exposure exceeding
the LOAEL.
Due to the individual COPEC exceedances, the LOAEL HIs for inorganics were greater than
1.0 for all receptors except the coyote when considering all site data. These exceedances
suggest that the cumulative potential for adverse effects from inorganics cannot be excluded.
When only potential receptor habitat was considered in the refined exposure analysis, the
LOAEL HIs for inorganic COPECs was only exceeded for the grasshopper mouse (HI=3.2)
(Table 26). Therefore, the potential for risk from inorganic COPECs is much lower in
potential habitat areas of the site than when including the OB/OD areas. Calculated HIs for
inorganics are a conservative approach to risk characterization; however, the mechanisms of
toxicity are not the same for all inorganic compounds, and inorganic HIs are not entirely
appropriate. Rather, the potential for risk from inorganics can be best described for individual
COPECs.
The conclusion for inorganics is that there is no potential for risk to four of six mammal
species in habitat areas of the TTU. Potential risks to kangaroo rats and grasshopper mice
from selenium cannot be excluded because they are based on non-detects and are retained as
uncertainties. The potential for risk to insectivorous mammals from cadmium also cannot be
excluded. It should be noted, however, that the LOAEL exceedance for cadmium is low
(HQ=1.8).
NOAEL-based TRV exceedances by 10 PAHs (2-methylnaphthalene, benzo(a)anthracene,
benzo(a)pyrene, benzo(b)fluoranthene, benzo(g,h,i)perylene, benzo(k)fluoranthene,
chrysene, dibenzo(a,h)anthracene, fluorene, and indeno(1,2,3-cd)pyrene) were observed for
at least one COPEC for each mammalian receptor except the coyote. Therefore, the potential
for risk to coyotes from PAHs was excluded. The NOAEL-HQs were generally of low
magnitude and only exceeded 10 for the grasshopper mouse (2-methylnaphthalene NOAEL-
HQ=114). Benzo(g,h,i)perylene exceeded the NOAEL for all mammalian receptors (except
the coyote), but was driven by non-detects. NOAEL exceedances based on detected
concentrations occurred for all receptors (except coyote) for 2-methylnaphthalene. LOAEL-
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based TRV exceedances by PAHs were observed for only two COPECs in two species.
Fluorene exposure to the kangaroo rat exceeded the LOAEL (HQ=1.4), and 2-
methylnapthalene exposure to the grasshopper mouse exceeded the LOAEL (HQ=14)
(Table 26). In addition to these two COPECs driving HIs for PAHs above 1.0 for the
kangaroo rat and grasshopper mouse, the LOAEL-HI for PAH exposure to the jackrabbit also
exceeded 1.0 (HI=1.2). However, when only samples from the habitat area of the TTU are
considered, neither the NOAEL nor LOAEL-HI for PAHs is greater than 1.0 for any
mammalian receptor. The conclusion is that samples that drive the potential for risk from
PAHs are associated with OB/OD areas and do not represent the potential for risks in the
surrounding wildlife habitat areas of the site. PAHs present no risk to mammals in ecological
habitat areas of the TTU.
Refined exposure modeling for TPH was only conducted for the grasshopper mouse, and the
NOAEL-TRV exceedance persisted (HQ=1.5) (Table 26). However, the LOAEL-TRV was
not exceeded. The potential for adverse effects at these concentrations is possible, but
uncertain, because NOEC exceedances represent concentrations lower than those where
adverse effects are initially observed. The NOEC for TPH was not exceeded when
considering only concentrations in wildlife habitat areas of the TTU (Table 27). Thus,
petroleum products were determined not to pose a potential risk to mammalian wildlife in
habitat areas of the site, and only a possible potential for risk in the entire TTU.
SVOCs were retained in the focused screen for three mammalian receptors (jackrabbit,
grasshopper mouse, and coyote). However, all of the COPECs driving the refined
mammalian wildlife screen for SVOCs were below detection. Seven of these non-detected
SVOCs exceeded both the NOAEL and LOAEL for the grasshopper mouse (Table 26). Only
one NOAEL exceedance from 2,4,5-trichlorophenol was observed for jackrabbits, and none
for coyotes. Samples driving the potential for risk from SVOCs are associated with OB/OD
areas and do not represent the potential for risks in the surrounding wildlife habitat areas of
the site. Only the 2,4,5-trichlorophenol LOAEL is exceeded (HQ=3.3) for the grasshopper
mouse when only areas of the TTU that provide wildlife habitat are considered (Table 27).
NOAEL exceedances for the grasshopper mouse were less than 10 for the six additional non-
detected SVOCs (2,4,6-trichlorophenol, 2,4-dichlorophenol, hexachlorobenzene,
hexachlorocyclopentadiene, hexachloroethane, and pentachlorophenol), and SVOCs did not
exceed the NOAEL for the jackrabbit or coyote. Because these COPECs exceed NOAELs
but not LOAELs where effects are first observed, the potential for risks is considered
possible but not likely. Therefore, the conclusion is that potential risk to insectivorous
mammals from 2,4,5-trichlorophenol cannot be excluded, but is retained as an uncertainty
because it is based on non-detects. SVOCs present no risk to all other mammals in ecological
habitat areas of the TTU.
Of the 33 VOCs retained for additional evaluation for mammals, only acetone and phenol
produced exposure estimates that exceeded NOAELs (Table 26). Detected acetone exceeded
the NOAEL by low magnitude (HQs less than 10) for all mammalian receptors except the
coyote, while non-detected phenol only exceeded the NOAEL for the grasshopper mouse
(HQ=4.4). LOAEL exceedances were also of low magnitude for each of three species: the
kangaroo rat (HQ=1.9), jackrabbit (HQ=1.2), the grasshopper mouse (HQ=1.4). However,
when only areas of the TTU that provide habitat are considered, neither NOAEL nor LOAEL
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exceedances occur for any VOC (Table 27). The conclusion is that samples driving the
potential for risk from VOCs are associated with OB/OD areas and do not represent the
potential for risks in the surrounding wildlife habitat areas of the site. VOCs, therefore,
present no risk to mammals in ecological habitat areas of the TTU.
6.2.5 Birds
The refined screening assessment for wildlife resulted in a reduced number of COPECs that
pose a potential risk to birds at the TTU (Tables 26 and 27). Table 28 shows a summary of
the refined screening evaluation results. Petroleum products were not considered in the
refined screening assessment for birds because they were eliminated as presenting risk for all
avian receptors during the initial screen. Analyte groups considered in the refined screen
included energetics, inorganics, PAHs, SVOCs, and VOCs.
Refined estimates of exposure for four (for the sage sparrow and burrowing owl) to as many
as eight (for the shrike and meadowlark) energetic COPECs exceeded avian NOAELs
(Table 26). However, the only detected COPEC in this group was 2,4-dinitrotoluene, which
did not exceed the LOAEL. There is a possible potential for adverse effects to these receptors
from COPECs with NOAEL exceedances, but this potential is low when the LOAEL is not
also exceeded. LOAELs were exceeded for only two of four species, the loggerhead shrike
and western meadowlark. These exceedances were for two analytes: non-detected
concentrations of RDX for shrikes and nitrobenzene for both species. LOAEL-HQs were less
than 5.0. None of the LOAEL-HIs for energetics exceeded 1.0 for any avian receptor. When
only samples from habitat areas of the TTU are considered (Table 27), nitrobenzene drops
out as producing estimated exposures in excess of the LOAEL for both species. The LOAEL
exceedance based on non-detected RDX for the shrike persists with low magnitude
(HQ=1.1). Samples driving the potential for risk to birds from energetics are mainly
associated with OB/OD areas. The conclusion is that energetics present no risk to three of
four bird species at the TTU. Risk to insectivorous birds from RDX cannot be excluded,
because it is based on non-detected concentrations, and is retained as an uncertainty.
Refined estimates of exposure for inorganics exceeded NOAELs and LOAELs for all avian
receptors (Table 26). These exceedances were driven by cadmium, lead, perchlorate, and
zinc. NOAEL-HQs ranged from 1.2 for zinc exposure for the owl to 360 for lead exposure
for the owl. While there is a possible potential for adverse effects to these receptors from
COPECs with NOAEL exceedances, this potential is low when the LOAEL is not also
exceeded. Lead exceeded the LOAEL for all avian receptors, with HQs ranging from 3.9
(sparrow) to 39 (owl). Cadmium exceeded the LOAEL for the shrike and meadowlark, with
HQs less than 2.0. These exceedances drove HIs above 1.0 for all avian receptors, ranging
from 4 (sage sparrow) to 40 (owl). Cadmium and lead EPCs driving HI exceedances were
also influenced by a few very high concentrations collected within OB/OD areas. When only
samples from the habitat area of the TTU are considered (Table 27), no exposure estimates
for any inorganic exceeded LOAELs for any species. NOAEL exceedances for inorganic
COPECs in habitat areas were low for cadmium in the shrike (HQ=1.4) and meadowlark
(HQ=1.0), and lead in the owl (HQ=2.9). The conclusion is that potential risks from
inorganics are associated with OB/OD areas and do not represent the potential for risks in the
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surrounding wildlife habitat areas of the site. Inorganics present no significant risk to any of
the four bird species in ecological habitat areas of the TTU.
PAHs were evaluated in the refined risk characterization for all bird receptor species except
the owl. Although screening level HIs for PAHs were greater than 1.0 for the sparrow,
shrike, and meadowlark, only 2-methylnaphthalene exposure exceeded the shrike and
meadowlark NOAELs in the refinement. These NOAEL-HQs were less than 2.0, and
modeled exposures did not exceed the LOAELs. While there is a possible potential for
adverse effects to these receptors from COPECs with NOAEL exceedances, this potential is
low when the LOAEL is not also exceeded. The lack of LOAEL exceedances resulted in the
conclusion that the potential for adverse effects in avian wildlife from PAHs is not likely.
PAHs in samples representing habitat areas within the TTU did not exceed NOAELs.
Therefore, there is a low potential for risk to avian receptors from PAHs at the TTU.
One detected SVOC (bis[2-ethylhexyl]phthalate) exceeded the NOAEL (HQ=1.0) for one
receptor (shrike) in the refined screening assessment. Non-detected SVOCs exceeded their
NOAEL-TRVs for all species. Exposure to four of these non-detected COPECs (2,4,5-
trichlorophenol, hexachlorobenzene, hexachlorocylopentadiene, and hexachloroethane) also
exceeded LOAELs for the shrike and meadowlark, with LOAEL-HQs less than 5. While the
potential for risk from non-detected COPECs is uncertain, it cannot be excluded. The
LOAEL HI for the loggerhead shrike, the only avian receptor with detected SVOC COPECs
retained, was below 1.0. When only samples from habitat area of the TTU are considered
(Table 26), no exposure estimates for any SVOC exceed LOAELs for any species. Several
non-detected phthalates continued to exceed their NOAELs for exposure to the shrike (butyl
benzylphthalate, diethylphthalate, dimethylphthalate, di-n-butylphthalate, and di-n-
octylphthalate) and meadowlark (butyl benzylphthalate, diethylphthalate, di-n-butylphthalate,
and di-n-octylphthalate) in habitat areas. However, these NOAEL-HQs were all less than
1.5 and were based on non-detected concentrations. Uncertainty associated with phthalate
exposure estimates is high. Phthalate exposures are likely overestimated due to the log Kows,
ranging from 3.6 to 10.6, driving the large estimated biotransfer factor (using the Kow-based
equation). Further, phthalate esters are rapidly broken down in the environment by photolysis
and biodegradation (Staples et al., 1997). Biotransformation limits bioaccumulation of
phthalate esters with increasing trophic level and general bioaccumulation models do not
consider these chemical specific variances. It is, therefore, likely that the Kow BCF model
contributes to overestimating exposure. The risk conclusion for avian exposure to SVOCs is
that potential for adverse effects are uncertain in OB/OD areas and are not present in the
surrounding wildlife habitat areas of the site. SVOCs present a low potential for risk to avian
receptors in ecological habitat areas of the TTU.
The NOAEL-HI for VOC exposure to the sage sparrow was greater than 1.0 in the initial
screening assessment, but did not exceed 1.0 in the refined screening assessment. Sparrow
exposure to all VOCs was less than NOAELs. Therefore, there is no potential for adverse
effects from VOCs to any avian wildlife receptor at the site.
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7.0 Uncertainties
Uncertainties are inherent in all risk assessments. The nature and magnitude of uncertainties
depend on the amount and quality of data available, the degree of knowledge concerning site
conditions, and the assumptions made to perform the assessment. A qualitative evaluation of
the major uncertainties associated with this screening assessment, in no particular order of
importance, is outlined below.
● No avian and mammalian life history data specific to the site were available;
therefore, exposure parameters were either modeled based on allometric relationships
(e.g., food ingestion rates) or were based on data from these same species in other
portions of their range. Because diet composition as well as food, water, and soil
ingestion rates can differ among individuals and locations, published parameter
values may not accurately reflect individuals present at the site. As a consequence,
risk may be either overestimated or underestimated.
● No site-specific data on concentrations in terrestrial plants, invertebrates, or small
mammals were available. Therefore, concentrations in these prey items were
estimated using literature-derived bioaccumulation models. The suitability of these
models is unknown. As a consequence, concentrations of COPECs in actual prey may
be either higher or lower than the data used in this screen.
● BCFs for estimating chemical specific tissue concentrations in plants were calculated
using a Kow-specific regression model from EPA (2005). These models were used
when chemical-specific BCFs were not available and provide the best available tool
for estimating the uptake of organic compounds into tissues. However, these models
are less accurate at predicting tissue concentrations for chemicals with Kow values
outside of the range for which they were developed (3-8). For these and other reasons,
exposure doses and potential risks to wildlife may be either overestimated or
underestimated.
● BCFs for estimating chemical-specific tissue concentrations in wildlife was estimated
using a Kow-specific regression model developed by Travis and Arms (1988). This
model was used only when chemical-specific BCFs were not available and is the best
available tool for estimating the uptake of organic compounds into tissues. However,
there are limitations to the Travis and Arms (1988) model that are described in Birak
et al. (2001). Essentially, the model is less accurate at predicting BCFs for chemicals
with Kow values outside of those used in the model development (6-6.9). For these
and other reasons, exposure doses and potential risks to wildlife may be
overestimated or underestimated.
● Assumptions that chemicals and organisms are at a steady state, that none of the
chemicals are metabolized, and that BCFs are consistent in all ingested media may
not be accurate. For these and other reasons, exposure doses and potential risks to
wildlife may be overestimated or underestimated.
● Concentrations in many samples were below detection limits. Concentrations in these
samples were estimated to be one-half the detection limit. If an analyte was never
detected in any sample, it was assumed not to be present, which may lead to an
underestimation of risk. In contrast, if an analyte was detected in at least one sample,
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summary statistics were based on the one-half detection limit assumption, leading to
an overestimation of risk.
● Literature-derived toxicity data based on laboratory studies were the only available
toxicity data used to evaluate risk to all receptor groups. It was assumed that effects
observed in laboratory species were indicative of effects that would occur in wild
species. The suitability of this assumption is unknown. Consequently, risk may be
either overestimated or underestimated. In addition, due to the limited availability of
toxicity data, confidence in the quality of some of the screening values (as defined by
the authors of these values) was low. This was particularly the case with the plant and
soil invertebrate screening values. These values may, therefore, overestimate toxicity
and risk.
● The exposure dose estimates in this screening risk assessment assume that
100 percent of the chemical concentrations to which receptors are exposed are in the
bioavailable form. Most chemicals will not be 100 percent bioavailable. In the cases
where bioavailability is less than 100 percent, risk is overestimated.
● Adequate toxicity information is not available for some constituents that were
detected in environmental media to quantify ecological risks. In some cases, data for
surrogate chemicals were used. The use of surrogate toxicity information to quantify
toxicity for these contaminants might lead to overestimates or underestimates of risk
to ecological receptors. For some contaminants, there is no information available
from which to develop TRVs and these constituents could not be evaluated.
● Dietary compositions were simplified for the site receptors to estimate concentrations
in food items using bioaccumulation models. It was assumed concentrations were
similar in comparable food types. The suitability of this assumption is unknown.
Consequently, risk may be either overestimated or underestimated.
● Few analyte-specific avian toxicity values were available for energetic compounds.
As a consequence, available data were often used as surrogates. Similarly,
bioaccumulation data for energetic compounds exist from EPA (2005) for TNT and
RDX, and for HMX and dinitrotoluenes (U.S. Army, 2005), but are otherwise
lacking. Further, only four energetics were detected in TTU soils, with frequencies of
detection of 32 percent or less. The analytes estimated to exceed LOAELs
(nitrobenzene and RDX) were below the detection limit in all samples analyzed.
These factors indicate uncertainty in the evaluation of risks from energetics to birds
and risks may be overestimated or underestimated.
● Because toxicity data specific for bird and mammal species at the site were not
available, it was necessary to extrapolate toxicity values from test species to site
receptor species. Therefore, risk may be either overestimated or underestimated.
● In this screen, risks for most chemicals were each considered independently. Because
chemicals may interact in an additive, antagonistic, or synergistic manner, evaluation
of single-chemical risk may either underestimate or overestimate risk associated with
chemical mixtures. The risks from inorganic, energetic, PAH, TPH, VOC, and SVOC
chemical classes were each summed to estimate the combined risk. The suitability of
the assumption of additive toxicity is not known; consequently, risk may be either
overestimated or underestimated.
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● Toxicity data was not available to evaluate the effects of all COPECs for all
receptors. The COPECs for which there is no toxicological information and the
potential for causing risks to ecological receptors is uncertain are summarized below:
7.1 Chemical Uncertainties for Plants
1,1,1,2-Tetrachloroethane, 1,1,1-Trichloroethane, 1,1,2,2-Tetrachloroethane, 1,1,2-
Trichloroethane, 1,1-Dichloroethane, 1,1-Dichloroethene, 1,2,3-Trichlorobenzene, 1,2,3-
Trichloropropane, 1,2,4-Trichlorobenzene, 1,2-Dibromo-3-chloropropane, 1,2-
Dichlorobenzene, 1,2-Dichloroethane, 1,2-Dichloropropane, 1,2-Ethylene Dibromide, 1,3-
Dichlorobenzene, 1,4-Dichlorobenzene, 2,4-Dimethylphenol, 2-Butanone, 2-
ChloroethylVinylEther, 2-Chloronaphthalene, 2-Hexanone, 2-Methylphenol, 2-Nitroaniline,
3,3-Dichlorobenzidine, 3-Nitroaniline, 4,6-Dinitro-2-methylphenol, 4-
Bromophenylphenylether, 4-Chloro-3-methylphenol, 4-Chlorophenylphenylether, 4-Methyl-
2-pentanone, 4-Methylphenol, 4-Nitroaniline, Acetone, Benzoic acid, Benzylalcohol, Bis(2-
chloroethoxy)methane, Bis(2-chloroethyl)ether, Bis(2-chloroisopropyl)ether,
Bromodichloromethane, Bromoform, Bromomethane, Carbon disulfide, Carbon
tetrachloride, Chloroethane, Chloroform, Chloromethane, cis-1,2-Dichloroethene, cis-1,3-
Dichloropropane, Dibenzofuran, Dibromochloromethane, Dibromomethane,
Dichlorodifluoromethane, Hexachloroethane, Iron, Isophorone, Magnesium, Methylene
chloride, Nitrate, Nitroglycerin, Nitroguanidine, n-Nitroso-di-n-propylamine, n-
Nitrosodiphenylamine, PETN, Phosphorus, Picric Acid, Strontium, tert-ButylMethylEther,
Trans-1,2-Dichloroethene, Trans-1,3-Dichloropropene, Trichloroethylene (TCE),
Trichlorofluoromethane, Vinyl Acetate, Vinyl chloride
7.2 Chemical Uncertainties for Soil Invertebrates
1,2-Dibromo-3-chloropropane, 1,2-Ethylene Dibromide, 2,4-Dimethylphenol, 2-Butanone, 2-
ChloroethylVinylEther, 2-Chloronaphthalene, 2-Hexanone, 2-Methylphenol, 2-Nitroaniline,
3,3-Dichlorobenzidine, 3-Nitroaniline, 4,6-Dinitro-2-methylphenol, 4-
Bromophenylphenylether, 4-Chloro-3-methylphenol, 4-Chlorophenylphenylether, 4-Methyl-
2-pentanone, 4-Methylphenol, 4-Nitroaniline, Acetone, Aluminum, Benzoic acid,
Benzylalcohol, Bis(2-chloroethoxy)methane, bis(2-chloroethyl)ether, bis(2-
chloroisopropyl)ether, Bromodichloromethane, Bromoform, Bromomethane, Carbon
disulfide, Carbon tetrachloride, Dibromochloromethane, Dibromomethane,
Dichlorodifluoromethane, Hexachlorobenzene, Hexachlorobutadiene,
Hexachlorocyclopentadiene, Hexachloroethane, Iron, Isophorone, Magnesium, Manganese,
Methylene chloride, Molybdenum, Nitrate, Nitroglycerin, Nitroguanidine, PETN,
Phosphorus, Picric acid, Silver, Strontium, tert-ButylMethylEther, Tetrachloroethene, Tetryl,
Trichloroethylene (TCE), Trichlorofluoromethane, Vanadium, Vinyl Acetate, Vinyl chloride
7.3 Uncertainties for Mammals
1,2,3-Trichlorobenzene, 1,2,4-Trichlorobenzene, 1,2-Dibromo-3-chloropropane,
1,2Dichlorobenzene, 1,2-Ethylene Dibromide, 1,3-Dichlorobenzene, 1,4-Dichlorobenzene,
2,4-Dimethylphenol, 2,4-Dinitrophenol, 2-ChloroethylVinylEther, 2-Chloronaphthalene, 2-
Chlorophenol, 2-Nitroaniline, 2-Nitrophenol, 3,3-Dichlorobenzidine, 3-Nitroaniline, 4,6-
Dinitro-2-methylphenol, 4-Bromophenylphenylether, 4-Chloro-3-methylphenol, 4-
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Chloroaniline, 4-Chlorophenylphenylether, 4-Nitroaniline, 4-Nitrophenol, Benzoic acid,
Benzylalcohol, Bis(2-chloroethoxy)methane, bis(2-chloroethyl)ether, bis(2-
chloroisopropyl)ether, Bromodichloromethane, Calcium, Carbon disulfide, Chloride,
Dibenzofuran, Dibromochloromethane, Dibromomethane, Dichlorodifluoromethane, Iron,
Isophorone, Magnesium, Nitrobenzene, Nitroguanidine, n-Nitroso-di-n-propylamine, n-
Nitrosodiphenylamine, Phosphorus, Picric acid, Potassium, Sodium, Styrene, Sulfate, tert-
ButylMethylEther, Trichlorofluoromethane, Vinyl Acetate
7.4 Uncertainties for Birds
1,2-Dibromo-3-chloropropane, 1,2-Ethylene Dibromide, 2,4-Dimethylphenol, 2,4-
Dinitrophenol, 2-ChloroethylVinylEther, 2-Chloronaphthalene, 2-Methylphenol, 2-
Nitroaniline, 2-Nitrophenol, 3,3-Dichlorobenzidine, 3-Nitroaniline, 4,6-Dinitro-2-
methylphenol, 4-Bromophenylphenylether, 4-Chloro-3-methylphenol, 4-Chloroaniline, 4-
Chlorophenylphenylether, 4-Methylphenol, 4-Nitroaniline, 4-Nitrophenol, Antimony,
Benzylalcohol, Beryllium, bis(2-chloroethoxy)methane, bis(2-chloroethyl)ether, bis(2-
hloroisopropyl)ether, Bromodichloromethane, Bromoform, Bromomethane, Calcium, Carbon
disulfide, Carbon tetrachloride, Chloride, Chloroform, Chrysene, Dibenzofuran, Iron,
Isophorone, Magnesium, Methylene chloride, Nitrate, Nitroglycerin, Nitroguanidine, n-
Nitroso-di-n-propylamine, n-Nitrosodiphenylamine, PETN, Phenol, Picric acid, Potassium,
Pyrene, Silver, Sodium, Strontium, Styrene, Sulfate, tert-ButylMethylEther, Tetryl,
Trichloroethylene (TCE), Trichlorofluoromethane, Vinyl acetate, Vinyl chloride
8.0 Conclusions
A SLERA for the Hill AFB TTU site was conducted in two parts: an initial conservative site-
wide screen followed by a refined evaluation. The initial site-wide screen employed
conservative assumptions, and used the maximum detected concentration coupled with no-
effect thresholds to differentiate between analytes that clearly presented no risk and those for
which insufficient data were available to permit their exclusion (e.g., retained analytes). The
refined screen employed biologically more realistic exposure and effects assumptions, and
focused only on retained analytes. Key conclusions of potential risk are described below and
are summarized in Table 28.
8.1 Background Comparison
Nine analytes had concentrations in all samples that were not significantly different from
background (aluminum, beryllium, chromium, iron, manganese, mercury, nickel,
phosphorus, and thallium). An additional six inorganic analytes were significantly greater in
concentration in background samples than on-site samples (arsenic, barium, cobalt,
magnesium, strontium, and vanadium). These 15 analytes were not considered to be site-
associated COPECs and were eliminated from further characterization and analysis.
8.2 Plants
Analytes not exceeding the NOEC-based TRVs included 11 non-detected and 16 detected
chemicals that are not considered to pose a potential risk to terrestrial plants at the Hill AFB
– TTU site. No TRVs could be identified for 49 detected analytes and 24 non-detected
analytes. Consequently, these analytes were retained as uncertainties.
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There were no exceedances of either NOEC or LOEC-TRVs by any detected analytes in the
energetics, SVOCs, and VOC chemical classes. The few and infrequent TRV exceedances
that did occur in these classes were based on detection limits for analytes that were not
detected. Therefore, it was concluded that all analytes in the energetics, SVOC, and VOC
chemical classed do not pose a risk to terrestrial plants at the site.
Of the 30 analytes displaying concentrations in excess of LOECs, the likelihood of potential
effects to the plant community was considered to be low. This was due to exceedances being
driven by non-detected concentrations for 18 COPECs and the low frequency of exceedances
by all detected and non-detected COPECs except zinc and TPH. The frequencies of LOEC
exceedances for five PAHs in site samples were also low. The potential for risk was mostly
associated with OB/OD areas and does not represent the potential for risks in the surrounding
habitat areas of the site. Only metal COPECs showed any NOEC and LOEC exceedances in
ecological habitat. Detected concentrations of antimony, copper, and molybdenum exceeded
the NOEC with a high frequency in ecological habitat areas. These NOEC exceedances ( less
than or equal to 87 percent) indicate that adverse effects are possible, but the lack of LOEC
exceedances suggests that adverse effects to the plant community are unlikely. Selenium
exceeded the LOEC with high frequency (67 percent); however, these exceedances were due
to inadequate detection limits (i.e., all were due to non-detected concentrations), and the
actual risks to plants from selenium are uncertain. The potential for adverse effects to plants
cannot be excluded for zinc due to the high frequency of LOEC-TRV exceedances in both
OB/OD and habitat samples.
8.3 Soil Invertebrates
Screening values were found for 53 of the 87 analytes detected at the site, and for 39 of the
64 analytes not found at concentrations greater than the detection limit. The remaining
34 detected analytes and 25 non-detected analytes without TRVs were retained as
uncertainties. The analytes not exceeding the NOEC-based TRVs included 24 non-detected
and 35 detected chemicals that are not considered to pose a potential risk to soil invertebrates
at the Hill AFB – TTU site.
There were no exceedances of either LOEC-TRVs by any detected analytes in the VOC
chemical classes. The few and infrequent ( less than 13 percent of samples) NOEC or LOEC
exceedances that did occur in these classes were based on detection limits. Therefore, these
classes of chemicals are not considered to pose a risk to terrestrial soil invertebrates at the
site.
Of the 20 analytes displaying concentrations in excess of LOECs, the likelihood of potential
effects to the soil invertebrate community was considered to be low. This was due to
exceedances being driven by non-detected concentrations for 10 COPECs and the low
frequency of exceedances by all detected and non-detected COPECs except TPH. Detected
concentrations of HMX, copper, lead, zinc, 2-methylnaphthalene, fluorene, naphthalene,
phenanthrene, and dibenzofuran each exceeded the LOEC in fewer than 20 percent of site-
wide samples. These low frequencies of LOEC exceedances suggest the absence of adverse
effects to the soil invertebrate community even when OB/OD samples are considered. No
PAH, TPH, VOC, or SVOCs exceed NOECs or LOECs when only samples from within
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habitat areas of the TTU are considered. Only HMX and two metal COPECs showed NOEC
(HMX and zinc) and LOEC (copper) exceedances in ecological habitat areas by detected
concentrations, indicating that samples driving the potential for risk were mostly associated
with OB/OD areas and do not represent the potential for risks in the surrounding habitat areas
of the site. HMX exceeded the NOEC by a low frequency of samples (10 percent) and is not
considered to pose a significant risk to invertebrate communities. Detected concentrations of
copper and zinc exceeded the NOEC with a high frequency in ecological habitat areas. These
NOEC exceedances ( less than or equal to 100 percent) indicate that adverse effects are
possible, but the lack of LOEC exceedances for zinc, and low LOEC exceedance frequency
for copper (5 percent), suggests the likelihood of significant community-level effects is low.
8.4 Mammals
NOEC-TRVs were found for 65 of the 87 detected COPECs at the site, and for 39 of the 64
non-detected COPECs at the site. The remaining 22 detected analytes and 25 non-detected
analytes without TRVs were retained as uncertainties. Overall, NOAEL-based HIs exceeded
1.0 in all species for energetics and inorganics, and in some species for PAHs, petroleum
products, SVOCs, and VOCs.
NOAEL exceedances by five energetics were generally of low magnitude and based on non-
detected concentrations for all except HMX. LOAELs were exceeded at a low magnitude by
only four energetic COPECs (HMX, RDX, 1,3-dinitrobenzene, and 2,6-dinitrotoluene) for
two mammalian receptors (Ord’s kangaroo rat and the grasshopper mouse). However, when
only samples from the habitat area of the TTU are considered, only LOAEL exceedances
based on non-detected RDX and 1,3-dinitrobenzene for the grasshopper mouse remain.
Therefore, the potential for risks from energetics to five of the six mammalian receptor
species in wildlife habitat areas of the TTU is considered unlikely. Risks to mammalian
insectivores (grasshopper mice) from RDX and 1,3-dinitrobenzene cannot be excluded, but
are retained as uncertainties because they are based on non-detects.
Refined exposure estimates resulted in exceedances of NOAELs or LOAELs for antimony,
cadmium, copper, lead, molybdenum, perchlorate, and selenium in at least one receptor. All
were detected except selenium, and represent possible potential for risks to mammalian
wildlife. Samples driving any potential for risk were mostly associated with OB/OD areas
and do not represent the potential for risks in the surrounding wildlife habitat areas. When
only samples from the habitat area of the TTU are considered, no exposure estimates for any
inorganic exceed NOAELs for the coyote, ground squirrel, or pronghorn. NOAELs were
only exceeded for non-detected selenium (kangaroo rat, jackrabbit, and grasshopper mouse)
and detected antimony, cadmium, lead, and molybdenum for the grasshopper mouse.
LOAELs were only exceeded (HQs less than 3.0) for cadmium and selenium for the
grasshopper mouse, and selenium for the kangaroo rat; therefore, there is no potential for
significant risk to four of six mammal species in habitat areas of the TTU. Potential risks to
small mammalian herbivores (kangaroo rats) and mammalian insectivores (grasshopper
mice) from selenium cannot be excluded because they are based on non-detects and are
retained as uncertainties; and, potential for risk to mammalian insectivores from cadmium
also cannot be excluded.
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NOAEL-based TRV exceedances by 10 PAHs were observed for at least one COPEC in each
mammalian receptor, except the coyote. LOAEL exceedances were also observed for
fluorene (kangaroo rat) and 2-methylnaphthalene (grasshopper mouse). However, PAHs are
associated with OB/OD areas and do not represent the potential for risks in the surrounding
wildlife habitat areas of the site. The NOAEL-HI for PAHs is less than 1.0 for all mammalian
receptors when only samples from the habitat area of the TTU are considered. Therefore,
PAHs present no risk to mammals in ecological habitat areas of the TTU.
Screening exposure estimates for TPH only exceeded NOAELs for the grasshopper mouse.
Therefore, petroleum products do not pose a potential for risk to the five other mammalian
receptors at the TTU. The refined exposure estimate for the grasshopper mouse exceeded the
NOAEL, but not when considering concentrations only from wildlife habitat areas of the
TTU. Thus, petroleum products were determined not to pose a potential risk to mammalian
wildlife in habitat areas of the site, and only a possible potential for risk for the grasshopper
mouse over the entire TTU.
SVOCs did not exceed initial screening exposure NOAEL-HIs for any mammalian receptor,
although several non-detected COPECs did exceed individual NOAELs for the jackrabbit,
grasshopper mouse, and coyote. These samples driving the potential for risk from SVOCs are
associated with OB/OD areas and do not represent the potential for risks in the surrounding
wildlife habitat areas of the site. Potential risk to mammalian insectivores (grasshopper mice)
from non-detected 2,4,5-trichlorophenol cannot be excluded, but is retained as an
uncertainty. Otherwise SVOCs present no risk to all other mammals in ecological habitat
areas of the TTU.
Acetone and phenol were the only VOCs that exceeded NOAELs in the refined exposure
estimates. However, the samples driving the potential for risk from VOCs are associated with
OB/OD areas and do not represent the potential for risks in the surrounding wildlife habitat
areas of the site. When only areas of the TTU that provide habitat are considered, NOAELs
were not exceeded by any VOC. The conclusion is that VOCs present no risk to mammals in
ecological habitat areas of the TTU.
8.5 Birds
NOAEL-TRVs were found for 62 of the 87 detected COPECs at the site, and for 34 of the
64 non-detected COPECs at the site. The remaining 25 detected analytes and 30 non-detected
analytes without TRVs were retained as uncertainties. Neither detected nor non-detects
petroleum products or VOCs exceeded their NOAELs for any avian receptor species. Thus,
the potential for risk to birds from these chemical classes is excluded. Refined estimates of
potential exposure identified NOAEL-based HIs greater than 1.0 in all species for inorganics,
and in at least one species for energetics, PAHs, and SVOCs.
Refined estimates of exposure for eight energetic COPECs exceeded NOAELs for all four
avian receptors. These exceedances were based on detected 2,4-dinitrotoluene, which did not
exceed its LOAEL, and on non-detected COPECs where the potential for risks are uncertain.
Samples driving the potential for risk to birds from energetics are mainly associated with
OB/OD areas. No detected energetic COPEC exceeded the NOAEL for any avian receptor
based on samples collected in habitat areas of the TTU. Eight COPECs continue to exceed
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NOAELs in habitat samples, but only non-detected RDX poses a potential for risk to shrikes,
based on the only LOAEL exceedance. The potential for risk to all avian receptors from all
other non-detected energetics exceeding only NOAEL exposures are uncertain. Therefore,
energetics do not present a potential for significant risk to three of four bird species in
wildlife habitat areas of the TTU. Risk to avian insectivores (loggerhead shrikes) from RDX
cannot be excluded because it is based on non-detects, and is retained as an uncertainty.
LOAEL-based HIs for inorganic COPECs were greater than 1.0 for all receptors, ranging
from 5 (sparrow) to 39 (owl). The primary risk drivers for inorganic HIs were cadmium and
lead. Perchlorate and zinc also exceeded shrike and owl NOAELs, but the possible potential
for adverse effects to these receptors is low because the LOAELs were not exceeded.
Cadmium, lead, perchlorate, and zinc EPCs driving NOEAL and LOAEL exceedances were
also influenced by a few very high concentrations collected within OB/OD areas, primarily at
the inactive burn pan site. When only samples from the habitat area of the TTU are
considered, no exposure estimates for any inorganic COPEC exceed the LOAEL for any
species. NOAEL exceedances for cadmium and lead in habitat areas were also of low
magnitude (HQs less than 3.0). The conclusion is that potential risks from inorganics are
associated with OB/OD areas and do not represent the potential for risks in the surrounding
wildlife habitat areas of the site. Inorganics do not present a significant risk to any of the four
bird species in ecological habitat areas of the TTU.
Screening exposure estimates for PAHs did not exceed burrowing owl NOAELs. Although
screening-level HIs for PAHs were greater than 1.0 for the sparrow, shrike, and meadowlark,
only detected 2-methylnaphthalene exposures exceeded the shrike and meadowlark NOAELs
in the refinement (HQs less than 3.0). PAHs in samples representing habitat areas within the
TTU did not exceed NOAELs. Therefore, there is no potential for risk to avian receptors
from PAHs in habitat areas at the TTU.
Screening exposure estimates for SVOC did not exceed NOAEL-HIs for the sparrow,
meadowlark, or owl. While the screening-level HI for the shrike exceeded 1.0, the refined
exposure estimate was equal to 1.0. Bis(2-ethylhexyl)phthalate exposure to the shrike was
equal to the NOAEL. No LOAEL was available for comparison to the exposure dose, but the
low magnitude of this exceedance indicates that the likelihood of adverse effects is low.
Otherwise, only non-detected SVOCs exceeded their NOAELs or LOAELs in the refined
screening assessment. No exposure estimate for any SVOC exceeded a LOAEL for any
species due to samples from habitat area of the TTU. Non-detected phthalates continue to
exceed NOAELs for phthalate exposure to the shrike and meadowlark in wildlife habitat
samples. However, the potential for possible adverse effects from these COPECs is
considered low due to rapid environmental degradation, biotransformation, and inappropriate
bioaccumulation modeling. The conclusion is that potential risks from SVOCs are uncertain
in OB/OD areas and are not significant in the surrounding wildlife habitat areas of the site.
8.6 Possible Actions to Reduce Potential Risks
The potential for risks over the entire TTU site could not be excluded for zinc to plants;
TPHs to plants and invertebrates; and HMX, antimony, cadmium, copper, lead, perchlorate,
2-methylnaphthalene, fluorene, total-PAHs, and acetone to one or more wildlife receptors.
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Samples driving the potential for risks to receptors are generally associated with OB/OD
areas, primarily at the inactive burn pan site, and do not represent the potential for risks in the
surrounding wildlife habitat areas of the site due to incomplete exposure pathways.
In an effort to reduce potential risk at the TTU, several ongoing actions are in place to assist
in the continual assessment and refinement of risk to receptors. These actions include: 1) the
continued collection of chemical data and refinement of the risk assessment, including the
revised soil sampling strategy for 2005, aimed at characterizing average chemical
concentrations within the operational areas of the TTU; and 2) continued control and
documentation of materials treated at the TTU, in accordance with the RCRA Part B permit,
to prevent the introduction of unknown or excess environmental hazards. These items are
addressed as part of the RCRA Part B Permit compliance activities that include the periodic
review of both the human health and ecological risk assessments and the preparation of the
Waste Characterization Technical Memorandum.
Remediation of OB/OD areas, once operations have ceased, will eliminate or reduce any
significant potential for risk to receptors at the TTU. The only detected COPECs to pose a
potential for adverse effects to receptors in habitat areas were cadmium for the grasshopper
mouse (LOAEL-HQ = 1.8) and zinc for plants (LOEC exceedances = 57 percent; LOEC-
HQmax = 1.3). These risk conclusions are based solely on literature-based toxicity, life
history, and bioaccumulation data and, therefore, may not accurately reflect site conditions.
When operations at the TTU have ceased and remedial plans are being developed for the
OB/OD areas of the site, more detailed analyses, to include site-specific bioassays and
bioaccumulation studies, may be considered to address retained risks from cadmium and zinc
in the habitat areas of the site. Site-specific data developed from these studies could result in
a more definitive risk determination and would support the development of site-specific
remedial goals.

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Verschuuren, H. G., R. Kroes, E. M. Den Tonkelaar, J. M. Berkvens, P. W. Helleman, A. G.
Rauws, P. L. Schuller, and G. J. Van Esch. 1976a. Toxicity of methyl mercury
chloride in rats. I. Short-term Study. Toxicol. 6: 85-96.
Verschuuren, H. G., R. Kroes, E. M. Den Tonkelaar, J. M. Berkvens, P. W. Helleman, A. G.
Rauws, P. L. Schuller, and G. J. Van Esch. 1976b. Toxicity of methyl mercury
chloride in rats. II. Reproduction study. Toxicol. 6: 97-106.
Verschuuren, H. G., R. Kroes, E. M. Den Tonkelaar, J. M. Berkvens, P. W. Helleman, A. G.
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Utah Test and Training Range
Attachment 10A - TTU Ecological Risk Assessment
Issued DRAFT

10A-70

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America, No. 231, 1996.

Tables
Table 1
Environmental Fate and Transport of Detected Chemicals
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Chemical Environmental Fate Reference
Aluminum
Aluminum has only one oxidation state (3+); thus, its fate and transport in the environment
depends upon its coordination chemistry and the characteristics of the local environmental
system. Aluminum does not exist as a free metal in nature due to its reactivity; it partitions
between the solid and liquid phases by reacting with water, chloride, fluoride, sulfate, nitrate,
phosphate, humic materials, and clay. The greater the mineral content of the soil, the lower
the mobility of aluminum. In water, aluminum forms relatively water-insoluble complexes, or
is found as a water-soluble complex. Aluminum undergoes hydrolysis to form hydroxy
aluminum species and pH determines the hydrolysis products that are formed. Aluminum
adsorbs to suspended solids and sediment. At a pH greater than 5.5, aluminum compounds
exist predominantly in undissolved forms. Decreasing pH generally results in an increase in
mobility for monomeric forms of aluminum.
Bodek et al., 1988; and others in
TOXNET
Antimony
Antimony usually occurs with the valence of 3+ and occasionally of 5+. Antimony binds to
soil particles, particularly those containing iron, manganese, or aluminum. In water,
antimony is oxidized when exposed to atmospheric oxygen.
TOXNET
(http://toxnet.nlm.nih.gov/)
Arsenic
The physical characteristics of the soil matrix determine the dominant form of arsenic and its
transport. Insoluble arsenic compounds bind tightly to organic matter in soil or sediment.
Various forms of arsenic in soil are interconverted by chemical reactions and microbial
activity. The bioavailability of arsenic in soil is inversely proportional to the organic carbon
and clay content of the soil matrix. Arsenic in soil is directly taken up by plants and soil
microbes and invertebrates, and indirectly taken up by terrestrial receptors via ingestion. In
surface water, soluble inorganic arsenate (As5+) predominates under normal conditions and
is more stable than arsenite. Movement and partitioning of arsenic in water depends on the
chemical form of arsenic and on interactions with other materials present. Soluble forms of
arsenic remain dissolved in the water column or adsorb onto sediments or soils, especially
those containing clays, iron oxides, aluminum hydroxides, manganese compounds, and
organic matter. Sediment bound arsenic is released back into the water by chemical or
biological interconversions and is influenced by the oxidation-reduction potential,
Callahan et al., 1979; NRCC,
1978; Woolson, 1975; and others
in TOXNET
pH, temperature, other metals, salinity, and biota.
Uptake by plants from soil is influenced by soil elements, temperature and plant species.
Aquatic organisms accumulate arsenic but do not biomagnify it. Arsenic is accumulated by
aquatic organisms primarily through dietary exposure. Bioavailability is not dependent on the
concentration of acid-volatile sulfides (AVS). Sediments are the major source of arsenic to
infaunal organisms.
Barium
In water, barium precipitates out of solution as an insoluble salt or adsorbs to suspended
particulate matter. Barium in sediments is found mostly in the form of barium sulfate. Barium
is not very mobile in most soil systems. The rate of transportation of barium in soil is
dependent on soil characteristics such as cation exchange capacity and calcium carbonate
content. Barium naturally forms compounds in the 2+ oxidation state. Only trace amounts of
barium dissolve in surface water. In general, the solubility of barium compounds increases
with decreasing pH.
Bodek et al., 1988; Kabata-
Pendias and Pendias, 1984; and
others in TOXNET
Cadmium
Cadmium exists primarily in the 2+ oxidation state. Cadmium in the water column can
partition to dissolved and particulate organic carbon. Cadmium speciation yields primarily
the divalent form (2+) between pH conc of 4.0 and 7.0 and it is this divalent form that is
believed to be responsible for observed biological effects. Cadmium compounds in soil are
stable and are not subject to degradation. Compounds can be transformed by precipitation,
dissolution, complexation, and ion exchange. In aquatic environments, cadmium
compounds are not affected by photolysis, volatilization, or biological methylation.
Precipitation and sorption to mineral surfaces and organic materials are important removal
processes. Concentrations are generally higher in sediments than in overlying water.
ATSDR, 1990a; Callahan et al.,
1979; and others in TOXNET
Cadmium readily bioconcentrates in Daphnia sp., aquatic insects, mollusks, and crayfish.
Fish uptake occurs through both water and diet, however water is the primary uptake
source. In mammals and birds, cadmium accumulates in the livers and kidneys following
ingestion. The concentration of AVS is an important factor controlling the toxicity and
bioaccumulation of cadmium in sediments.
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Table 1
Environmental Fate and Transport of Detected Chemicals
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Chemical Environmental Fate Reference
Chromium
In soil, chromium 3+ is readily hydrolyzed and precipitated as chromium hydroxide. It exists
in soil primarily as insoluble oxide with very limited mobility. In water, chromium 6+ can
occur in the soluble state. It can be adsorbed onto clay-like materials, organics, or iron
oxides. chromium 6+ persists in water for 140 days, but is eventually reduced to chromium
3+ by organic matter or other reducing agents in water.
Plants can bioaccumulate and reduce chromium. In aqueous solutions, within a pH range of
6 to 8, hexavalent chromium is distributed between two species: monovalent hydrochromate
anion and divalent chromate anion. A log bioconcentration factor (BCF) of 2.74 was
reported for Daphnia magna. Hexavalent chromium tends to accumulate in the gills of fish
following exposure.
Copper occurs naturally in many organisms and is an essential micronutrient. Copper may
exist in two oxidation states: 1+ or 2+. Copper (1+) is unstable and oxidizes to the 2+ state
in many aerated waters within the pH range of 6 to 8. In the aquatic environment, the fate of
copper is determined by the formation of complexes. Copper concentrations remaining in
solution depend on water chemistry, such as pH and temperature, and the concentration of
other chemical species. The majority of copper released to surface waters settles out or
adsorbs to sediments. Some copper complexes with both inorganic and organic ligand.
Callahan et al., 1979; and others
in TOXNET
As an essential nutrient, copper is strongly bioaccumulated by plants and animals. All
organisms have active transport mechanisms for it, but it does not biomagnify. Biogenic
ligands play an important role in complexing copper (which affects precipitation and sorption
behavior), an biological activity is a major factor in determining the distribution and
occurrence of copper in the ecosystem. Free copper ions are the most bioavailable
inorganic forms. The amount of bioavailable copper in sediment is controlled mostly by the
concentration of AVS and organic matter. Copper is accumulated by aquatic organisms
primarily through dietary exposure.
Iron
In the hydrosphere, iron minerals in igneous and metamorphic rocks are the primary
sources of iron. Mobilization and redistribution occur with chemical weathering. Iron
mobilizes mostly as dissolved Fe(II) in reducing conditions and as particulate Fe(III)
oxyhydroxides in oxygenated conditions. In reducing conditions, Fe(II) is soluble and mobile
below ~ pH 7 to 8. In oxidized surface waters and sediment, dissolved iron, Fe 3+ and Fe
(III) inorganic complexes, are mobile below ~ pH 3 to 4. Fe (III) as ferric-organic complexes,
are also mobile in many soils and in surface and groundwaters up to ~ pH 5 to 6; as
colloidal ferric oxyhydroxides between ~ pH 3 to 8.
TOXNET
(http://toxnet.nlm.nih.gov/
Lead
In water, lead is most soluble and bioavailable under conditions of low pH, low organic
content, low suspended sediment concentrations, and low concentrations of salts of other
metals. Therefore, the solubility in water is low. Most lead in natural waters is precipitated to
sediment as carbonates and hydroxides. Lead is readily precipitated by many common
anions. In sediments, lead is mobilized and released during sharp decreases in pH.
In soils, the major sink for lead, is relatively immobile and can persist for long periods of
time in numerous forms. Adsorption or precipitation of in soils is promoted by presence of
organic matter, carbonates, and phosphate minerals. It usually accumulates in topsoil due
to complexation with organic matter and the transformation of soluble lead compounds to
relatively insoluble sulfate or phosphate derivatives. The efficient fixation of lead by most
soils greatly limits the transfer of lead to aquatic systems and also inhibits absorption of lead
by plants. However, leaching of lead can be relatively rapid from some soils, especially at
highly contaminated sites or landfills.
Aquatic biota (invertebrate and vertebrate) can bioconcentrate lead at levels greater than in
water, and sometimes similar to those in sediments. Concentrations of lead tend to
decrease with increasing aquatic trophic levels. However, lead does not appear to
bioconcentrate significantly in fish but does in some shellfish such as mussels. Lead is
accumulated by aquatic organisms equally from water and through dietary exposure.
Bioaccumulation of organolead compounds is rapid and high and concentrated in the fatty
tissues of aquatic organisms. Log BCFs of 5.15 (cladoceran) and 3.56 (midge) were
reported in the literature.
TOXNET
(http://toxnet.nlm.nih.gov/)
Copper
Hodson et al., 1984; and others
in TOXNET
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Table 1
Environmental Fate and Transport of Detected Chemicals
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Chemical Environmental Fate Reference
Manganese
Manganese transport and partitioning is controlled by the solubility of the chemical form
present, which is determined by pH, oxidation-reduction potential, and the characteristics of
available anions. Manganese may exist in water in any of four oxidation states (2+, 3+, 4+,
or 7+). Mn 24 is most common in waters (pH 4-7) but may become oxidized at pH greater
than 8 or 9. Adsorption to soil and sediment may be highly variable because adsorption
depends on the cation exchange capacity and the organic composition of the substrate.
Manganese in water may undergo oxidation at high pH or oxidation-reduction potential and
is also subject to microbial activity.
Kabata-Pendias and Pendias,
1984; and others in TOXNET
Mercury
In soil, mercury exists in the mercuric (Hg+2) and mercurous (Hg+1) states. Mercury adsorbs
to soil or is converted to volatile forms. Mercury can migrate by volatilization from aquatic
and terrestrial sources through the reduction of metallic mercury to complex species.
Atmospheric transport is a major environmental distribution pathway. Mercury 2+ is the
predominant form of mercury in surface waters. Nonvolatile mercury in surface water binds
to organic matter and sediment particles.
Where mercury is found in soil, water and sediment methylmercury may also be found since
it is both produced and destroyed by microbial processes involving mercury compounds.
Fish and other aquatic orgamanisms readily bioconcentrate methyl mercury either directly
through water or through components of the food chain. Subsequently, fish eating birds
tend to show the highest concentrations. Factors which affect the observed levels of
mercury in plants and animals at different trophic levels include age, surface area,
metabolism, habitat, and activity. There is an inverse relationship between total mercury and
percent methylmercury in tissues of various avian species. Among mammals, mercury
burdens are higher in fish-eating species than in herbivorous ones. Bioconcentration factors
for methylmercury are highly variable. Log BCFs for methylmercury in brook trout range
from 4.84 to 5.80.
Bioaccumulation factors increased with higher levels in both the pelagic and benthic
components of aquatic food webs. Fish bioconcentrate methylmercury directly from water by
uptake across the gills and piscivores readily accumulate mercury from dietary sources.
Mercury is accumulated by all trophic levels with biomagnification occurring up the food
web. The transfer of mercury through the food web is affected by the form of mercury.
Although inorganic mercury is the dominant form in the environment and easily
accumulated, it is also depurated quickly. Methylmercury accumulates quickly, depurates
very slowly, and therefore has a greater potential to biomagnify in higher trophic-level
species.
Nickel
Most nickel released into waterways is associated with particulate matter. Nickel is strongly
adsorbed at mineral surfaces such as oxides and hydrous oxides of iron, manganese, and
aluminum. It is strongly adsorbed by soil. Soil pH and clay content most influence nickel
sorption. The 2+ valence is the predominant species in solution.
Nickel BCFs ranging from 40-100 suggest that the potential for bioconcentration in aquatic
organisms is low to moderate. Although aquatic organisms may accumulate nickel from
their surroundings, there is little evidence for significant biomagnification along the food
chain. Water-soluble nickel compounds, such as the chloride and sulfate compounds, are
poorly absorbed by most living organisms. The uptake of nickel by plants depends upon the
extractable nickel content of a soil which is a function of physical, chemical and biological
factors of the soil environment. Higher nickel concentrations have been observed in shellfish
and crustacea than in fish.
Bioaccumulation of nickel is most pronounced in sediments when the ratio of simultaneously
extracted metals to acid-volatile sulfide (SEM/AVS) is greater than 1. Although nickel
concentrations in animals from sediments with SEM/AVS ratios >1 were approximately 2- to
10-fold greater than nickel concentrations in benthic organisms from sediments with
SEM/AVS <1, nickel uptake (tissue concentration) was proportional to the concentration in
sediment.
SRC, 2000; and others in
TOXNET
Callahan et al. 1979; ATSDR,
1994; Eisler, 2000; and others in
TOXNET
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Table 1
Environmental Fate and Transport of Detected Chemicals
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Chemical Environmental Fate Reference
Silver
Transport and partitioning is influenced by the particular form of the compound. Under
oxidizing conditions, the primary silver compounds would be bromides, chlorides, and
iodides, while under reducing conditions the free metal and silver sulfide would
predominate. Mobility in soils is affected by oxidation-reduction potential, pH, and the
presence of organic matter. In fresh water, silver often forms complex ions with chlorides,
ammonium, and sulfates; forms soluble organic compounds; and adsorbs onto humic
complexes and suspended particulates. Silver tends to form complexes with inorganic
chemicals and humic substances in soil.
TOXNET
(http://toxnet.nlm.nih.gov/
Thallium
In soil, thallium exists in either the monovalent (thallous) or trivalent (thallic) form. The
monovalent form is more common and stable. Thallium is reactive with air and moisture.
Moisture increases the oxidation of thallium. Thallium adsorbs to soil and is not transformed
or biodegraded. Elemental thallium is relatively insoluble in water.
Callahan et al., 1979; and others
in TOXNET
Zinc
Zinc occurs naturally in the 2+ oxidation state. Sorption to suspended and bed sediments is
the dominant reaction involving zinc. The relative mobility of zinc in soil and aquatic systems
is determined by factors such as the solubility of the compound, pH, redox potential, and
salinity. Zinc generally remains as a free ion at low pH conc.s. It partitions to sediments or
suspended solids in surface water through sorption onto hydrous iron and manganese
oxides, clay minerals, and organic material. Zinc tends to sorb more readily at a high pH
(pH>7) than at a low pH. Zinc sorbs strongly onto soil particulates and its mobility depends
on the solubility of the speciated forms of the element and on soil properties such as cation
exchange capacity, pH, redox potential, and the chemical species present in soil.
Callahan et al., 1979; and others
in TOXNET
Zinc compounds have low mobility in soils and are absorbed by plants and vegetables.
Adsorbtion to suspended solids and sediments is expected. Studies indicate that zinc is not
a highly mobile element in most aquatic habitats. In fish, zinc tends to accumulates in the
gills, liver, kidney and opercular bone, but not the muscle. A log BCF of 2.90 was
determined for the midge Chironomus riparius.
Polynuclear
Aromatic
Hydrocarbons
(PAHs)
Polynuclear aromatic hydrocarbons are a diverse group of organic molecules composed of
two or more fused aromatic (benzene) rings. They are moderately persistent in the
environment. In general, as the number of rings increases, mobility and volatility decrease.
Because of these physical-chemical properties, PAHs have low solubility, low volatility, and
a high tendency to sorb to organic matter. In water, PAHs have high boiling points and are
insoluble. When oil is spilled in water, PAH in the oil can enter the water column in
dispersed form or be absorbed on organic and inorganic compounds. In the terrestrial
environment, PAHs tend to be associated with soil particulates and have low mobility in soil.
Eisler, 2000; and others in
TOXNET
PAHs generally do not biomagnify in food chains despite high lipid solubility, because they
are rapidly metabolized. However, some PAHs can be detected in tissues of aquatic
organisms and wildlife at high concentrations immediately following exposure. In general,
biodegradation rates are inversely related to the number of fused benzene rings and are
further slowed by substitutions, including alkylation. Bioaccumulation and metabolism vary
greatly among clams, invertebrates, shrimp, and fish. Bioaccumulation was substantially
higher for amphipods than for clams, shrimp, or fish. Clams unable to metabolize PAHs had
higher concentration levels of PAHs than amphipods, shrimp, and fish.
Bis(2-
Ethylhexyl)Phth
alate
In the environment, bis(2-ethylhexyl)phthalate undergoes biodegradation in water and soil.
It is predicted to react with hydroxyl radicals in the atmosphere. It has an estimated half-life
of 12 hours in the air, 10 - 20 days in soil, and days to weeks in water. The half-life of the
molecule, due to evaporation from bodies of water, is about 15 years. Bis(2-
ethylhexyl)phthalate rapidly degrades in the marine environment by experimental
microcosms. This chemical has been found to bind organic acids in the soil and water,
resulting in an increase in its solubility and mobility in the environment. It also absorbs to
both freshwater and marine sediments.
Callahan et al., USEPA, 1987;
and others in TOXNET
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Table 1
Environmental Fate and Transport of Detected Chemicals
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Chemical Environmental Fate Reference
Dibenzofuran
In the atmosphere, dibenzofuran exists primarily in the gas-phase and sometimes in the
particulate -phase. As a gas, this chemical reacts with photochemically - produced hydroxyl
radicals and has a half-life of 4.1 days. As a particulate, wet and dry deposition are
expected to be the dominant tropospheric removal process. In soil, this chemical has very
low mobility. It is biodegraded in areas where populations of adapted microorganisms are
present. In an aquatic environment, dibenzofuran is expected to strongly absorb to
particulates and sediment. Dissolved dibenzofuran may volatilize from water. Adapted
microbes supplied with sufficient oxygen can readily biodegrade dibenzofuran.
SRC, 2000; and others in
TOXNET
2,4-DNT
If released to air, 2,4-dinitrotoluene will exist solely as a vapor in the ambient atmosphere.
Vapor-phase 2,4-dinitrotoluene will be degraded in the atmosphere by reaction with
photochemically-produced hydroxyl radicals; the half-life for this reaction in air is estimated
to be 75 days. If released to soil, it is expected to have moderate mobility based upon an
estimated KOC of 360. Volatilization from moist soil surfaces is not expected to be an
important fate process based upon an estimated Henry's Law constant of 1.3X10-7 atm-cu
m/mole. 2,4-Dinitrotoluene may undergo direct photolysis in soil, based on the rapid rate of
photolysis of 2,4-dinitrotoluene in water. If released into water, 2,4-dinitrotoluene is expected
to adsorb to suspended solids and sediment in water based upon the estimated KOC.
Volatilization from water surfaces is not an important fate process based upon this
compound's estimated Henry's Law constant. An estimated BCF of 7 suggests the potential
for bioconcentration in aquatic organisms is low.
SRC, 2000
HMX
When found in water, photolysis was found to be the dominant transformation process with
half-lives ranging from 17 to 7900 days depending on the water body. Major photolytic
transformation products were nitrate, nitrite, and formaldehyde. Poor light trasmission in
rivers was found to inhibit photolytic processes. One study suggests that HMX will be
persistent in water with dilution serving as the major factor in reducing concentrations.
Biotransformation of HMX may occur under both anaerobic and aerobic conditions resulting
in mono-through tetra-nitroso derivatives of HMX as metabolites which are eventually
metabolized to 1,1-dimethylhydrazine. Studies show that HMX is likely to move from soil into
groundwater, particularly in sandy soils though this movement is expected to be slow.
ATSDR, 1997a (Public Health
Statement)
Nitroguanidine
If released to air, 1-nitroguanidine will exist solely in the vapor phase in the ambient
atmosphere. Vapor-phase 1-nitroguanidine will be degraded in the atmosphere by reaction
with photochemically-produced hydroxyl radicals; the half-life for this reaction in air is
estimated to be 18 hrs. If released to soil, this chemical is expected to have very high
mobility based upon an estimated Koc of 25. Volatilization from moist soil surfaces is not
expected to be an important fate process based upon an estimated Henry's Law constant of
4.4X10-12 atm-cu m/mole. If released into water,it is not expected to adsorb to suspended
solids and sediment in water based upon the estimated Koc. Volatilization from water
surfaces is not expected to be an important fate process based upon this compound's
estimated Henry's Law constant. An estimated BCF of 3.2 suggests the potential for
bioconcentration in aquatic organisms is low.
SRC, 2000
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Table 1
Environmental Fate and Transport of Detected Chemicals
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Chemical Environmental Fate Reference
Picric Acid
If released to air, Picric acid otherwise known as 2,4,6-trinitrophenol, will exist in both the
vapor and particulate phases in the ambient atmosphere. Vapor-phase 2,4,6-trinitrophenol
will be degraded in the atmosphere by reaction with photochemically-produced hydroxyl
radicals; the half-life for this reaction in air is an estimated 433 days. Particulate-phase 2,4,6-
trinitrophenol may be removed from the air by wet and dry deposition. If released to soil, this
acid is expected to have high mobility based upon an estimated Koc value of 130. This
compound will exist primarily as an anion in moist soil surfaces and anions are expected to
have very high mobility in soils. Volatilization of 2,4,6-trinitrophenol from moist soil surfaces
is not expected to be an important fate process since the anion will not volatilize and the
neutral species has a Henry's Law constant of 1.7X10-8 atm-cu m/mole at 25 deg C. 2,4,6-
Trinitrophenol is not expected to volatilize from dry soil surfaces based upon its vapor
pressure. If released into water, 2,4,6-trinitrophenol is not expected to adsorb to suspended
solids and sediment in the water column based on the KOC values. A BCF value of less than
SRC, 2000
2.4 measured in carp suggests bioconcentration in aquatic organisms is low.
TPH
When TPH is released directly to water through spills or leaks, certain TPH fractions will
float in water and form thin surface films. Other heavier fractions will accumulate in the
sediment at the bottom of the water, which may affect bottom-feeding fish and organisms.
Some organisms found in the water (primarily bacteria and fungi) may break down some of
the TPH fractions. TPH released to the soil may move through the soil to the groundwater.
Individual compounds may then separate from the original mixture, depending on the
chemical properties of the compound. Some of these compounds will evaporate into the air
and others will dissolve into the groundwater and move away from the release area. Other
compounds will attach to particles in the soil and may stay in the soil for a long period of
time, while others will be broken down by organisms found in the soil.
ATSDR, 1999 (Public Health
Statement)
Nitrate
Nitrate (NO3
-) is one of the many essential compounds in the nitrogen cycle. Nitrate is the
preferred form of nitrogen as a macro-nutrient for most organisms. Nitrate is produced as a
bi-product of nitrification from NH3 and NH4
+, with NO2- as an intermediary. Nitrate is nor
held well in soils and consequently leaches readily into aquatic systems including
groundwater and surface water runoff. Nitrate is typically high in areas where nitrogen is
applied to fields such as farms and golf courses. Within both terrestrial and aquatic systems
nitrate is reduced to N2 through the process of denitrification. Nitrate can also be an
intermediary in the process of nitrogen fixation in anaerobic environments.
McDowell, 1992
Phosphorus
Phosphorus exists in abundance in the earth's crust making up approximately 0.12 percent.
It does not occur free in nature but is found in the form of phosphates in minerals. It is also
found in fertile soils and is an essential constituent of protoplasm, nervous tissue and bones.
In plants, active uptake occurs and generally accumulates in the living top part.
Biomagnification of phosphorus was not found in a Precambrian Shield lake ecosystem
within clams, fish, birds, and mammals.
Budavari, 1989; and others in
TOXNET
Acetone
Acetone is expected to exist as a vapor in the ambient atmosphere. It is degraded in the
atmosphere by reaction with photochemically-produced hydroxyl radicals and also
undergoes photodecomposition by sunlight. Acetone has high mobility in soils and
volatilization from moist and dry soils is expected to occur. In water, this chemical is not
expected to absorb to suspended solids or sediment. Volatilization from water surfaces is
an important fate process. Bioconcentration in aquatic organisms is considered low based
on the BCF value of 1.
Lyman et al., 1990; SRC, 2000;
and others in TOXNET
2-Butanone
Methyl Ethyl Ketone is expected to exist solely as a vapor in the ambient atmosphere. It is
degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals. It
is also able to undergo photolysis in the natural light. Based on Koc values of 29 and 34 (in
silty loams), Methyl Ethyl Ketone is expected to have high mobility in soils. Volatilization
from moist and dry soil surfaces are expected. This chemical is not expected to absorb to
suspended solids or sediment in water. Bioconcentration in aquatic organisms is considered
low due to the estimated BCF value of 1. The most common exposure to methyl ethyl
ketone is through inhalation and ingestion of contaminated water or food.
Walton, et al., 1992; SRC, 2000;
and others in TOXNET.
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/1 Page 6 of 7
Table 1
Environmental Fate and Transport of Detected Chemicals
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Chemical Environmental Fate Reference
Benzene
In the ambient atmosphere, benzene will exist as a vapor with a vapor pressure of 94.8 mm
Hg at 25 deg C. Vapor-phase benzene will be degraded by a reaction with photochemically-
produced hydroxyl radicals and the half-life of this reaction is about 13 days. It can also be
degraded by ozone radicals and nitrate found in the atmosphere. Benzene is expected to
have high mobility in soil and volatilization in moist soil is an important fate process.
Benzene may volatilize from dry soil based on vapor pressure. In an aquatic environment,
volatilization is the important fate process. Inhalation of ambient air, ingestion of drinking
water, and dermal contact are routes of exposure.
SRC, 2000; and others in
TOXNET.
Xylenes
Based upon an experimental vapor pressure of 7.99 mm Hg at 25 deg C, xylene is expected
to exist entirely in the vapor phase in the ambient atmosphere. Vapor-phase xylene is
degraded in the atmosphere by reaction with photochemically-produced hydroxyl radicals
with an estimated atmospheric lifetime of about 1-2 days. Xylene is expected to have
moderate to high mobility in soils based upon experimental Koc values obtained with a
variety of soils at differing pH values and organic carbon content. Volatilization from moist
soil surfaces is expected based on an experimental Henry's Law constant of 7.0X10-3 atm-
cu m/mole. Biodegradation is an important environmental fate process for xylene. In
general, it has been found that xylene is biodegraded in soil and groundwater samples
under aerobic conditions and may be degraded under anaerobic denitrifying conditions. In
water, xylene is expected to adsorb somewhat to sediment or particulate matter based on its
measured Koc values. This compound is expected to volatilize from water surfaces given its
experimental Henry's Law constant.
SRC, 2000
Estimated half -lives for a model river and model lake are 3 and 99 hours. The potential for
bioconcentration is aquatic organisms is low based on an experimental BCF value of 20,
measured in eels.
Styrene
If released to air, a vapor pressure of 6.40 mm Hg at 25 deg C indicates styrene will exist
solely as a vapor in the ambient atmosphere. Vapor-phase styrene will be degraded in the
atmosphere by reaction with photochemically-produced hydroxyl radicals and ozone; the
half-life for these reactions in air are estimated to be 7 and 16 hrs, respectively. Direct
photochemical or photolytic reactions for styrene are slow. If released to soil, styrene is
expected to have low mobility based upon an estimated Koc of 960. Volatilization from moist
soil surfaces is expected to be an important fate process. Biodegradation by aerobic
microorganisms may lead to extensive or complete destruction of styrene in soil. If released
into water, styrene is expected to adsorb to suspended solids and sediment based upon the
estimated Koc. Degradation of styrene is rapid in sewage under aerobic conditions.
SRC, 2000
Volatilization from water surfaces is expected to be rapid. A BCF of 13.5 for goldfish
suggests bioconcentration in aquatic organisms is low. Styrene is not expected to undergo
hydrolysis in the environment due to the lack of hydrolyzable functional groups.
Perchlorate
Perchlorate (ClO4) is an anion that originates as a contaminant in ground water and surface
waters from the dissolution of ammonium, potassium, magnesium, or sodium salts.
Because perchlorate is nonlabile kinetically (i.e., the reduction of the central chlorine atom
occurs extremely slowly) and sorption or natural chemical reduction in the environment is
not significant, perchlorate is exceedingly mobile in aqueous systems and can persist for
many decades under typical ground and surface water conditions.
USEPA, 2002
Notes:
Information on the fate and transport of chemicals was researched through TOXNET (http://toxnet.nlm.nih.gov/) in the Hazardous Substances Data Bank.
Additional citations for the primary references listed can be found on the HSDB summary for each chemical listed.
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/1 Page 7 of 7
Table 2
Mechanisms of Ecotoxicity
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Mechanisms of Ecotoxicity References
Aluminum Aluminum is a cytotoxin that interferes with enzymes associated with adenosine triphosphate and
maintenance of neurotransmitters; it disrupts neuromotor activity and cognitive abilities; decreases
offspring growth, body weights and neurological development; increases resorption rates; alters
calcium and phosphorus metabolism; causes embryo lethality; minor skeletal malformations; decrease
in egg shell strength and production.
ATSDR, 1992a; and others in
TOXNET
Antimony Mutagenic in bacteria or phage; induces chromosomal aberrations or abnormal cell division; antimony
combines with sulfhydryl groups in several respiratory enzymes; trivalent antimony induces heme
oxygenase, which causes heme degradation in the liver and kidney; causes pulmonary, hepatic and
reproductive effects in mammals.
ATSDR, 1990ba; and others in
TOXNET
Arsenic Reaction of trivalent form (arsenite) with sulfhydryl groups leads to enzyme (oxidative respiration)
inhibition. Methylated arsenic is transferred efficiently in food webs, but does not bioacccumulate.
Arsenic reduces growth and development in plants and causes inhibition of light activation, wilting,
chlorosis, browning, dehydration and death in plants. Arsenic causes malformations and death in toad
embryos. It is carcinogenic and mutagenic and causes impaired behavior, reduced growth, lack of
appetite, suffocation by gill clogging and vascular collapse in the gills, testicular and ovarian
degeneration, liver damage, and failure to metabolize food in fish. Inorganic arsenic destroys the
blood vessel lining in the gut and lowers blood pressure in birds. It also causes hepatocyte damage in
birds by inhibition of the sodium pump. Behavioral, systemic, growth, systemic and reproductive
effects occur as a result of chronic exposures. It is teratogenic, carcinogenic and possibly mutagenic
in mammals. Its developmental effects include malformations (exencephaly, eye defects and renal
and gonadal agenesis) and fetal death in mammals.
Sadiq 1992; Eisler, 2000; Stanley
et al. 1994; Whitworth et al. 1991;
Camardese et al. 1990; ATSDR,
1993a; Mance, 1990; and others in
TOXNET
Barium Barium can inhibit intestinal absorption in the winter flounder. Barium accumulates in plants and the
bones in birds and mammals. It affects potassium metabolism in muscles and causes respiratory
weakness, muscle paralysis and stimulation, irregular cardiac contractions and lowered pulse rate in
mammals. Some reproductive effects (reduced ovary weight) have been observed.
Amdur et al. 1991; ATSDR 1990c;
Schroeder 1970 as cited in
ATSDR 1990b; Charney and
Taglietta 1992; Borzelleca et al.,
1988.
Cadmium Cadmium causes mutagenesis, teratogenesis, carcinogenesis; It inhibits enzyme reactions by
replacement of essential divalent nutrients (e.g., zinc) at critical sites on proteins and enzymes;
combines with sulfhydryl groups in enzymes; inhibition of Phase I and Phase II biotransformation
reactions; kidney lesions; reduces growth rates and feed consumption; causes reproductive effects in
birds; testicular damage; decreases hemoglobin and hematocrit; causes behavior, growth, and
physiological changes in aquatic organisms; accumulates primarily in the kidneys;
immunosuppressive effects have been shown in mice, fish, and oysters. Soluble form is highly
available for plant uptake and can disturb enzyme activity.
ATSDR, 1990b; Eisler, 2000;
Rompala et al, 1994 as cited in
Irwin et al, 1997; Wren et al., 1995,
as cited in Irwin et al., 1997; Bodek
et al., 1988; and others in
TOXNET
Chromium Beneficial but not essential for plants; trivalent form essential form in mammals for maintaining
efficient lipid, glucose and protein metabolism; mutagenic, teratogenic and carcinogenic; hexavalent
form associated with inhibition of photosynthesis and interference with transport and mobilization of
essential nutrients. Hexavalent form can cause oxidation stress in cells, abnormal enzyme activity,
lowered resistance to pathogens, disrupted feeding, disrupted osmoregulation, histopathology, and
damage to beta cells of pancreatic islets. Can cause nephron and liver damage. Decreased weight
gain, increased oxygen consumption, impaired reproduction, and increased hematocrit have been
noted in aquatic organisms. High deposition of trivalent form in fish gills leads to tissue damage
including hyperplasia, clubbing of lamellae, and necrosis.
ATSDR, 1993b; Eisler, 2000;
Moore et al., 1990, as cited in Irwin
et al., 1997.
Copper Essential element for animals as a component of metalloenzymes and respiratory pigments, iron
utilization, function of enzymes in pigmentation, connective tissue formation and energy production;
forms stable inhibitory complexes with cytochrome P-450; impairs function of NADPH-cytochrome C
reductase; inhibits heme biosynthesis; teratogen and possible carcinogen; accumulates in the liver
and reduces liver's ability to excrete copper; decreases growth and food consumption in birds;
disrupts internal ion balance in aquatic organisms; alters hematology, respiratory physiology, and
cardiac physiology in fish; causes histological changes in the gills, kidneys, hematopoietic tissue,
mechanoreceptors, and chemoreceptors in fish. Reproductive effects in fish include blockage of
spawning, reduced egg production, abnormalities in young, and reduced survival of young.
ATSDR, 1990d; Rand and
Petrocelli, 1985, as cited in Irwin et
al., 1997; Sorenson, 1991, as cited
in Irwin et al., 1997.
Iron Essential for the production of proteins in plants and hemoglobin in animals. Toxicity related to
cellular oxidative stress, dysfunction and toxicity due to peroxide formation.
TOXNET
(http://toxnet.nlm.nih.gov/)
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/2 Page 1 of 3
Table 2
Mechanisms of Ecotoxicity
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Mechanisms of Ecotoxicity References
Lead Inhibits growth in plants. Reduces photosynthetic activity by blocking sulfhydril groups and inhibiting
the conversion of coproporphyrinogen to proporphyrinogen. Reduces mitosis and water absorption.
In animals, lead inhibits the formation of heme and reduces amino-levulinate acid dehydratase activity
in blood. Toxic effects in animals include reduced growth and reproductive output, accumulation in
hematopoietic organs, changes in the central nervous system (at high concentrations near those
causing mortality) kidney disfunction, enzyme inhibition, and behavioral changes. In birds, lead
decreases egg shell thickness and limits growth, ovulation, and sperm formation. In fish, lead can
increase mucous formation and cause death from suffocation.
ATSDR, 1993c; Eisler, 2000;
Finley and Stendell, 1978; Friberg
et al., 1986; Rompala et al., 1984,
as cited in Irwin et al., 1997.
Manganese Manganese is cytotoxic and causes chromosomal aberations in rodents. Reduction in testicular
growth (weight) and reduced seminal vesicle weight have been noted in rodents exposed to
manganese. Can cause dopamine depletion in nerve cells. Adverse behavioral and systemic effects
have been noted in birds exposed to manganese above nutrient levels.
ATSDR, 1992b
Mercury Mercury binds strongly with sulfhydryl groups and interferes with thiol metabolism, inhibiting or
inactivating proteins containing thiol ligands. This leads to mitotic disturbances and inhibition of cell
division. Organic mercury compounds are potent inhibitors of cell division. Methylmercury irreversibly
destroys central nervous system neurons in mammals and aquatic organisms and is the most toxic
form. Mercury compounds adversely affect metabolism, growth, development and behavior in birds
and mammals at relatively low exposure levels. The most sensitive target organ of inorganic mercury
appears to be the kidneys.
ATSDR, 1994; Eisler, 2000;
Leland and Kuwabara, 1985, as
cited in Irwin et al., 1997; Heinz,
1979.
Nickel Nickel is nephrotoxic, carcinogenic, and immunotoxic in mammals. Elevated levels of nickel cause
tremors, edema in joints and reduction in body weight and humerus length in birds; decreased
reproductive capacity has been noted. Retarded growth, anemia, and decreased enzyme activity have
been observed in rats.
ATSDR, 1995; Friberg et al., 1986.
Silver Silver has a strong affinity for sulfhydryl groups and proteins, resulting in cytotoxicity. Respiratory
depression in aquatic organisms has been noted; can cause cardiac enlargement, vascular
hypertension, hepatic necrosis, anemia, lowered immunological activity, kidney pathology, enzyme
inhibition, growth retardation, and shortened life span in mammals and birds.
ATSDR, 1990e; Eisler, 2000.
Thallium Exposure to elevated levels of thallium causes neuromorphological changes and systemic effects in
mammals (hair loss, increases in skeletal abnormalities and weight loss). No information was located
for birds.
ATSDR, 1992c
Zinc Zinc is essential for normal reproduction and growth in plants and animals. In animals, it is regulated
by metallothioneins, which temporarily store zinc, reducing its toxicity. Zinc-dependent enzymes
regulate the rates of biosynthesis and catabolism of RNA and DNA. At high exposures, zinc interferes
with the metabolism of calcium and iron and induces copper deficiency. Zinc causes cytoplasmic
vacuolation, cellular atrophy and cell death in the pancreas. It accumulates preferentially in bone and
induces osteomalacia (softening of the bone) as a result of a deficiency of minerals, including calcium
and phosphorous. In fish, zinc causes destruction of gill epithelium and tissue hypoxia. In rainbow
trout, disruption of internal ion balance has been noted.
Eisler, 2000; Rand and Petrocelli,
1985, as cited in Irwin et al., 1997.
Polycyclic
Aromatic
Hydrocarbons
(PAHs)
Toxicity is highly variable and related to the number of ring structures and molecular weight. Low
molecular weight compounds of 2 or three rings (e. g., naphthalene) cause acute toxicity, but are not
carcinogenic. Higher molecular weight PAHs with > 4 rings (e. g., benzo(a)pyrene) are mutagenic,
teratogenic and carcinogenic to a wider variety of animals. PAHs are toxic to a variety of animal
tissues. Causes narcosis toxicity in aquatic animals.
Eisler, 2000.
Phthalates Little information is known about the ecotoxicological effects that might be caused by this type of
chemical. Adverse effects in animals were generally seen only at high doses or with long term
exposures. Mildly harmful effects have been seen in the livers and kidneys of some rats and mice
given very high doses (e.g., di (2-ethylhexyl)phthalate, di-n-octylphthalate). Longer exposures to high
doses might affect the ability of both males and females to reproduce and caused birth defects.
ATSDR, 1997b
2,4-DNT 2,4-DNT is a noncarcinogenic though it is found to bind covalently with the liver, lung and intestines.
Inhalation of the fumes and dust, ingestion, or absorption through the skin may cause a chemical
change of the blood oxyhemoglobin to methemoglobin (via oxidation of iron [II] to iron [III].
TOXNET
(http://toxnet.nlm.nih.gov/)
HMX HMX may be harmful to the liver and central nervous system though the mechanisms by which HMX
causes adverse effects is not understood.
ATSDR, 1997a (Public Health
Statement)
Nitroguanidine Data is not available on the carcinogenic effects of nitroguanidine. Reproductive studies on spargue
dawley rats indicated no effects related to chemicals doses ranging from 100 to 1000 mg/kg/day.
Nitroguanidine was found to cause chromosomal aborations when incubated in vitro with Chinese
hamster cells. An experimental hygeinetic toxicological study suggested maximum tolerable level in
water, based on toxicology endpoints should be 0.1 mg/L.
TOXNET
(http://toxnet.nlm.nih.gov/)
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/2 Page 2 of 3
Table 2
Mechanisms of Ecotoxicity
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Mechanisms of Ecotoxicity References
Picric acid Picric acid may be a permanent uncoupler, with delta psi transmembrane electrical potential
difference. The uncoupling activity of picric acid in everted membrane systems is probably due to its
protonophoric action. In crayfish picric acid caused a specific inhibition fo voltage dependent K
conductance. Weakly ionized phenols caused motor excitation and discoordination in intact crayfish.
TOXNET
(http://toxnet.nlm.nih.gov/)
TPH TPHs have a range of toxicities and mechanisms. Smaller compounds such as benzene, toluene, and
xylene can affect the central nervous system. Other compounds affect blood, immune system, liver,
spleen, kidneys, developing fetus' , and lungs. Benzene has also been found to be carcinogenic.
ATSDR, 1999 (Public Health
Statement)
Nitrate Acute toxicity of nitrate occurs as a result of the reduction to nitrite, a process that can occur in the
stomach. Nitrite acts in blood to oxidize hemoglobin to methemoglobin, which does not perform as
oxygen carriers to tissues. Annoxia and death may occur. Additionally in water, nitrate may be
converted to N-nitroso CMPD, a direct carcinogenic agent.
TOXNET
(http://toxnet.nlm.nih.gov/)
Phosphorus Phosphine toxicity results from inhalation of yellow phosphorus. Phosphorus may affect hepatocyte
mitochondria, as well as cause liver cirrhosis.
TOXNET
(http://toxnet.nlm.nih.gov/)
Acetone As is typical of solvents, acetone is irritating to the mucous membranes. Acetone is also narcotic, and
although the mechanism by which acetone exerts is effects on the central nervous system is
unknown, as a solvent, it may interfere with the composition of membranes, altering their permeability
to ions. The mechanisms by which acetone produces hematological, hepatic, renal, reproductive, and
developmental effects is unknown, but acetone has been found to distribute to all of these target
organs, including the brain, and can undergo transplacental transfer. One of the main effects of
acetone is the induction of microsomal enzymes. Enzyme induction is probably responsible for the
increased liver and kidney weights observed in animals.
ASTDR, 1997c
Toluene LD50 for male mice was 1.15 g/kg. Known to have an additive effect with benzene. Evidence
suggests lack of carcinogenicity in experimental animals. Alterations in specific neuron populations
and their afferent and efferent terminal fields may complement changes in neurophysiology and
behavior that have been observed in prenatally and perinatally exposed rodent pups. In utero
exposure in rats can cause maternal malnutrition increasing the risk for fetotoxicity.
TOXNET
(http://toxnet.nlm.nih.gov/)
Styrene There is limited evidence in experimental animals for the carcinogenicity of styrene. Styrene has
moderate toxicity to aquatic life. Styrene by itself is not likely to cause environmental harm at levels
normally found in the environment. Styrene can contribute to smog formation when it reacts with other
volatile substances in air. Animal studies have not reported developmental or reproductive effects
from inhalation exposure to styrene.
USEPA, 1994
Perchlorate The known mode of action for perchlorate is that it acts as a competitive inhibitor of active iodide
uptake by the symporter in most mammals, including human and laboratory test species. This
decrease in intrathyroidal iodide results in a decreased production of T3 and T4 thyroid hormones.
This decrease can potentially perturb the hypothalamic-pituitary-thyroid axis to increase TSH from the
pituitary to stimulate production of thyroid hormone. Prolonged stimulation may result in thyroid
neoplasia, particularly in rodents known to be sensitive. Tumors have occurred in rats dosed with high
levels of perchlorate for long periods.
TOXNET
(http://toxnet.nlm.nih.gov/)
Xylene(s) After inhalation exposure the retention in the lungs is about 60% of the inhaled dose. Xylene is
efficiently metabolized. More than 90% is biotransformed to methylhippuric acid, which is excreted in
urine. Xylene does not accumulate significantly in the human body. Acute exposure to high
concentrations of xylene can result in CNS effects and irritation in humans. The chronic toxicity
appears to be relatively low in laboratory animals. There is suggestive evidence, however, that chronic
CNS effects may occur in animals at moderate concentrations of xylene. Xylene does not appear to be
a mutagen or carcinogen. The critical end point is developmental toxicity. The xylene isomers are of
moderate to low toxicity for aquatic organisms. The acute toxicity of xylene to birds is low. There is
inadequate evidence in humans and experimental animals for the carcinogenicity of xylenes.
TOXNET
(http://toxnet.nlm.nih.gov/)
2-Butanone There is very limited info on the mechanisms of toxic action of 2-butanone. Relatively high inhalation
exposure caused pulmonary vasoconstriction and hypertension in cats and dogs. From the
toxicological point of view, interactions leading to the potentiation of effects, particularly neurotoxicity,
by other intrinsically toxic substances constitute the main hazard of 2-butanone. The mechanisms
underlying these interactions are incompletely known.
TOXNET
(http://toxnet.nlm.nih.gov/)
Benzene Benzene is a carcinogenic chemical. Exposure through ingestion of food or water cause blood and
immune system damage and may cause cancer. Death in animals due to inhalation exposure has
been linked to ventricular fibrillation due to an increased release of adrenaline.
ASTDR, 1997d
Notes:
Information on the fate and transport of chemicals was researched through TOXNET (http://toxnet.nlm.nih.gov/) in the Hazardous Substances Data Bank.
Additional citations for the primary references listed can be found on the HSDB summary for each chemical listed.
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/2 Page 3 of 3
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5
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8
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0
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7
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4
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5
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4
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1
3
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1
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6
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8
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M
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6
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6
7
.
0

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7
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8
%

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.
9
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6
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7
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7
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7
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7
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7
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m
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4
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4
8

1
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1
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6
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2
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7
2
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9

6
4
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M
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2
2
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2
2
4
.
0

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4
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7

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2
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7
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5
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7
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4
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2
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3
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2
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3
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M
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7
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8
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7
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8
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7
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4
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4
2

1
0
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%
15
4
0
0

1
5
6
0
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1
8
8
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1
8
8
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2
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6
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M
a
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n
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7
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M
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m
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4
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6
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1
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5
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M
a
x

D
e
t

1
6

G
A
M
M
A

1
6
.
0
0
0
0

U
C
L
Co
b
a
l
t

7
4
4
0
4
8
4

i
n
o
r
g
a
n
i
c

m
g
/
k
g

2
2

2
8

7
9
%

4
.
2
0

4
.
9
0

1
.
0
0

4
.
9
0

2
.
9
0

2
.
7
8

1
.
1
2

4
.
9
0

M
a
x

D
e
t

3
.
1
3

N
O
R
M
A
L

3
.
1
3

U
C
L
Co
p
p
e
r

7
4
4
0
5
0
8

i
n
o
r
g
a
n
i
c

m
g
/
k
g

4
1

4
8

8
5
%

1
.
0
0

9
4
.
7

6
.
0
0

1
8
0
0
0

4
9
8

4
2
9

2
5
9
0

1
8
0
0
0

M
a
x

D
e
t

4
1
5
0

N
O
N
-
P
A
R
A
M
E
T
R
I
C

4
1
5
0
.
0

U
C
L
Ir
o
n

7
4
3
9
8
9
6

i
n
o
r
g
a
n
i
c

m
g
/
k
g

4
2

4
2

1
0
0
%

4
5
1
0

1
5
0
0
0

1
0
6
0
0

1
0
6
0
0

2
7
9
0

1
5
0
0
0

M
a
x

D
e
t

1
1
4
0
0

G
A
M
M
A

1
1
4
0
0
.
0

U
C
L
Le
a
d

7
4
3
9
9
2
1

i
n
o
r
g
a
n
i
c

m
g
/
k
g

4
0

4
8

8
3
%

2
.
0
0

8
1
1

2
.
8
0

4
8
0
0
0

1
2
7
0

1
0
7
0

6
9
2
0

4
8
0
0
0

M
a
x

D
e
t

1
1
0
0
0

N
O
N
-
P
A
R
A
M
E
T
R
I
C

1
1
0
0
0
.
0

U
C
L
Ma
g
n
e
s
i
u
m

7
4
3
9
9
5
4

i
n
o
r
g
a
n
i
c

m
g
/
k
g

4
2

4
2

1
0
0
%

9
7
0
0

2
4
3
0
0

1
6
7
0
0

1
6
7
0
0

4
0
0
0

2
4
3
0
0

M
a
x

D
e
t

1
7
8
0
0

G
A
M
M
A

1
7
8
0
0
.
0

U
C
L
Ma
n
g
a
n
e
s
e

7
4
3
9
9
6
5

i
n
o
r
g
a
n
i
c

m
g
/
k
g

4
8

4
8

1
0
0
%

1
2
0

5
1
9

3
1
8

3
1
8

1
1
6

5
1
9

M
a
x

D
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t

3
5
0

G
A
M
M
A

3
5
0
.
0
0
0
0

U
C
L
Me
r
c
u
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y

7
4
3
9
9
7
6

i
n
o
r
g
a
n
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c

m
g
/
k
g

1
3

4
8

2
7
%

0
.
0
1
0
0

0
.
1
1
0

0
.
0
0
5
0
0

0
.
0
7
0
0

0
.
0
1
7
2

0
.
0
2
2
3

0
.
0
1
5
3

0
.
0
7
0
0

M
a
x

D
e
t

0
.
0
3
1
9

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
3
1
9

U
C
L
Mo
l
y
b
d
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n
u
m

7
4
3
9
9
8
7

i
n
o
r
g
a
n
i
c

m
g
/
k
g

2
0

2
2

9
1
%

0
.
3
0
0

0
.
3
0
0

0
.
6
0
0

1
7

1
.
8
9

1
.
7
3

3
.
4
5

1
7

M
a
x

D
e
t

4
.
9
3

N
O
N
-
P
A
R
A
M
E
T
R
I
C

4
.
9
3

U
C
L
Ni
c
k
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l

7
4
4
0
0
2
0

i
n
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r
g
a
n
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c

m
g
/
k
g

4
8

4
8

1
0
0
%

6
.
7
0

4
1
.
3

1
1
.
3

1
1
.
3

5
.
8
3

4
1
.
3

M
a
x

D
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t

1
2
.
7

N
O
N
-
P
A
R
A
M
E
T
R
I
C

1
2
.
7
0
0
0

U
C
L
Ni
t
r
a
t
e

1
4
7
9
7
5
5
8

i
n
o
r
g
a
n
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c

m
g
/
k
g

4
4

4
8

9
2
%

1
.
7
0

2
.
5
0

0
.
0
0
4
0
0

2
2
.
8

4
.
5
7

4
.
2
8

5
.
9
2

2
2
.
8

M
a
x

D
e
t

1
2
.
8

N
O
N
-
P
A
R
A
M
E
T
R
I
C

1
2
.
8
0
0
0

U
C
L
Pe
r
c
h
l
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r
a
t
e

7
6
0
1
9
0
3

i
n
o
r
g
a
n
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c

m
g
/
k
g

1
1

2
2

5
0
%

0
.
0
1
0
6

0
.
1
1
2

0
.
0
1
5
6

4
.
5
0

0
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8
3
3

0
.
4
2
2

1
.
0
9

4
.
5
0

M
a
x

D
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t

2
.
7
3

N
O
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A
R
A
M
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C

2
.
7
3

U
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L
Ph
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s
p
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7
7
2
3
1
4
0

i
n
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g
a
n
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c

m
g
/
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g

2
0

2
0

1
0
0
%

4
5
0

9
9
0

6
5
6

6
5
6

1
7
1

9
9
0

M
a
x

D
e
t

7
2
2

N
O
R
M
A
L

7
2
2
.
0
0
0
0

U
C
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Po
t
a
s
s
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m

7
4
4
0
0
9
7

i
n
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g
a
n
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c

m
g
/
k
g

4
2

4
2

1
0
0
%

1
3
0
0

4
9
0
0
0
0

1
5
8
0
0

1
5
8
0
0

7
5
0
0
0

4
9
0
0
0
0

M
a
x

D
e
t

-
-

-
-

-
-

n
o
t

a

C
O
P
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C
Se
l
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n
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7
7
8
2
4
9
2

i
n
o
r
g
a
n
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m
g
/
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g

0

4
8

0
%

0
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1
8
0

1
0

2
.
4
8

2
.
1
7

5
.
0
0

0
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5
*
M
a
x
N
D

-
-

-
-

5
.
0
0

0
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5
*
M
a
x
N
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l
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r

7
4
4
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2
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i
n
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g
a
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m
g
/
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4

4
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8
%

0
.
1
7
1

2
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0
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0
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1
7
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4
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0
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1
4

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6
0
8

0
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6
4
3

4
.
0
0

M
a
x

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1
.
0
1

N
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A
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1
.
0
1

U
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d
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m

7
4
4
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2
3
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i
n
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m
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4
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4
2

1
0
0
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2
7
4

2
0
2
0

9
1
7

9
1
7

4
6
2

2
0
2
0

M
a
x

D
e
t

-
-

-
-

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-

n
o
t

a

C
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C
St
r
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m

7
4
4
0
2
4
6

i
n
o
r
g
a
n
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c

m
g
/
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g

2
2

2
2

1
0
0
%

2
4
4

4
8
4

3
5
1

3
5
1

7
1
.
9

4
8
4

M
a
x

D
e
t

3
7
7

N
O
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L

3
7
7
.
0

U
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l
f
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t
e

1
4
8
0
8
7
9
8

i
n
o
r
g
a
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m
g
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g

2
3

4
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5
5
%

0
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5
0
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0
.
5
0
0

9
.
2
0

3
0
6
0

2
9
7

1
6
3

5
3
8

3
0
6
0

M
a
x

D
e
t

-
-

-
-

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-

n
o
t

a

C
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C
Th
a
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7
4
4
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8
0

i
n
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m
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2
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4
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5
4
%

0
.
1
7
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5
.
0
0

0
.
1
1
0

0
.
5
5
0

0
.
2
7
9

1
.
2
0

1
.
1
2

0
.
5
5
0

M
a
x

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t

2
.
8
0

N
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A
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A
M
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C

0
.
5
5
0

M
a
x

D
e
t
Va
n
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d
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m

7
4
4
0
6
2
2

i
n
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g
a
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m
g
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g

2
8

2
8

1
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0
%

9
.
9
0

2
5
.
7

1
6
.
7

1
6
.
7

3
.
4
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2
5
.
7

M
a
x

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t

1
7
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8

N
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L

1
7
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8
0
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0

U
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n
c

7
4
4
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6
6
6

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a
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m
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4
8

4
8

1
0
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2
9
.
7

2
3
0
0

1
2
5

1
2
5

3
3
6

2
3
0
0

M
a
x

D
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3
3
7

N
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A
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C

3
3
7
.
0

U
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M
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m
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4

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0
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0
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1
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9

4
3
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7

1
7
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M
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9
7

N
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9
7
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0

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8
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m
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0
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0
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0
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M
a
x
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0
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m
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7
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7
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7
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5
6
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m
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5

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1
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0

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0
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M
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s
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1
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s
(
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Br
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h
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7
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0
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0
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8
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M
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n
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0
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6
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0
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U
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7
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1

2
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0
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9
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0
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0
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0
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7

N
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0
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0
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1
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0
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0
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N
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C

0
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7
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1

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t

0
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4
8

N
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0
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0
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f
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6
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6
6
3

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1

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0
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6
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0
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0
0
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0
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0
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.
0
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.
0
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M
a
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0
.
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7

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0
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0
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5
7

U
C
L
Ch
l
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o
m
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t
h
a
n
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7
4
8
7
3

V
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m
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/
k
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1

2
2

5
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0
.
0
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0
.
0
0
2
0
0

0
.
0
0
1
0
0

0
.
0
0
1
0
0

0
.
0
0
1
0
0

0
.
0
0
0
5
6
7

0
.
0
0
0
1
8
4

0
.
0
0
1
0
0

M
a
x

D
e
t

0
.
0
0
0
7
3
8

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
0
0
7
3
8
UC
L
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

1
5
6
5
9
2

V
O
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m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
6
0
0

0
.
0
0
1
3
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
4
6
1

0
.
0
0
0
1
2
7

0
.
0
0
0
7
0
0

M
a
x

D
e
t

0
.
0
0
0
4
9
7

N
O
R
M
A
L

0
.
00
0
4
9
7

U
C
L
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e

1
0
0
6
1
0
1
5

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
5
0
0

0
.
0
0
1
1
0

0
.
0
0
0
6
0
0

0
.
0
0
0
6
0
0

0
.
0
0
0
6
0
0

0
.
0
0
0
4
2
3

0
.
0
0
0
1
1
5

0
.
0
0
0
6
0
0

M
a
x

D
e
t

0
.
0
0
0
5
3
5

N
O
N
-
P
AR
A
M
E
T
R
I
C

0
.
0
0
0
5
3
5

U
C
L
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e

1
2
4
4
8
1

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
5
6
0

0
.
0
0
1
6
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
4
3
0

0
.
0
0
0
1
4
9

0
.
0
0
0
7
0
0

M
a
x

D
e
t

0
.
0
0
0
5
6
7

N
O
N
-
P
A
R
A
M
E
TR
I
C

0
.
0
0
0
5
6
7

U
C
L
Di
b
r
o
m
o
m
e
t
h
a
n
e

7
4
9
5
3

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
5
0
0

0
.
0
0
1
5
0

0
.
0
0
0
5
0
0

0
.
0
0
0
5
0
0

0
.
0
0
0
5
0
0

0
.
0
0
0
4
0
2

0
.
0
0
0
1
3
9

0
.
0
0
0
5
0
0

M
a
x

D
e
t

0
.
0
0
0
4
4
2

N
O
R
M
A
L

0
.
0
0
0
4
4
2

U
C
L
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e

7
5
7
1
8

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
6
1
0

0
.
0
0
1
5
0

0
.
0
0
1
1
0

0
.
0
0
1
1
0

0
.
0
0
1
1
0

0
.
0
0
0
5
1
5

0
.
0
0
0
1
6
1

0
.
0
0
1
1
0

M
a
x

D
e
t

0
.
0
0
0
6
6
5

N
O
N
-
P
A
R
A
M
E
T
R
IC

0
.
0
0
0
6
6
5

U
C
L
Et
h
y
l
b
e
n
z
e
n
e

1
0
0
4
1
4

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
7
0
0

0
.
0
0
1
2
0

0
.
0
0
1
3
0

0
.
0
0
1
3
0

0
.
0
0
1
3
0

0
.
0
0
0
4
8
9

0
.
0
0
0
2
0
0

0
.
0
0
1
3
0

M
a
x

D
e
t

0
.
0
0
0
5
6
3

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
0
0
5
6
3
UC
L
m,
p
-
X
y
l
e
n
e

1
3
3
0
2
0
7

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
9
0
0

0
.
0
0
2
5
0

0
.
0
0
2
0
0

0
.
0
0
2
0
0

0
.
0
0
2
0
0

0
.
0
0
0
8
8
2

0
.
0
0
0
3
7
4

0
.
0
0
2
0
0

M
a
x

D
e
t

0
.
0
0
0
9
6
5

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
0
0
9
6
5

U
CL
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e

7
5
0
9
2

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
6
8
0

0
.
0
0
3
2
0

0
.
0
0
3
2
0

0
.
0
0
3
2
0

0
.
0
0
3
2
0

0
.
0
0
0
8
7
8

0
.
0
0
0
6
3
2

0
.
0
0
3
2
0

M
a
x

D
e
t

0
.
0
0
1
4
6

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
0
14
6

U
C
L
o-
X
y
l
e
n
e

9
5
4
7
6

V
O
C

m
g
/
k
g

3

2
2

1
4
%

0
.
0
0
0
4
0
0

0
.
0
0
1
2
0

0
.
0
0
0
8
0
0

0
.
0
0
2
7
0

0
.
0
0
1
9
1

0
.
0
0
0
5
9
1

0
.
0
0
0
6
3
0

0
.
0
0
2
7
0

M
a
x

D
e
t

0
.
0
0
1
1
8

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
0
1
1
8

U
C
L
Ph
e
n
o
l

1
0
8
9
5
2

V
O
C

m
g
/
k
g

0

2
8

0
%

0
.
0
7
1
2

2
1

1
.
2
9

3
.
2
6

1
0
.
5

0
.
5
*
M
a
x
N
D

-
-

-
-

1
0
.
5

0
.
5
*
M
a
x
N
D
St
y
r
e
n
e

1
0
0
4
2
5

V
O
C

m
g
/
k
g

3

2
2

1
4
%

0
.
0
0
0
5
0
0

0
.
0
0
2
7
0

0
.
0
0
0
6
0
0

0
.
0
0
2
6
0

0
.
0
0
1
6
0

0
.
0
0
0
6
2
2

0
.
0
0
0
5
6
3

0
.
0
0
2
6
0

M
a
x

D
e
t

0
.
0
0
1
1
5

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
0
1
1
5

U
C
L
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r

1
6
3
4
0
4
4

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
6
0
0

0
.
0
0
1
7
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
4
7
3

0
.
0
0
0
1
5
8

0
.
0
0
0
7
0
0

M
a
x

D
e
t

-
-

-
-

-
-

n
o
t

a

C
O
P
E
C
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e

1
2
7
1
8
4

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
7
9
0

0
.
0
0
1
3
0

0
.
0
0
0
9
0
0

0
.
0
0
0
9
0
0

0
.
0
0
0
9
0
0

0
.
0
0
0
5
3
1

0
.
0
0
0
1
2
3

0
.
0
0
0
9
0
0

M
a
x

D
e
t

0
.
0
0
0
6
5
6

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
0
0
6
5
6

U
C
L
To
l
u
e
n
e

1
0
8
8
8
3

V
O
C

m
g
/
k
g

5

2
2

2
3
%

0
.
0
0
0
6
0
0

0
.
0
0
1
1
0

0
.
0
0
1
8
0

0
.
0
1
8
7

0
.
0
1
1
1

0
.
0
0
2
8
4

0
.
0
0
5
3
6

0
.
0
1
8
7

M
a
x

D
e
t

0
.
0
1
4
2

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
1
4
2

U
C
L
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

1
5
6
6
0
5

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
6
0
0

0
.
0
0
1
2
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
4
4
8

0
.
0
0
0
1
0
2

0
.
0
0
0
7
0
0

M
a
x

D
e
t

0
.
0
0
0
5
5
2

N
O
N
-
P
A
RA
M
E
T
R
I
C

0
.
0
0
0
5
5
2

U
C
L
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e

1
0
0
6
1
0
2
6

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
6
0
0

0
.
0
0
1
4
0

0
.
0
0
0
8
0
0

0
.
0
0
0
8
0
0

0
.
0
0
0
8
0
0

0
.
0
0
0
4
8
3

0
.
0
0
0
1
2
5

0
.
0
0
0
8
0
0

M
a
x

D
e
t

0
.
0
0
0
5
1
9

N
O
R
MA
L

0
.
0
0
0
5
1
9

U
C
L
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)

7
9
0
1
6

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
6
0
0

0
.
0
0
1
1
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
7
0
0

0
.
0
0
0
4
1
0

0
.
0
0
0
0
9
9
2

0
.
0
0
0
7
0
0

M
a
x

D
e
t

0
.
0
0
0
5
0
9

N
O
N
-
P
A
R
AM
E
T
R
I
C

0
.
0
0
0
5
0
9

U
C
L
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e

7
5
6
9
4

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
5
1
0

0
.
0
0
1
6
0

0
.
0
0
1
1
0

0
.
0
0
1
1
0

0
.
0
0
1
1
0

0
.
0
0
0
5
0
3

0
.
0
0
0
1
8
3

0
.
0
0
1
1
0

M
a
x

D
e
t

-
-

-
-

-
-

n
o
t

a

C
O
P
E
C
Vi
n
y
l

A
c
e
t
a
t
e

1
0
8
0
5
4

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
1
0
0

0
.
0
0
1
8
0

0
.
0
0
1
2
0

0
.
0
0
1
2
0

0
.
0
0
1
2
0

0
.
0
0
0
7
0
7

0
.
0
0
0
1
6
9

0
.
0
0
1
2
0

M
a
x

D
e
t

-
-

-
-

-
-

n
o
t

a

C
O
P
E
C
Vi
n
y
l

c
h
l
o
r
i
d
e

7
5
0
1
4

V
O
C

m
g
/
k
g

1

2
2

5
%

0
.
0
0
0
6
1
0

0
.
0
0
1
7
0

0
.
0
0
1
2
0

0
.
0
0
1
2
0

0
.
0
0
1
2
0

0
.
0
0
0
5
6
7

0
.
0
0
0
1
8
4

0
.
0
0
1
2
0

M
a
x

D
e
t

0
.
0
0
0
7
3
8

N
O
N
-
P
A
R
A
M
E
T
R
I
C

0
.
0
0
0
7
3
8

U
C
L
pH

p
H

O
t
h
e
r

-

2
0

2
0

1
0
0
%

7
.
4

8
.
9

7
.
9
8

7
.
9
8

0
.
3
7
6
4
0
9
6

7
.
9
8

A
v
e
r
a
g
e

-
-

-
-

-
-

n
o
t

a

C
O
P
E
C
No
t
e
s
:
De
t

=

n
u
m
b
e
r

o
f

s
a
m
p
l
e
s

w
h
e
r
e

t
h
e

a
n
a
l
y
t
e

c
o
n
c
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Table 4
Linkage Between Assessment and Measurement Endpoints
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Assessment Endpoint Measurement Endpoints Linkage Null Hypotheses
1. Protection of the terrestrial plant
community from direct toxic effects on
survival, reproduction and growth due to
chemicals in soil
Comparison of concentrations of
chemicals in on-site surface soil to
literature-based survival, growth and
reproduction effects concentrations for
terrestrial plants (Table 10)
Direct exposure Maximum Detected soil concentrations of
chemicals do not exceed relevant NOEC
or LOEC benchmarks
2. Protection of the soil invertebrate
community from direct toxic effects on
survival, reproduction and growth due to
chemicals in soil
Comparison of concentrations of
chemicals in on-site surface soil to
literature-based survival, growth and
reproduction concentrations for terrestrial
invertebrates (Table 11)
Direct exposure Maximum Detected soil concentrations of
chemicals do not exceed relevant NOEC
or LOEC benchmarks
3. Protection of populations of
herbivorous small mammals from toxic
effects on survival, reproduction and
growth due to chemicals in soil and
plants
Comparison of exposure doses (based
on the EPC) to published values for
survival, growth and reproduction no
observed adverse effect levels (NOAELs)
or lowest observed adverse effect levels
(LOAELs) (Table 12)
Direct exposure, ingestion Exposure doses, based on UCL95
concentrations within the TTU, do not
exceed survival, growth, reproduction, or
other relevant NOAELs or LOAELs
4. Protection of populations of
insectivorous small mammals from toxic
effects on survival, reproduction and
growth due to chemicals in soil and
terrestrial invertebrates
Comparison of exposure doses (based
on the EPC) to published values for
survival, growth and reproduction no
observed adverse effect levels (NOAELs)
or lowest observed adverse effect levels
(LOAELs) (Table 12)
Direct exposure, ingestion Exposure doses, based on UCL95
concentrations within the TTU, do not
exceed survival, growth, reproduction, or
other relevant NOAELs or LOAELs
5. Protection of populations of
carnivorous mammals from toxic effects
on survival, reproduction, and growth due
to chemicals in soil and prey
Comparison of exposure doses (based
on the EPC) to published values for
survival, growth and reproduction no
observed adverse effect levels (NOAELs)
or lowest observed adverse effect levels
(LOAELs) (Table 12)
Direct exposure, ingestion Exposure doses, based on UCL95
concentrations within the TTU, do not
exceed survival, growth, reproduction, or
other relevant NOAELs or LOAELs
6. Protection of populations of
herbivorous birds from toxic effects on
survival, reproduction and growth due to
chemicals in soil and plants
Comparison of exposure doses (based
on the EPC) to published values for
survival, growth and reproduction no
observed adverse effect levels (NOAELs)
or lowest observed adverse effect levels
(LOAELs) (Table 13)
Direct exposure, ingestion Exposure doses, based on UCL95
concentrations within the TTU, do not
exceed survival, growth, reproduction, or
other relevant NOAELs or LOAELs
7. Protection of populations of
insectivorous birds from toxic effects on
survival, reproduction, and growth due to
chemicals in soil and invertebrates
Comparison of exposure doses (based
on 95th UCL soil concentrations) to
published values for survival, growth and
reproduction no observed adverse effect
levels (NOAELs) or lowest observed
adverse effect levels (LOAELs) (Table
13)
Direct exposure, ingestion Exposure doses, based on UCL95
concentrations within the TTU, do not
exceed survival, growth, reproduction, or
other relevant NOAELs or LOAELs
8. Protection of populations of
carnivorous birds from toxic effects on
survival, reproduction, and growth due to
chemicals in soil and invertebrates
Comparison of exposure doses (based
on the EPC) to published values for
survival, growth and reproduction no
observed adverse effect levels (NOAELs)
or lowest observed adverse effect levels
(LOAELs) (Table 13)
Direct exposure, ingestion Exposure doses, based on UCL95
concentrations within the TTU, do not
exceed survival, growth, reproduction, or
other relevant NOAELs or LOAELs
Notes:
The EPC (Exposure Point Concentration) was calculated as the maximum detected concentration (or maximum non-detected concentration) in the initial risk characterization. The lesser of the
UCL 95 or maximum soil concentration was the EPC in the refined risk characterization.
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/4 Page 1 of 1
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Table 9
Regression Equations for Chemical Biotransfer Factors
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Receptor B0 B1 Source
Small Mammal/Bird BTF
Arsenic General -4.847 0.8188 Sample et. al (1998a)
Cadmium General -0.4036 0.4865 Sample et. al (1998a)
Cobalt General -4.4669 1.307 Sample et. al (1998a)
Copper General 2.042 0.1444 Sample et. al (1998a)
Iron General -0.2879 0.5969 Sample et. al (1998a)
Lead General 0.0761 0.4422 Sample et. al (1998a)
Selenium General -0.4158 0.3764 Sample et. al (1998a)
Zinc General 4.4713 0.0738 Sample et. al (1998a)
Terrestrial Invertebrate BTF
Arsenic Earthworm -1.421 0.706 Sample et. al (1998b)
Cadmium Earthworm 2.114 0.795 Sample et. al (1998b)
Copper Earthworm 1.675 0.264 Sample et. al (1998b)
Lead Earthworm -0.218 0.807 Sample et. al (1998b)
Manganese Earthworm -0.809 0.682 Sample et. al (1998b)
Mercury Earthworm -0.684 0.118 Sample et. al (1998b)
Selenium Earthworm -0.075 0.733 Sample et. al (1998b)
Zinc Earthworm 4.449 0.328 Sample et. al (1998b)
RDX Soil Invertebrate 4.376 0.230 Army Risk Assessment Modelling System (2005)
2-Amino-4,6-Dinitrotoluene Soil Invertebrate 1.593 0.766 Army Risk Assessment Modelling System (2005)
Plant BTF
Arsenic General -1.992 0.564 Bechtel Jacobs (1998)
Cadmium General -0.476 0.546 Bechtel Jacobs (1998)
Copper General 0.669 0.394 Bechtel Jacobs (1998)
Lead General -1.328 0.561 Bechtel Jacobs (1998)
Mercury General -0.996 0.544 Bechtel Jacobs (1998)
Nickel General -2.224 0.748 Bechtel Jacobs (1998)
Selenium General -0.678 1.104 Bechtel Jacobs (1998)
Zinc General 1.575 0.555 Bechtel Jacobs (1998)
2-Amino-4,6-Dinitrotoluene General 0.8777 0.3026 Army Risk Assessment Modelling System (2005)
Acenaphthene General 5.562 0.8556 USEPA 2005
Acenaphthylene General 1.144 0.791 USEPA 2005
Anthracene General 0.9887 0.7784 USEPA 2005
Benzo(a)anthracene General 0.7078 0.5944 USEPA 2005
Benzo(a)pyrene General 0.0615 0.975 USEPA 2005
Benzo(g,h,i)perylene General 0.9313 1.1829 USEPA 2005
Benzo(k)fluoranthene General 0.1579 0.8595 USEPA 2005
Chrysene General 0.7078 0.5944 USEPA 2005
Fluorene General 5.562 0.8556 USEPA 2005
HMX General 2.769 0.5296 Army Risk Assessment Modelling System (2005)
RDX General 3.453 0.4305 Army Risk Assessment Modelling System (2005)
Phenanthrene General 0.1665 0.6203 USEPA 2005
Notes:
All values are reported as dry weight.
mg/kg = Milligrams per kilogram.
95UCL = 95% upper confidence limit
Equations:
1 ln (Prey Conc) = B1*(ln[Site Specific Soil Concentration]) + B0
where:
BTF = Biotransfer Factor.
B0 = Slope.
B1 = Intercept.
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/9 Page 1 of 1
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5
Ar
s
e
n
i
c

N
A

U
S
E
P
A

2
0
0
5

(
E
c
o

S
S
L
)

1

1
8

N
A

N
S
V
Ba
r
i
u
m

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

5
0

1

5
0
0
Be
r
y
l
l
i
u
m

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

1

1

1
0
Ca
d
m
i
u
m

N
A

U
S
E
P
A

2
0
0
5

(
E
c
o

S
S
L
)

1

3
2

N
A

N
S
V
Ca
l
c
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ch
l
o
r
i
d
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ch
r
o
m
i
u
m

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

0
.
1

1

1
Co
b
a
l
t

N
A

U
S
E
P
A

2
0
0
5

(
E
c
o

S
S
L
)

1

1
3

1

2
0
LO
E
C

f
r
o
m

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a
Co
p
p
e
r

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

1
0

1

1
0
0
Ir
o
n

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Le
a
d

N
A

U
S
E
P
A

2
0
0
5

(
E
c
o

S
S
L
)

1

1
1
0

N
A

2
0
7
Ma
g
n
e
s
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ma
n
g
a
n
e
s
e

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

5
0

1

5
0
0
Me
r
c
u
r
y

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

0
.
0
3

1

0
.
3
Mo
l
y
b
d
e
n
u
m

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

0
.
2

1

2
Ni
c
k
e
l

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

3

1

3
0
Ni
t
r
a
t
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Pe
r
c
h
l
o
r
a
t
e

N
A

E
P
A

2
0
0
2

0
.
5

2
0

1

4
0
Ph
o
s
p
h
o
r
u
s

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Po
t
a
s
s
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Se
l
e
n
i
u
m

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

0
.
1

1

1
Si
l
v
e
r

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

0
.
2

1

2
So
d
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
St
r
o
n
t
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Su
l
f
a
t
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Th
a
l
l
i
u
m

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

0
.
1

1

1
Va
n
a
d
i
u
m

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

0
.
2

1

2
Zi
n
c

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

5

1

5
0
2,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

T
N
T

G
o
n
g

e
t

a
l
.

1
9
9
9

0
.
1

5

1

5
0
2-
B
u
t
a
n
o
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

n
a
p
h
t
h
a
l
e
n
e

C
C
M
E

1
9
9
9

0
.
1

0
.
3

1

3
se
e
d

e
m
e
r
g
e
n
c
e

L
C
2
5
s
Ac
e
n
a
p
h
t
h
e
n
e

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

2

1

2
0
Ac
e
t
o
n
e
NA

N
A

N
S
V

N
A

N
S
V
An
t
h
r
a
c
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Be
n
z
e
n
e

t
o
l
u
e
n
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

2
0

1

2
0
0
bi
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

D
i
e
t
h
y
l
p
h
t
h
a
l
a
t
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

1
0

1

1
0
0
Di
b
e
n
z
o
f
u
r
a
n

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Fl
u
o
r
a
n
t
h
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Fl
u
o
r
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
HM
X

N
A

R
o
b
i
d
o
u
x

e
t

a
l
.

2
0
0
3

1

4
5
0
0

N
A

N
S
V
Na
p
h
t
h
a
l
e
n
e

N
A

C
C
M
E

1
9
9
9

0
.
1

0
.
3

1

3
se
e
d

e
m
e
r
g
e
n
c
e

L
C
2
5
s
Ni
t
r
o
g
u
a
n
i
d
i
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
No
t
e
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
il
l
A
F
B
_
T
T
U
_0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
0
Pa
g
e

1

o
f

4
Ta
b
l
e

1
0
Ec
o
l
o
g
i
c
a
l

S
c
r
e
e
n
i
n
g

B
e
n
c
h
m
a
r
k
s

f
o
r

T
e
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s

E
x
p
o
s
e
d

t
o

S
o
i
l
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
Un
c
e
r
t
a
i
n
t
y

F
a
c
t
o
r

(
f
o
r

no
r
m
a
l
i

e
d

N
O
E
C
)
a
No
r
m
a
l
i

e
d

NO
E
C

(
m
g
/
k
g
)
b
Un
c
e
r
t
a
i
n
t
y

F
a
c
t
o
r

(
f
o
r

no
r
m
a
l
i

e
d

L
O
E
C
)
c
No
r
m
a
l
i

e
d

L
O
E
C

(m
g
/
k
g
)
d
No
t
e
s
o-
X
y
l
e
n
e

x
y
l
e
n
e
s

C
C
M
E

1
9
9
9

0
.
1

0
.
5

1

5
se
e
d

L
C
2
5
s
Ph
e
n
a
n
t
h
r
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Pi
c
r
i
c

a
c
i
d

N
A

N
A

N
A

N
S
V

N
A

N
S
V
St
y
r
e
n
e

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

3
0

1

3
0
0
To
l
u
e
n
e

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

2
0

1

2
0
0
TP
H

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

2
0
0
4

1

8
0
0
0

1

1
0
0
0
0
lo
w
e
s
t

N
O
E
C
/
N
O
E
C

f
o
r

d
i
e
s
e
l

r
a
n
g
e

T
P
H
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e

T
N
T

G
o
n
g

e
t

a
l
.

1
9
9
9

0
.
1

5

1

5
0
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e

T
N
T

G
o
n
g

e
t

a
l
.

1
9
9
9

0
.
1

5

1

5
0
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

3
,
4
-
d
i
c
h
l
o
r
o
p
h
e
n
o
l

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

2

1

2
0
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

3
,
4
-
d
i
c
h
l
o
r
o
p
h
e
n
o
l

E
f
r
o
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1
9
9
7
a

0
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2
0
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4
,
6
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T
r
i
n
i
t
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t
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l
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e

(
T
N
T
)

N
A

G
o
n
g

e
t

a
l
.

1
9
9
9

0
.
1

5

1

5
0
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4
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D
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c
h
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e
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3
,
4
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d
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c
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E
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1
9
9
7
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2
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4
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D
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m
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t
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y
l
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e
n
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l

N
A

N
A

N
A

N
S
V

N
A

N
S
V
2,
4
-
D
i
n
i
t
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e
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E
f
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l
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1
9
9
7
a

0
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2
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6
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G
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t

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1
9
9
9

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5
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D
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N
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T
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m
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l
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1
9
9
9

1

8
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N
A

N
S
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C
h
l
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e
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h
y
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V
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n
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l
E
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h
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N
A

N
A

N
A

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N
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N
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2-
C
h
l
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n
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N
A

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N
S
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N
A

N
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C
h
l
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3
-
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E
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9
7
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0
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1

0
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7

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7
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H
e
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N
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N
A

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V

N
A

N
S
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M
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t
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N
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N
A

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A

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N
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N
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N
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t
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N
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N
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2
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E
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T
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G
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1
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9
9

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N
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N
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N
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G
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1
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9
9

0
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5
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6
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m
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N
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N
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S
1
1
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S
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B
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f
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T
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P
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T
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R
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A
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An
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S
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R
e
f
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e
Un
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y

F
a
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(
f
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r

no
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e
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E
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No
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m
a
l
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NO
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C

(
m
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Un
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y

F
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(
f
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no
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O
E
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c
No
r
m
a
l
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e
d

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O
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C

(m
g
/
k
g
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d
No
t
e
s
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
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r

N
A

N
A

N
A

N
S
V

N
A

N
S
V
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
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l

N
A

N
A

N
A

N
S
V

N
A

N
S
V
4-
C
h
l
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a
n
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l
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3
-
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h
l
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E
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1
9
9
7
a

0
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1

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1

2
0
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C
h
l
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p
h
e
n
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l
p
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n
y
l
e
t
h
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r

N
A

N
A

N
A

N
S
V

N
A

N
S
V
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
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e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
4-
M
e
t
h
y
l
p
h
e
n
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l

N
A

N
A

N
A

N
S
V

N
A

N
S
V
4-
N
i
t
r
o
a
n
i
l
i
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
4-
N
i
t
r
o
p
h
e
n
o
l

2
,
4
-
D
i
n
i
t
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o
p
h
e
n
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l

E
f
r
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y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

2

1

2
0
4-
N
i
t
r
o
t
o
l
u
e
n
e

T
N
T

G
o
n
g

e
t

a
l
.

1
9
9
9

0
.
1

5

1

5
0
Ac
e
n
a
p
h
t
h
y
l
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Be
n
z
o
(
a
)
p
y
r
e
n
e

N
A

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3

N
O
E
C

f
o
r

r
y
e
,

w
h
e
a
t

a
n
d

c
o
r
n

(
S
i
m
s

a
n
d

Ov
e
r
c
a
s
h

1
9
8
3
)
;

h
i
g
h

N
O
E
C

u
s
e
d

f
o
r

LO
E
C

(
M
o
n
t
i
z
a
a
n

e
t

a
l
.

1
9
8
9
)
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Be
n
z
o
i
c

a
c
i
d

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Be
n
z
y
l
a
l
c
o
h
o
l

N
A

N
A

N
A

N
S
V

N
A

N
S
V
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r

N
A

N
A

N
A

N
S
V

N
A

N
S
V
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Br
o
m
o
f
o
r
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Br
o
m
o
m
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e

D
i
e
t
h
y
l
p
h
t
h
a
l
a
t
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

1
0

1

1
0
0
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ch
l
o
r
o
b
e
n
z
e
n
e

N
A

H
u
l
z
e
b
o
z

e
t

a
l
.

1
9
9
3

0
.
0
1

2
.
4
8

0
.
1

2
4
.
8
ba
s
e
d

o
n

E
C
5
0

=

2
4
8

m
g
/
k
g
Ch
l
o
r
o
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ch
l
o
r
o
f
o
r
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ch
l
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ch
r
y
s
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

C
C
M
E

1
9
9
9

1

1
.
2

1

3
.
3
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Di
b
r
o
m
o
m
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

1
0

1

1
0
0
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e

D
i
e
t
h
y
l
p
h
t
h
a
l
a
t
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

1
0

1

1
0
0
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

2
0

1

2
0
0
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e

D
i
e
t
h
y
l
p
h
t
h
a
l
a
t
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
a

0
.
1

1
0

1

1
0
0
Et
h
y
l
b
e
n
z
e
n
e

N
A

C
C
M
E

1
9
9
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s
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ma
n
g
a
n
e
s
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Me
r
c
u
r
y

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

0
.
0
1

1

0
.
1
Mo
l
y
b
d
e
n
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ni
c
k
e
l

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2
0

1

2
0
0
Ni
t
r
a
t
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Pe
r
c
h
l
o
r
a
t
e

N
A

E
P
A

2
0
0
2

0
.
0
1

4
.
4
5

0
.
1

4
4
.
4
pH

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Ph
o
s
p
h
o
r
u
s

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Po
t
a
s
s
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Si
l
v
e
r

N
A

N
A

N
A

N
S
V

N
A

N
S
V
So
d
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
St
r
o
n
t
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Su
l
f
a
t
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Th
a
l
l
i
u
m

N
A

C
C
M
E

19
9
9

1

1
2

1

2
7

e
a
r
t
h
w
o
r
m

m
o
r
t
a
l
i
t
y
Va
n
a
d
i
u
m

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Zi
n
c

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2
0

1

2
0
0
2,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

T
N
T

R
o
b
i
d
o
u
x

e
t

a
l
.

2
0
0
2

1

3
2
.
8

1

5
8
.
8
2-
B
u
t
a
n
o
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

F
l
u
o
r
e
n
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

3

1

3
0
Ac
e
n
a
p
h
t
h
e
n
e

N
A

S
v
e
r
d
r
u
p

e
t

a
l
.

2
0
0
2

0
.
1

3
.
1

0
.
1

1
0
.
7

N
O
E
C
=
r
e
p
r
o
d

E
C
1
0
;

L
O
E
C
=
L
C
5
0

f
o
r

c
o
l
l
e
m
b
o
l
a
Ac
e
t
o
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
An
t
h
r
a
c
e
n
e

N
A

S
v
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r
d
r
u
p

e
t

a
l
.

2
0
0
2

0
.
1

0
.
5

0
.
1

6
.
7

N
O
E
C
=
r
e
p
r
o
d

E
C
1
0
;

L
O
E
C
=
L
C
5
0

f
o
r

c
o
l
l
e
m
b
o
l
a
Be
n
z
e
n
e

N
A

C
C
M
E

1
9
9
9

0
.
0
1

1
.
6
1

0
.
1

1
6
.
1
bi
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

D
i
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2
0

1

2
0
0
Di
b
e
n
z
o
f
u
r
a
n

N
A

S
v
e
r
d
r
u
p

e
t

a
l
.

2
0
0
1

0
.
1

1
.
4

0
.
1

2
.
3

L
O
E
C
=
r
e
p
r
o
d

E
C
5
0

f
o
r

c
o
l
l
e
m
b
o
l
a
Fl
u
o
r
a
n
t
h
e
n
e

N
A

S
v
e
r
d
r
u
p

e
t

a
l
.

2
0
0
1

0
.
1

4
.
7

0
.
1

5
.
1

L
O
E
C
=
r
e
p
r
o
d

E
C
5
0

f
o
r

c
o
l
l
e
m
b
o
l
a
Fl
u
o
r
e
n
e

N
A

S
v
e
r
d
r
u
p

e
t

a
l
.

2
0
0
2

0
.
1

0
.
7
7

0
.
1

3
.
9

N
O
E
C
=
r
e
p
r
o
d

E
C
1
0
;

L
O
E
C
=
L
C
5
0

f
o
r

c
o
l
l
e
m
b
o
l
a
HM
X

N
A

R
o
b
i
d
o
u
x

e
t

a
l
.

2
0
0
2

0
.
1

1
.
5
6

1

1
5
.
6
Na
p
h
t
h
a
l
e
n
e

N
A

S
v
e
r
d
r
u
p

e
t

a
l
.

2
0
0
2

0
.
1

2

0
.
1

1
6
.
7

N
O
E
C
=
r
e
p
r
o
d

E
C
1
0
;

L
O
E
C
=
L
C
5
0

f
o
r

c
o
l
l
e
m
b
o
l
a
Ni
t
r
o
g
u
a
n
i
d
i
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
o-
X
y
l
e
n
e

x
y
l
e
n
e
s

C
C
M
E

1
9
9
9

0
.
0
1

0
.
5
6

0
.
1

5
.
6

b
a
s
e
d

o
n

L
C
2
5
Ph
e
n
a
n
t
h
r
e
n
e

N
A

S
v
e
r
d
r
u
p

e
t

a
l
.

2
0
0
1

0
.
1

2
.
1

0
.
1

3

L
O
E
C
=
r
e
p
r
o
d

E
C
5
0

f
o
r

c
o
l
l
e
m
b
o
l
a
Pi
c
r
i
c

a
c
i
d

N
A

N
A

N
A

N
S
V

N
A

N
S
V
No
t
e
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_0
6
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c
t
0
5
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C
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u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
1
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g
e

1

o
f

4
Ta
b
l
e

1
1
Ec
o
l
o
g
i
c
a
l

S
c
r
e
e
n
i
n
g

B
e
n
c
h
m
a
r
k
s

f
o
r

I
n
v
e
r
t
e
b
r
a
t
e
s

E
x
p
o
s
e
d

t
o

S
o
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l
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
Un
c
e
r
t
a
i
n
t

F
a
c
t
o
r

(
f
o
r

no
r
m
a
l
i

e
d

N
O
E
C
)
a
No
r
m
a
l
i

e
d

NO
E
C

(
m
g
/
k
g
)
b
Un
c
e
r
t
a
i
n
t

F
a
c
t
o
r

(f
o
r

n
o
r
m
a
l
i

e
d

LO
E
C
)
c
No
r
m
a
l
i

e
d

LO
E
C

(
m
g
/
k
g
)
d
No
t
e
s
St
y
r
e
n
e

x
y
l
e
n
e
s

C
C
M
E

1
9
9
9

0
.
0
1

0
.
5
6

0
.
1

5
.
6

i
n
t
e
r
i
m

r
e
m
e
d
i
a
t
i
o
n

c
r
i
t
e
r
i
o
n

=

5
6

m
g
/
k
g
To
l
u
e
n
e

N
A

C
C
M
E

1
9
9
9

0
.
0
1

0
.
4
4

0
.
1

4
.
4

b
a
s
e
d

o
n

L
C
2
5
TP
H

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

2
0
0
4

1

7
0
0

1

2
4
0
0

l
o
w
e
s
t

N
O
E
C
/
L
O
E
C

f
o
r

N
o
.
2

f
u
e
l

o
i
l

r
a
n
g
e

T
P
H
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
Se
l
e
n
i
u
m

N
A

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

7

1

7
0
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2

1

2
0
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2

1

2
0
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2

1

2
0
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

E
f
r
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y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2

1

2
0
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

E
f
r
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y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2

1

2
0
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

1
,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

E
f
r
o
y
m
s
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n

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t

a
l
.

1
9
9
7
b

0
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1

2

1

2
0
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

E
f
r
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y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
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1

2

1

2
0
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

7
0

1

7
0
0
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
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N
A

E
f
r
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y
m
s
o
n

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t

a
l
.

1
9
9
7
b

0
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1

2

1

2
0
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

1
,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

2

1

2
0
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e

E
f
r
o
y
m
s
o
n

e
t

a
l
.

1
9
9
7
b

0
.
1

7
0

1

7
0
0
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e

N
A

E
f
r
o
y
m
s
o
n

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t

a
l
.

1
9
9
7
b

0
.
1

7
0

1

7
0
0
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e

N
A

N
A

N
A

N
S
V

N
A

N
S
V
1,
3
,
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N
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=
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p
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d

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C
1
0
;

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=
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C
5
0

f
o
r

c
o
l
l
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m
b
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a
Be
n
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o
(
a
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n
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N
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2
0
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N
A

N
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Be
n
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(
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N
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Be
n
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(
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l
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2
0
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1

3
6
0

N
A

N
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V
Be
n
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o
(
g
,
h
,
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)
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B
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(
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l
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S
v
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2
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3
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0

N
A

N
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Be
n
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(
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r
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N
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2
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1

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6
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N
A

N
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n
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a
c
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d

N
A

N
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N
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N
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n
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y
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a
l
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h
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l

N
A

N
A

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A

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N
A

N
S
V
bi
s
(
2
-
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)
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N
A

N
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N
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N
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N
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N
S
V
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s
(
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s
(
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N
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N
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Bu
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b
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N
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N
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Ch
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Ch
l
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Ch
l
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Ch
l
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Ch
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N
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N
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s
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.

1
9
6
6

1
.
9
3

1
9
.
3

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
An
t
i
m
o
n
y

N
A

U
S
E
P
A

2
0
0
3

(
E
c
o

S
S
L
)

0
.
0
5
9

0
.
6
4

L
O
A
E
L

f
r
o
m

P
o
o
n

e
t

a
l
.
,

1
9
9
8

i
n

E
c
o
S
S
L
Ar
s
e
n
i
c

N
A

N
e
m
e
c

e
t

a
l
.

1
9
9
8

0
.
3
9
6

1
.
5
8
Ba
r
i
u
m

N
A

N
T
P

1
9
9
4

4
5

7
5
Be
r
y
l
l
i
u
m

N
A

U
S
E
P
A

2
0
0
3

(
E
c
o

S
S
L
)

0
.
5
3
2

N
S
V
Ca
d
m
i
u
m

N
A

U
S
E
P
A

2
0
0
3

(
E
c
o

S
S
L
)

0
.
7
7

1
.
4
2

L
O
A
E
L

f
r
o
m

W
e
b
s
t
e
r

(
1
9
7
8
)

i
n

E
c
o
S
S
L
Ca
l
c
i
u
m

N
A

N
A

N
S
V

N
S
V
Ch
l
o
r
i
d
e

N
A

N
A

N
S
V

N
S
V
Ch
r
o
m
i
u
m

N
A

M
a
c
k
e
n
z
i
e

e
t

a
l
.

1
9
5
8
/
S
t
e
v
e
n

e
t

a
l
.

1
9
7
6

3
.
2
8

1
3
.
1
4

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Co
p
p
e
r

N
A

A
u
l
e
r
i
c
h

e
t

a
l
.

1
9
8
2

1
1
.
7

1
5
.
1
4

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Co
b
a
l
t

N
A

P
a
t
e
r
n
a
i
n

e
t

a
l
.

1
9
8
8

1
.
1
3
5

1
1
.
3
5
Ir
o
n

N
A

N
A

N
S
V

N
S
V
Le
a
d

N
A

K
i
m
m
e
l

e
t

a
l
.

1
9
8
0

0
.
9
2

4
.
7
Ma
n
g
a
n
e
s
e

N
A

L
a
s
k
e
y

e
t

a
l
.

1
9
8
2

8
8

2
8
4

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ma
g
n
e
s
i
u
m

N
A

N
A

N
S
V

N
S
V
Me
r
c
u
r
y

N
A

V
e
r
s
c
h
u
u
r
e
n

e
t

a
l
.

1
9
7
6

0
.
0
3
2

0
.
1
6

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ni
c
k
e
l

N
A

A
m
b
r
o
s
e

e
t

a
l
.

1
9
7
6

4
0

8
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Mo
l
y
b
d
e
n
u
m

N
A

S
c
h
r
o
e
d
e
r

a
n
d

M
i
t
c
h
e
n
e
r

1
9
7
1

0
.
2
6

2
.
6

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ni
t
r
a
t
e

N
A

S
l
e
i
g
h
t

a
n
d

A
t
a
l
l
a
h

1
9
6
8

5
0
7

1
1
3
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Pe
r
c
h
l
o
r
a
t
e

N
A

E
P
A

2
0
0
2

2
.
5
9

2
5
.
9
Ph
o
s
p
h
o
r
u
s

N
A

N
A

N
S
V

N
S
V
Po
t
a
s
s
i
u
m

N
A

N
A

N
S
V

N
S
V
Si
l
v
e
r

N
A

R
u
n
g
b
y

a
n
d

D
a
c
s
h
e
r

1
9
8
4

2
.
3
8

2
3
.
8
Su
l
f
a
t
e

N
A

N
A

N
S
V

N
S
V
Th
a
l
l
i
u
m

N
A

F
o
r
m
i
g
l
i

e
t

a
l
.

1
9
8
6

0
.
0
0
7
4

0
.
0
7
4

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
So
d
i
u
m

N
A

N
A

N
S
V

N
S
V
St
r
o
n
t
i
u
m

N
A

S
k
o
r
y
n
a

1
9
8
1

2
6
3

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Zi
n
c

N
A

S
c
h
l
i
c
k
e
r

a
n
d

C
o
x

1
9
6
8

1
6
0

3
2
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

2

8
Va
n
a
d
i
u
m

N
A

D
o
m
i
n
g
o

e
t

a
l
.

1
9
8
6

0
.
2
1

2
.
1

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2-
B
u
t
a
n
o
n
e

a
c
e
t
o
n
e

E
P
A

1
9
8
6
c

1
0

5
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

N
A

M
u
r
a
t
a

e
t

a
l
.

1
9
9
7

5
.
0
3

5
0
.
3
Ac
e
n
a
p
h
t
h
e
n
e

N
A

U
S
E
P
A

2
0
0
1

1
7
5

3
5
0
Ac
e
t
o
n
e

N
A

E
P
A

1
9
8
6
c

1
0

5
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
An
t
h
r
a
c
e
n
e

N
A

U
S
E
P
A

2
0
0
1

1
0
0
0

N
S
V
Be
n
z
e
n
e

N
A

W
o
l
f

e
t

a
l
.

1
9
5
6

0
.
7

7
bi
s
(
2
-
e
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

N
A

L
a
m
b

e
t

a
l
.

1
9
8
7

1
8
.
3

1
8
3

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Di
b
e
n
z
o
f
u
r
a
n

N
A

N
A

N
S
V

N
S
V
Fl
u
o
r
a
n
t
h
e
n
e

N
A

U
S
E
P
A

2
0
0
1

1
2
5

2
5
0
Fl
u
o
r
e
n
e

N
A

U
S
E
P
A

2
0
0
1

1
2
5

2
5
0
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
2
Pa
g
e

1

o
f

5
Ta
b
l
e

1
2
To
x
i
c
i
t
y

R
e
f
e
r
e
n
c
e

V
a
l
u
e
s

C
o
n
s
i
d
e
r
e
d

f
o
r

M
a
m
m
a
l
i
a
n

W
i
l
d
l
i
f
e

R
e
c
e
p
t
o
r
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
No
r
m
a
l
i
z
e
d
NO
A
E
L
TR
V
1
,
3
(m
g
/
k
g
b
w
-
d
)
No
r
m
a
l
i
z
e
d
LO
A
E
L
TR
V
1
,
3
(m
g
/
k
g
b
w
-
d
)
No
t
e
s
HM
X

N
A

H
o
l
d
s
w
o
r
t
h

e
t

a
l
.

2
0
0
1
a

1

5
Na
p
h
t
h
a
l
e
n
e

N
A

N
a
v
a
r
r
o

e
t

a
l
.

1
9
9
1

5
0

1
5
0
Ni
t
r
o
g
u
a
n
i
d
i
n
e

N
A

N
A

N
S
V

N
S
V
o-
X
y
l
e
n
e

x
y
l
e
n
e
s

U
S
E
P
A

2
0
0
1

1
7
9

3
5
7
Ph
e
n
a
n
t
h
r
e
n
e

A
c
e
n
a
p
h
t
h
e
n
e

U
S
E
P
A

2
0
0
1

1
7
5

3
5
0
Pi
c
r
i
c

a
c
i
d

N
A

N
A

N
S
V

N
S
V
St
y
r
e
n
e

N
A

N
A

N
S
V

N
S
V
To
l
u
e
n
e

N
A

G
o
s
p
e

e
t

a
l
.

1
9
9
4

5
2

5
2
0
TP
H

N
A

C
o
o
p
e
r

a
n
d

M
a
t
t
i
e

1
9
9
6

1
0
0
0

1
5
0
0
0
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e

N
A

N
A

N
S
V

N
S
V
Se
l
e
n
i
u
m

N
A

R
o
s
e
n
f
e
l
d

a
n
d

B
e
a
t
h

1
9
5
4

0
.
2

0
.
3
3

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

T
e
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e

B
u
b
e
n

a
n
d

O
'
F
l
a
h
e
r
t
y

1
9
8
5

1
.
4

7

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

N
A

L
a
n
e

e
t

a
l
.

1
9
8
2

1
0
0
0

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

T
e
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e

B
u
b
e
n

a
n
d

O
'
F
l
a
h
e
r
t
y

1
9
8
5

1
.
4

7

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

L
a
n
e

e
t

a
l
.

1
9
8
2

1
0
0
0

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

L
a
n
e

e
t

a
l
.

1
9
8
2

5
0

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

1
,
1
-
D
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

Q
u
a
s
t

e
t

a
l
.

1
9
8
3

2
.
5

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
S
V

N
S
V
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e

1
,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

L
a
n
e

e
t

a
l
.

1
9
8
2

1
0
0
0

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
S
V

N
S
V
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e

N
A

N
A

N
S
V

N
S
V
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
S
V

N
S
V
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

N
A

L
a
n
e

e
t

a
l
.

1
9
8
2

5
0

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

L
a
n
e

e
t

a
l
.

1
9
8
2

5
0

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e

N
A

N
A

N
S
V

N
S
V
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e

N
A

H
o
l
d
s
w
o
r
t
h

e
t

a
l
.

2
0
0
1
b

2
.
6
8

1
3
.
3
1
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
S
V

N
S
V
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e

N
A

H
o
l
d
s
w
o
r
t
h

e
t

a
l
.

2
0
0
1
c

0
.
0
4

0
.
2
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

N
A

N
S
V

N
S
V
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

p
e
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

S
c
h
w
e
t
z

e
t

a
l
.

1
9
7
8

0
.
2
4

2
.
4

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

p
e
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

S
c
h
w
e
t
z

e
t

a
l
.

1
9
7
8

0
.
2
4

2
.
4

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)

N
A

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

2

8
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l

p
e
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

S
c
h
w
e
t
z

e
t

a
l
.

1
9
7
8

0
.
2
4

2
.
4

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

2

8
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

N
A

H
o
l
d
s
w
o
r
t
h

e
t

a
l
.

2
0
0
1
d

9

4
8
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r

N
A

N
A

N
S
V

N
S
V
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e

N
A

N
A

N
S
V

N
S
V
2-
C
h
l
o
r
o
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
2
Pa
g
e

2

o
f

5
Ta
b
l
e

1
2
To
x
i
c
i
t
y

R
e
f
e
r
e
n
c
e

V
a
l
u
e
s

C
o
n
s
i
d
e
r
e
d

f
o
r

M
a
m
m
a
l
i
a
n

W
i
l
d
l
i
f
e

R
e
c
e
p
t
o
r
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
No
r
m
a
l
i
z
e
d
NO
A
E
L
TR
V
1
,
3
(m
g
/
k
g
b
w
-
d
)
No
r
m
a
l
i
z
e
d
LO
A
E
L
TR
V
1
,
3
(m
g
/
k
g
b
w
-
d
)
No
t
e
s
2-
H
e
x
a
n
o
n
e

a
c
e
t
o
n
e

E
P
A

1
9
8
6
c

1
0

5
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2-
M
e
t
h
y
l
p
h
e
n
o
l

N
A

H
o
r
n
s
h
a
w

e
t

a
l
.

1
9
8
6

3
4
0

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2-
N
i
t
r
o
a
n
i
l
i
n
e

N
A

N
A

N
S
V

N
S
V
2-
N
i
t
r
o
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
2-
N
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

2

8
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e

N
A

N
A

N
S
V

N
S
V
3-
N
i
t
r
o
a
n
i
l
i
n
e

N
A

N
A

N
S
V

N
S
V
3-
N
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

2

8
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r

N
A

N
A

N
S
V

N
S
V
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
4-
C
h
l
o
r
o
a
n
i
l
i
n
e

N
A

N
A

N
S
V

N
S
V
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r

N
A

N
A

N
S
V

N
S
V
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e

N
A

M
i
c
r
o
b
i
o
l
o
g
i
c
a
l

A
s
s
o
c
.

1
9
8
6

2
5

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
4-
M
e
t
h
y
l
p
h
e
n
o
l

2
-
M
e
t
h
y
l
p
h
e
n
o
l

H
o
r
n
s
h
a
w

e
t

a
l
.

1
9
8
6

3
4
0

N
S
V

u
p
d
a
t
e
d

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
4-
N
i
t
r
o
a
n
i
l
i
n
e

N
A

N
A

N
S
V

N
S
V
4-
N
i
t
r
o
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
4-
N
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

2

8
Ac
e
n
a
p
h
t
h
y
l
e
n
e

A
c
e
n
a
p
h
t
h
e
n
e

U
S
E
P
A

2
0
0
1

1
7
5

3
5
0
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

M
a
c
k
e
n
z
i
e

a
n
d

A
n
g
e
v
i
n
e

1
9
8
1

1

1
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Be
n
z
o
(
a
)
p
y
r
e
n
e

N
A

M
a
c
k
e
n
z
i
e

a
n
d

A
n
g
e
v
i
n
e

1
9
8
1

1

1
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

M
a
c
k
e
n
z
i
e

a
n
d

A
n
g
e
v
i
n
e

1
9
8
1

1

1
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

M
a
c
k
e
n
z
i
e

a
n
d

A
n
g
e
v
i
n
e

1
9
8
1

1

1
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

M
a
c
k
e
n
z
i
e

a
n
d

A
n
g
e
v
i
n
e

1
9
8
1

1

1
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Be
n
z
o
i
c

a
c
i
d

N
A

N
A

N
S
V

N
S
V
Be
n
z
y
l
a
l
c
o
h
o
l

N
A

N
A

N
S
V

N
S
V
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r

N
A

N
A

N
S
V

N
S
V
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r

N
A

N
A

N
S
V

N
S
V
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
Br
o
m
o
f
o
r
m

C
h
l
o
r
o
f
o
r
m

P
a
l
m
e
r

e
t

a
l
.

1
9
7
9

1
5

4
1

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Br
o
m
o
m
e
t
h
a
n
e

C
h
l
o
r
o
f
o
r
m

P
a
l
m
e
r

e
t

a
l
.

1
9
7
9

1
5

4
1

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e

D
i
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e

L
a
m
b

e
t

a
l
.

1
9
8
7

5
5
0

1
8
3
3

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e

N
A

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
a

1
6

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
2
Pa
g
e

3

o
f

5
Ta
b
l
e

1
2
To
x
i
c
i
t
y

R
e
f
e
r
e
n
c
e

V
a
l
u
e
s

C
o
n
s
i
d
e
r
e
d

f
o
r

M
a
m
m
a
l
i
a
n

W
i
l
d
l
i
f
e

R
e
c
e
p
t
o
r
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
No
r
m
a
l
i
z
e
d
NO
A
E
L
TR
V
1
,
3
(m
g
/
k
g
b
w
-
d
)
No
r
m
a
l
i
z
e
d
LO
A
E
L
TR
V
1
,
3
(m
g
/
k
g
b
w
-
d
)
No
t
e
s
Ch
l
o
r
o
b
e
n
z
e
n
e

C
h
l
o
r
o
f
o
r
m

P
a
l
m
e
r

e
t

a
l
.

1
9
7
9

1
5

4
1

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ch
l
o
r
o
e
t
h
a
n
e

C
h
l
o
r
o
f
o
r
m

P
a
l
m
e
r

e
t

a
l
.

1
9
7
9

1
5

4
1

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ch
l
o
r
o
f
o
r
m

N
A

P
a
l
m
e
r

e
t

a
l
.

1
9
7
9

1
5

4
1

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ch
l
o
r
o
m
e
t
h
a
n
e

C
h
l
o
r
o
f
o
r
m

P
a
l
m
e
r

e
t

a
l
.

1
9
7
9

1
5

4
1

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ch
r
y
s
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

M
a
c
k
e
n
z
i
e

a
n
d

A
n
g
e
v
i
n
e

1
9
8
1

1

1
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

N
A

B
a
r
n
e
s

e
t

a
l
.

1
9
8
5

4
5
.
2

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e

c
i
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

B
a
r
n
e
s

e
t

a
l
.

1
9
8
5

4
5
.
2

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

M
a
c
k
e
n
z
i
e

a
n
d

A
n
g
e
v
i
n
e

1
9
8
1

1

1
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
Di
b
r
o
m
o
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e

N
A

L
a
m
b

e
t

a
l
.

1
9
8
7

4
5
8
3

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e

D
i
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e

L
a
m
b

e
t

a
l
.

1
9
8
7

5
5
0

1
8
3
3

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e

N
A

L
a
m
b

e
t

a
l
.

1
9
8
7

5
5
0

1
8
3
3

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e

D
i
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e

L
a
m
b

e
t

a
l
.

1
9
8
7

5
5
0

1
8
3
3

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Et
h
y
l
b
e
n
z
e
n
e

N
A

W
o
l
f

e
t

a
l
.

1
9
5
6

9
7

2
9
1
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e

N
A

G
r
a
n
t

e
t

a
l
.

1
9
7
7

1
.
6

3
.
2

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e

H
e
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e

G
r
a
n
t

e
t

a
l
.

1
9
7
7

1
.
6

3
.
2

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e

H
e
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e

G
r
a
n
t

e
t

a
l
.

1
9
7
7

1
.
6

3
.
2

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e

H
e
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e

G
r
a
n
t

e
t

a
l
.

1
9
7
7

1
.
6

3
.
2

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e

B
e
n
z
o
(
a
)
p
y
r
e
n
e

M
a
c
k
e
n
z
i
e

a
n
d

A
n
g
e
v
i
n
e

1
9
8
1

1

1
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Is
o
p
h
o
r
o
n
e

N
A

N
A

N
S
V

N
S
V
m,
p
-
X
y
l
e
n
e

x
y
l
e
n
e
s

U
S
E
P
A

2
0
0
1

1
7
9

3
5
7
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e

N
A

N
C
A

1
9
8
2

5
.
8
5

5
0

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ni
t
r
o
b
e
n
z
e
n
e

N
A

N
A

N
S
V

N
S
V
Ni
t
r
o
g
l
y
c
e
r
i
n

N
A

M
i
d
g
e
l
y

e
t

a
l
.

2
0
0
1

3

3
2
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e

N
A

N
A

N
S
V

N
S
V
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e

N
A

N
A

N
S
V

N
S
V
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

N
A

S
c
h
w
e
t
z

e
t

a
l
.

1
9
7
8

0
.
2
4

2
.
4

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
PE
T
N

N
A

H
o
l
d
s
w
o
r
t
h

e
t

a
l
.

2
0
0
1
e

1
7
0

1
7
0
0
Ph
e
n
o
l

N
A

B
i
s
h
o
p

e
t

a
l
.

1
9
9
7

1
7
.
1

N
S
V
Py
r
e
n
e

N
A

U
S
E
P
A

2
0
0
1

7
5

1
2
5
RD
X

N
A

T
a
l
m
a
g
e

e
t

a
l
.

1
9
9
9

2

2
0
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)

N
A

B
u
b
e
n

a
n
d

O
'
F
l
a
h
e
r
t
y

1
9
8
5

0
.
7

7

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r

N
A

N
A

N
S
V

N
S
V
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e

N
A

B
u
b
e
n

a
n
d

O
'
F
l
a
h
e
r
t
y

1
9
8
5

1
.
4

7

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Te
t
r
y
l

N
A

T
a
l
m
a
g
e

e
t

a
l
.

1
9
9
9

1
.
3

6
.
2
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

c
i
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

B
a
r
n
e
s

e
t

a
l
.

1
9
8
5

4
5
.
2

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e

c
i
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

B
a
r
n
e
s

e
t

a
l
.

1
9
8
5

4
5
.
2

N
S
V

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
2
Pa
g
e

4

o
f

5
Ta
b
l
e

1
2
To
x
i
c
i
t
y

R
e
f
e
r
e
n
c
e

V
a
l
u
e
s

C
o
n
s
i
d
e
r
e
d

f
o
r

M
a
m
m
a
l
i
a
n

W
i
l
d
l
i
f
e

R
e
c
e
p
t
o
r
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
No
r
m
a
l
i
z
e
d
NO
A
E
L
TR
V
1
,
3
(m
g
/
k
g
b
w
-
d
)
No
r
m
a
l
i
z
e
d
LO
A
E
L
TR
V
1
,
3
(m
g
/
k
g
b
w
-
d
)
No
t
e
s
Vi
n
y
l

A
c
e
t
a
t
e

N
A

N
A

N
S
V

N
S
V
Vi
n
y
l

c
h
l
o
r
i
d
e

N
A

F
e
r
o
n

e
t

a
l
.

1
9
8
1

0
.
1
7

1
.
7

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
No
t
e
s
:
NA

-

n
o
t

a
p
p
l
i
c
a
b
l
e
NS
V

-

n
o

s
c
r
e
e
n
i
n
g

v
a
l
u
e

a
v
a
i
l
a
b
l
e
NO
A
E
L

=

n
o

o
b
s
e
r
v
e
d

a
d
v
e
r
s
e

e
f
f
e
c
t

l
e
v
e
l
LO
A
E
L

=

l
o
w
e
s
t

o
b
s
e
r
v
e
d

a
d
v
e
r
s
e

e
f
f
e
c
t

l
e
v
e
l
1)

S
e
l
e
c
t
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7

N
S
V

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Me
r
c
u
r
y

N
A

H
e
i
n
z

1
9
7
6
;

H
e
i
n
z

a
n
d

H
o
f
f
m
a
n

1
9
9
8

0
.
0
6
8

0
.
3
7

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Mo
l
y
b
d
e
n
u
m

N
A

L
e
p
o
r
e

a
n
d

M
i
l
l
e
r

1
9
6
5

3
.
5

3
5
.
3

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ni
c
k
e
l

N
A

C
a
i
n

a
n
d

P
a
f
f
o
r
d

1
9
8
1

1
7
.
6

7
7
.
4

u
p
d
a
t
e
d

f
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ni
t
r
a
t
e

N
A

N
A

N
S
V

N
S
V
Pe
r
c
h
l
o
r
a
t
e

N
H
4
(
C
l
O
4
)

M
c
N
a
b
b

e
t

a
l
.

2
0
0
4

3
.
2
6

3
2
.
6
Ph
o
s
p
h
o
r
u
s

N
A

S
p
a
r
l
i
n
g

e
t

a
l
.

1
9
9
7

0
.
0
3
7

0
.
2
6
Po
t
a
s
s
i
u
m

N
A

N
A

N
S
V

N
S
V
Si
l
v
e
r

N
A

N
A

N
S
V

N
S
V
So
d
i
u
m

N
A

N
A

N
S
V

N
S
V
St
r
o
n
t
i
u
m

N
A

N
A

N
S
V

N
S
V
Su
l
f
a
t
e

N
A

N
A

N
S
V

N
S
V
Th
a
l
l
i
u
m

N
A

B
e
a
n

a
n
d

H
u
d
s
o
n

1
9
7
6

0
.
6

1
.
2
Va
n
a
d
i
u
m

N
A

W
h
i
t
e

a
n
d

D
i
e
t
e
r

1
9
7
8

1
1
.
4

N
S
V

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Zi
n
c

N
A

S
t
a
h
l

e
t

a
l
.

1
9
9
0

1
4
.
5

1
3
1

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2,
4
-
D
I
N
I
T
R
O
T
O
L
U
E
N
E

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

0
.
0
7

1
.
8
2-
B
u
t
a
n
o
n
e

a
c
e
t
o
n
e

H
i
l
l

a
n
d

C
a
m
a
r
d
e
s
e

1
9
8
6

3
9
.
3

3
9
3
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

n
a
p
h
t
h
a
l
e
n
e

W
i
l
d
l
i
f
e

I
n
t
e
r
n
a
t
i
o
n
a
l

1
9
8
5

2
6
.
9

2
6
9
Ac
e
n
a
p
h
t
h
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Ac
e
t
o
n
e

N
A

H
i
l
l

a
n
d

C
a
m
a
r
d
e
s
e

1
9
8
6

3
9
.
3

N
S
V
An
t
h
r
a
c
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Be
n
z
e
n
e

x
y
l
e
n
e
s

H
i
l
l

a
n
d

C
a
m
a
r
d
e
s
e

1
9
8
6

1
0
.
2

1
0
1
.
7
bi
s
(
2
-
e
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

N
A

P
e
a
k
a
l
l

1
9
7
4

1
.
1

N
S
V

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Di
b
e
n
z
o
f
u
r
a
n

N
A

N
A

N
S
V

N
S
V
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
3
Pa
g
e

1

o
f

5
Ta
b
l
e

1
3
To
x
i
c
i
t
y

R
e
f
e
r
e
n
c
e

V
a
l
u
e
s

C
o
n
s
i
d
e
r
e
d

f
o
r

A
v
i
a
n

W
i
l
d
l
i
f
e

R
e
c
e
p
t
o
r
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
No
r
m
a
l
i

e
d
NO
A
E
L
TR
V
1,
3
(m
g
/
k
g
b
w
-
d
)
No
r
m
a
l
i

e
d
LO
A
E
L
TR
V
1,
3
(m
g
/
k
g
b
w
-
d
)
No
t
e
s
Fl
u
o
r
a
n
t
h
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Fl
u
o
r
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
HM
X

N
A

H
o
l
d
s
w
o
r
t
h

e
t

a
l
.

2
0
0
1
a

9

6
2
.
5
Na
p
h
t
h
a
l
e
n
e

N
A

W
i
l
d
l
i
f
e

I
n
t
e
r
n
a
t
i
o
n
a
l

1
9
8
5

2
6
.
9

2
6
9
Ni
t
r
o
g
u
a
n
i
d
i
n
e

N
A

N
A

N
S
V

N
S
V
o-
X
y
l
e
n
e

x
y
l
e
n
e
s

H
i
l
l

a
n
d

C
a
m
a
r
d
e
s
e

1
9
8
6

1
0
.
2

1
0
1
.
7
Ph
e
n
a
n
t
h
r
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Pi
c
r
i
c

a
c
i
d

N
A

N
A

N
S
V

N
S
V
St
y
r
e
n
e

N
A

N
A

N
S
V

N
S
V
To
l
u
e
n
e

x
y
l
e
n
e
s

H
i
l
l

a
n
d

C
a
m
a
r
d
e
s
e

1
9
8
6

1
0
.
2

1
0
1
.
7
TP
H

N
A

S
z
a
r
o

e
t

a
l
.

1
9
8
1

5
0
0

5
0
0
0

N
o
.

2

f
u
e
l

o
i
l
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e

N
A

N
A

N
S
V

N
S
V
Se
l
e
n
i
u
m

N
A

H
e
i
n
z

e
t

a
l
.

1
9
8
7

0
.
4

0
.
8

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e

N
A

N
A

N
S
V

N
S
V
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

N
A

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e

N
A

N
A

N
S
V

N
S
V
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

0
.
0
7

1
.
8
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e

N
A

S
c
h
a
f
e
r

1
9
7
2

0
.
4
2

N
S
V
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

p
e
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

N
e
b
e
k
e
r

e
t

a
l
.

1
9
9
4

1
6
.
9

3
8
.
4
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

p
e
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

N
e
b
e
k
e
r

e
t

a
l
.

1
9
9
4

1
6
.
9

3
8
.
4
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)

N
A

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

0
.
0
7

1
.
8
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l

p
e
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

N
e
b
e
k
e
r

e
t

a
l
.

1
9
9
4

1
6
.
9

3
8
.
4
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

0
.
0
7

1
.
8
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
3
Pa
g
e

2

o
f

5
Ta
b
l
e

1
3
To
x
i
c
i
t
y

R
e
f
e
r
e
n
c
e

V
a
l
u
e
s

C
o
n
s
i
d
e
r
e
d

f
o
r

A
v
i
a
n

W
i
l
d
l
i
f
e

R
e
c
e
p
t
o
r
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
No
r
m
a
l
i

e
d
NO
A
E
L
TR
V
1,
3
(m
g
/
k
g
b
w
-
d
)
No
r
m
a
l
i

e
d
LO
A
E
L
TR
V
1,
3
(m
g
/
k
g
b
w
-
d
)
No
t
e
s
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

0
.
0
7

1
.
8
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r

N
A

N
A

N
S
V

N
S
V
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e

N
A

N
A

N
S
V

N
S
V
2-
C
h
l
o
r
o
p
h
e
n
o
l

p
e
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

N
e
b
e
k
e
r

e
t

a
l
.

1
9
9
4

1
6
.
9

3
8
.
4

s
u
b
c
h
r
o
n
i
c

v
a
l
u
e
s

2-
H
e
x
a
n
o
n
e

a
c
e
t
o
n
e

H
i
l
l

a
n
d

C
a
m
a
r
d
e
s
e

1
9
8
6

3
9
.
3

3
9
3
2-
M
e
t
h
y
l
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
2-
N
i
t
r
o
a
n
i
l
i
n
e

N
A

N
A

N
S
V

N
S
V
2-
N
i
t
r
o
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
2-
N
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

0
.
0
7

1
.
8
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e

N
A

N
A

N
S
V

N
S
V
3-
N
i
t
r
o
a
n
i
l
i
n
e

N
A

N
A

N
S
V

N
S
V
3-
N
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

0
.
0
7

1
.
8
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r

N
A

N
A

N
S
V

N
S
V
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
4-
C
h
l
o
r
o
a
n
i
l
i
n
e

N
A

N
A

N
S
V

N
S
V
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r

N
A

N
A

N
S
V

N
S
V
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e

a
c
e
t
o
n
e

H
i
l
l

a
n
d

C
a
m
a
r
d
e
s
e

1
9
8
6

3
9
.
3

3
9
3
4-
M
e
t
h
y
l
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
4-
N
i
t
r
o
a
n
i
l
i
n
e

N
A

N
A

N
S
V

N
S
V
4-
N
i
t
r
o
p
h
e
n
o
l

N
A

N
A

N
S
V

N
S
V
4-
N
i
t
r
o
t
o
l
u
e
n
e

T
N
T

J
o
h
n
s
o
n

e
t

a
l
.

2
0
0
0

0
.
0
7

1
.
8
Ac
e
n
a
p
h
t
h
y
l
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Be
n
z
o
(
a
)
p
y
r
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Be
n
z
o
i
c

a
c
i
d
ar
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Be
n
z
y
l
a
l
c
o
h
o
l

N
A

N
A

N
S
V

N
S
V
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r

N
A

N
A

N
S
V

N
S
V
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r

N
A

N
A

N
S
V

N
S
V
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
Br
o
m
o
f
o
r
m

N
A

N
A

N
S
V

N
S
V
Br
o
m
o
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e

D
i
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e

P
e
a
k
a
l
l

1
9
7
4

0
.
1
1

1
1

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e

N
A

N
A

N
S
V

N
S
V
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
3
Pa
g
e

3

o
f

5
Ta
b
l
e

1
3
To
x
i
c
i
t
y

R
e
f
e
r
e
n
c
e

V
a
l
u
e
s

C
o
n
s
i
d
e
r
e
d

f
o
r

A
v
i
a
n

W
i
l
d
l
i
f
e

R
e
c
e
p
t
o
r
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e
No
r
m
a
l
i

e
d
NO
A
E
L
TR
V
1,
3
(m
g
/
k
g
b
w
-
d
)
No
r
m
a
l
i

e
d
LO
A
E
L
TR
V
1,
3
(m
g
/
k
g
b
w
-
d
)
No
t
e
s
Ch
l
o
r
o
b
e
n
z
e
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ch
l
o
r
o
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

A
l
u
m
o
t

e
t

a
l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
o
m

S
a
m
p
l
e

e
t

a
l
.

1
9
9
6
Ch
l
o
r
o
f
o
r
m

N
A

N
A

N
S
V

N
S
V
Ch
l
o
r
o
m
e
t
h
a
n
e

1
,
2
-
D
i
c
h
l
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A
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t

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l
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1
9
7
6
b

1
7
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2

3
4
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4

F
r
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m

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m
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t

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l
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1
9
9
6
Ch
r
y
s
e
n
e

N
A

N
A

N
S
V

N
S
V
ci
s
-
1
,
2
-
D
i
c
h
l
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r
o
e
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1
,
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-
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6
b

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7
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2

3
4
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4

F
r
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m

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9
6
ci
s
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1
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3
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c
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l
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e

1
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-
D
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c
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A
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9
7
6
b

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7
.
2

3
4
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4

F
r
o
m

S
a
m
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t

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l
.

1
9
9
6
Di
b
e
n
z
o
(
a
,
h
)
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n
t
h
r
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n
e
ar
o
m
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t
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c

h
y
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n
Pa
t
t
o
n

a
n
d

D
i
e
t
e
r

1
9
8
0

3
2
5
.
2

N
S
V
Di
b
r
o
m
o
c
h
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m
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t
h
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n
e

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,
2
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6
b

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7
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2

3
4
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4

F
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9
9
6
Di
b
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n
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,
2
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D
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c
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A
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6
b

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7
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2

3
4
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4

F
r
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m

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9
9
6
Di
c
h
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f
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1
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6
b

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7
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2

3
4
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4

F
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m

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6
Di
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D
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P
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F
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6
Di
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D
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Di
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A

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F
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6
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x
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9
9
6
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
ar
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m
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t
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c

h
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d
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d

D
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t
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r

1
9
8
0

3
2
5
.
2

N
S
V
Is
o
p
h
o
r
o
n
e

N
A

N
A

N
S
V

N
S
V
m,
p
-
X
y
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e

x
y
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s

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a
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7
Me
t
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c
h
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N
A

N
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N
S
V

N
S
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Ni
t
r
o
b
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0
7

1
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8
Ni
t
r
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g
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n

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A

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n-
N
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N
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p
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A

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N
S
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Pe
n
t
a
c
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6
.
9

3
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T
N

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Ph
e
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l

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A

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N
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Py
r
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n
e

N
A

N
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N
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RD
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Tr
i
c
h
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e

(
T
C
E
)

N
A

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N
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V

N
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te
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M
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E
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A

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N
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V

N
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Te
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a
c
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A
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9
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6
b

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7
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2

3
4
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4

F
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m

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t

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l
.

1
9
9
6
Te
t
r
y
l

N
A

N
A

N
S
V

N
S
V
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
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e
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e

1
,
2
-
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c
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A
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1
9
7
6
b

1
7
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2

3
4
.
4

F
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m

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m
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t

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l
.

1
9
9
6
SL
C

J
M
S

E
S
1
1
2
0
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5
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1
0
S
L
C
/
H
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l
l
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s
/
1
3
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4

o
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Ta
b
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e

1
3
To
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i
c
i
t
y

R
e
f
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n
c
e

V
a
l
u
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s

C
o
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s
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d

f
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r

A
v
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a
n

W
i
l
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l
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R
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p
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s
At
t
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t

1
0
A

-

T
h
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a
l

T
r
e
a
t
m
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n
t

U
n
i
t
,

E
c
o
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c
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l

R
i
s
k

A
s
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s
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m
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t
An
a
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e

S
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R
e
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e
No
r
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l
i

e
d
NO
A
E
L
TR
V
1,
3
(m
g
/
k
g
b
w
-
d
)
No
r
m
a
l
i

e
d
LO
A
E
L
TR
V
1,
3
(m
g
/
k
g
b
w
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d
)
No
t
e
s
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
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p
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e

1
,
2
-
D
i
c
h
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h
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n
e

A
l
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m
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t

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t

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l
.

1
9
7
6
b

1
7
.
2

3
4
.
4

F
r
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m

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m
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t

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l
.

1
9
9
6
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e

N
A

N
A

N
S
V

N
S
V
Vi
n
y
l

a
c
e
t
a
t
e

N
A

N
A

N
S
V

N
S
V
Vi
n
y
l

c
h
l
o
r
i
d
e

N
A

N
A

N
S
V

N
S
V
No
t
e
s
:
NA

-

n
o
t

a
p
p
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c
a
b
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e
NS
V

-

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o

s
c
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n
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v
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e

a
v
a
i
l
a
b
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e
NO
A
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L

=

n
o

o
b
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d

a
d
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f
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=

l
o
w
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o
b
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a
d
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e
f
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l
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l
1)

S
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l
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c
t
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o
f

T
R
V
s

a
n
d

a
p
p
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f

U
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F
a
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w
a
s

p
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n

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c
c
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a
n
c
e

w
i
t
h

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S
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P
A
,

(
1
9
9
7
)

a
s

d
e
s
c
r
i
b
e
d

i
n

f
o
o
tn
o
t
e
s

3

a
n
d

4
.
2)

>

d
e
n
o
t
e
s

s
e
l
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c
t
e
d

N
O
A
E
L

e
n
d
p
o
i
n
t

s
t
u
d
y
;

+

d
e
n
o
t
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s

s
e
l
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c
t
e
d

L
O
A
E
L

e
n
d
p
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i
n
t

s
t
u
d
y
;

>
+

d
e
n
o
t
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s

b
o
t
h

N
O
A
E
L

a
n
d

L
O
A
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L

w
e
r
e

s
e
l
e
c
te
d

f
r
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m

t
h
e

s
a
m
e

s
t
u
d
y
.
3)

T
h
e

f
o
l
l
o
w
i
n
g

p
r
e
f
e
r
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n
c
e
s

w
e
r
e

u
s
e
d

w
h
e
n

s
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l
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c
t
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n
g

s
t
u
d
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e
s
:

N
O
A
E
L

e
n
d
p
o
i
n
t
s

w
e
r
e

g
i
v
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n

p
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f
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n
c
e

o
v
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r

L
O
A
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L

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n
d
p
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n
t
s

w
h
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n

b
o
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h

w
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e

a
v
a
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l
a
b
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e
.

S
t
u
d
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s

w
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Table 14
Direct Toxicity Screening for Plants Exposed to Soil Using Maximum Detected Concentrations
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte
Soil NOEC Screening Value
(mg/kg) EPC
1 (mg/kg) DF NOEC HQ
2
Screening
Conclusion
1,3,5-Trinitrobenzene 5.00 0.105 0%0.021 Pass
1,3-Dinitrobenzene 5.00 0.08 0%0.016 Pass
2,4,6-Trinitrotoluene (TNT)5.00 1.5 0%0.30 Pass
2,4-Dinitrophenol 2.00 50 0%25 Retain
2,4-Dinitrotoluene 5.00 2 2%0.40 Pass
2,6-Dinitrotoluene 5.00 10.5 0%2.1 Retain
2-Amino-4,6-Dinitrotoluene 80.00 1.5 0%0.019 Pass
2-Nitroaniline NSV 50 0%NA Uncertain
2-Nitrophenol 2.00 10.5 0%5.2 Retain
2-Nitrotoluene 5.00 0.14 0%0.028 Pass
3-Nitroaniline NSV 50 0%NA Uncertain
3-Nitrotoluene 5.00 0.15 0%0.030 Pass
4,6-Dinitro-2-methylphenol NSV 50 0%NA Uncertain
4-Nitroaniline NSV 50 0%NA Uncertain
4-Nitrophenol 2.00 50 0%25 Retain
4-Nitrotoluene 5.00 0.19 0%0.038 Pass
HMX 4500 25 31%0.0056 Pass
Nitrobenzene 5.00 10.5 0%2.1 Retain
Nitroglycerin NSV 0.34 0%NA Uncertain
Nitroguanidine NSV 0.3 5%NA Uncertain
PETN NSV 0.5 0%NA Uncertain
Picric acid NSV 0.5 7%NA Uncertain
RDX 50.00 1.5 0%0.030 Pass
Tetryl 2.50 0.23 0%0.092 Pass
HI - Energetics 0.41 Pass
Aluminum 5.00 54000 100%11000 Retain
Antimony 0.50 166.93 79%330.00 Retain
Arsenic 18.00 41.3 58%2.3 Retain
Barium 50.00 640 100%13.00 Retain
Beryllium 1.00 0.72 48%0.72 Pass
Cadmium 32.00 32 44%1.0 Retain
Carbon disulfide NSV 0.0011 5%NA Uncertain
Chromium 0.10 55.3 100%550 Retain
Cobalt 13.00 4.9 79%0.38 Pass
Copper 10.00 18000 85%1800 Retain
Iron NSV 15000 100%NA Uncertain
Lead 110.00 48000 83%440 Retain
Magnesium NSV 24300 100%NA Uncertain
Manganese 50.00 519 100%10.00 Retain
Mercury 0.03 0.07 27%2.3 Retain
Molybdenum 0.20 17 91%85 Retain
Nickel 3.00 41.3 100%14 Retain
Nitrate NSV 22.8 92%NA Uncertain
Perchlorate 20.00 4.5 50%0.22 Pass
Phosphorus NSV 990 100%NA Uncertain
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/14 Page 1 of 4
Table 14
Direct Toxicity Screening for Plants Exposed to Soil Using Maximum Detected Concentrations
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte
Soil NOEC Screening Value
(mg/kg) EPC
1 (mg/kg) DF NOEC HQ
2
Screening
Conclusion
Selenium 0.10 5 0%50 Retain
Silver 0.20 4 8%20 Retain
Strontium NSV 484 100%NA Uncertain
Thallium 0.10 0.55 54%5.5 Retain
Vanadium 0.20 25.7 100%130 Retain
Zinc 5.00 2300 100%460 Retain
HI - Inorganics 15000 Retain
2-Methylnaphthalene 0.30 170 14%570 Retain
Acenaphthene 2.00 0.04185 0%0.021 Pass
Acenaphthylene 1.20 10.5 0%8.8 Retain
Anthracene 1.20 3.7 7%3.1 Retain
Benzo(a)anthracene 1.20 10.5 0%8.8 Retain
Benzo(a)pyrene 1.20 10.5 0%8.8 Retain
Benzo(b)fluoranthene 1.20 10.5 0%8.8 Retain
Benzo(g,h,i)perylene 1.20 10.5 0%8.8 Retain
Benzo(k)fluoranthene 1.20 10.5 0%8.8 Retain
Chrysene 1.20 10.5 0%8.8 Retain
Dibenzo(a,h)anthracene 1.20 10.5 0%8.8 Retain
Fluoranthene 1.20 0.144 4%0.12 Pass
Fluorene 1.20 33 14%28 Retain
Indeno(1,2,3-c,d)pyrene 1.20 10.5 0%8.8 Retain
Naphthalene 0.30 53 25%180 Retain
Phenanthrene 1.20 92 18%77 Retain
Pyrene 1.20 10.5 0%8.8 Retain
HI - PAHs 850 Retain
TPH 8000.00 47000 100%5.9 Retain
HI - Petroleum 5.9 Retain
2,4,5-Trichlorophenol 2.00 50 0%25 Retain
2,4,6-Trichlorophenol 2.00 10.5 0%5.2 Retain
2,4-Dichlorophenol 2.00 10.5 0%5.2 Retain
2,4-Dimethylphenol NSV 10.5 0%NA Uncertain
2-Chloronaphthalene NSV 10.5 0%NA Uncertain
2-Methylphenol NSV 10.5 0%NA Uncertain
3,3-Dichlorobenzidine NSV 21 0%NA Uncertain
4-Chloro-3-methylphenol NSV 10.5 0%NA Uncertain
4-Chloroaniline 2.00 10.5 0%5.2 Retain
4-Methylphenol NSV 10.5 0%NA Uncertain
Benzoic acid NSV 50 0%NA Uncertain
Benzylalcohol NSV 10.5 0%NA Uncertain
bis(2-Ethylhexyl)phthalate 10.00 1.5 18%0.15 Pass
Butyl benzylphthalate 10.00 10.5 0%1.0 Retain
Dibenzofuran NSV 12 14%NA Uncertain
Diethylphthalate 10.00 10.5 0%1.0 Retain
Dimethylphthalate 10.00 10.5 0%1.0 Retain
Di-n-butylphthalate 20.00 10.5 0%0.52 Pass
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/14 Page 2 of 4
Table 14
Direct Toxicity Screening for Plants Exposed to Soil Using Maximum Detected Concentrations
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte
Soil NOEC Screening Value
(mg/kg) EPC
1 (mg/kg) DF NOEC HQ
2
Screening
Conclusion
Di-n-octylphthalate 10.00 10.5 0%1.0 Retain
Hexachlorobenzene 1.00 10.5 0%11.00 Retain
Hexachlorobutadiene 1.00 0.0008 4%0.00080 Pass
Hexachlorocyclopentadiene 1.00 10.5 0%11.00 Retain
Hexachloroethane NSV 10.5 0%NA Uncertain
Isophorone NSV 10.5 0%NA Uncertain
n-Nitroso-di-n-propylamine NSV 10.5 0%NA Uncertain
n-Nitrosodiphenylamine NSV 10.5 0%NA Uncertain
Pentachlorophenol 5.00 50 0%10.00 Retain
HI - SVOCs 0.15 Pass
1,1,1,2-Tetrachloroethane NSV 0.0006 5%NA Uncertain
1,1,1-Trichloroethane NSV 0.0009 5%NA Uncertain
1,1,2,2-Tetrachloroethane NSV 0.001 5%NA Uncertain
1,1,2-Trichloroethane NSV 0.0008 5%NA Uncertain
1,1-Dichloroethane NSV 0.0007 5%NA Uncertain
1,1-Dichloroethene NSV 0.0011 5%NA Uncertain
1,2,3-Trichlorobenzene NSV 0.0028 5%NA Uncertain
1,2,3-Trichloropropane NSV 0.0009 5%NA Uncertain
1,2,4-Trichlorobenzene NSV 0.0032 4%NA Uncertain
1,2-Dibromo-3-chloropropane NSV 0.0039 5%NA Uncertain
1,2-Dichlorobenzene NSV 0.0014 4%NA Uncertain
1,2-Dichloroethane NSV 0.0008 5%NA Uncertain
1,2-Dichloropropane NSV 0.0007 5%NA Uncertain
1,2-Ethylene Dibromide NSV 0.0009 5%NA Uncertain
1,3-Dichlorobenzene NSV 0.0019 4%NA Uncertain
1,4-Dichlorobenzene NSV 0.0031 4%NA Uncertain
2-Butanone NSV 0.0159 18%NA Uncertain
2-ChloroethylVinylEther NSV 0.00595 0%NA Uncertain
2-Chlorophenol 0.70 10.5 0%15.00 Retain
2-Hexanone NSV 0.0038 5%NA Uncertain
4-Bromophenylphenylether NSV 10.5 0%NA Uncertain
4-Chlorophenylphenylether NSV 10.5 0%NA Uncertain
4-Methyl-2-pentanone NSV 0.0043 5%NA Uncertain
Acetone NSV 24 32%NA Uncertain
Benzene 20.00 0.0041 14%0.00020 Pass
Bis(2-chloroethoxy)methane NSV 0.074 0%NA Uncertain
Bis(2-chloroethyl)ether NSV 10.5 0%NA Uncertain
Bis(2-chloroisopropyl)ether NSV 10.5 0%NA Uncertain
Bromodichloromethane NSV 0.0007 5%NA Uncertain
Bromoform NSV 0.0005 5%NA Uncertain
Bromomethane NSV 0.0015 5%NA Uncertain
Carbon tetrachloride NSV 0.0009 5%NA Uncertain
Chlorobenzene 2.48 0.0007 5%0.00028 Pass
Chloroethane NSV 0.001 5%NA Uncertain
Chloroform NSV 0.0007 5%NA Uncertain
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/14 Page 3 of 4
Table 14
Direct Toxicity Screening for Plants Exposed to Soil Using Maximum Detected Concentrations
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte
Soil NOEC Screening Value
(mg/kg) EPC
1 (mg/kg) DF NOEC HQ
2
Screening
Conclusion
Chloromethane NSV 0.001 5%NA Uncertain
cis-1,2-Dichloroethene NSV 0.0007 5%NA Uncertain
cis-1,3-Dichloropropene NSV 0.0006 5%NA Uncertain
Dibromochloromethane NSV 0.0007 5%NA Uncertain
Dibromomethane NSV 0.0005 5%NA Uncertain
Dichlorodifluoromethane NSV 0.0011 5%NA Uncertain
Ethylbenzene 0.60 0.0013 5%0.0022 Pass
m,p-Xylene 0.50 0.002 5%0.0040 Pass
Methylene chloride NSV 0.0032 5%NA Uncertain
o-Xylene 0.50 0.0027 14%0.0054 Pass
Phenol 7.00 10.5 0%1.5 Retain
Styrene 30.00 0.0026 14%0.000087 Pass
tert-ButylMethylEther NSV 0.0007 5%NA Uncertain
Tetrachloroethene 10.00 0.0009 5%0.000090 Pass
Toluene 20.00 0.0187 23%0.00093 Pass
Trans-1,2-Dichloroethene NSV 0.0007 5%NA Uncertain
Trans-1,3-Dichloropropene NSV 0.0008 5%NA Uncertain
Trichloroethylene (TCE)NSV 0.0007 5%NA Uncertain
Trichlorofluoromethane NSV 0.0011 5%NA Uncertain
Vinyl Acetate NSV 0.0012 5%NA Uncertain
Vinyl chloride NSV 0.0012 5%NA Uncertain
HI - VOCs 0.013 Pass
Notes:
1 EPC = Exposure Point Concentration. Maximum detected concentration or 1/2 detection limit for non-detected analytes
2 Hazard Indices (HI) calculated as the sum of HQs for detected analytes
Retain = screening value exceeded, chemical is retained for refined risk characterization
Pass = Screening value not exceeded and chemical passed screening evaluation; conclusion of no potential for risk; no further evaluation
Uncertain = uncertainty exists because no toxicological screening value was found for evaluating potential for risk
HQ = Hazard Quotient = Maximum Detect / Benchmark
DF = Detection Frequency
mg/kg = milligram per kilogram
NOEC = No observed Effect concentration
Hazard quotients in bold exceed one.
Chemicals not detected in any samples are
NA - not applicable
NSV - no screening value available
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/14 Page 4 of 4
Table 15
Direct Toxicity Screening for Invertebrates Exposed to Soil Using Maximum Detected Concentrations
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Anal te
Soil NOEC Screening Value
mg/kg
Soil Ma imum Detection
Concentration1 (mg/kg) DF NOEC HQ
2
Screening
Conclusion
1,3,5-Trinitrobenzene 32.80 0.105 0% 0.0032 Pass
1,3-Dinitrobenzene 32.80 0.08 0% 0.0024 Pass
2,4,6-Trinitrotoluene (TNT) 32.80 1.5 0% 0.046 Pass
2,4-Dinitrophenol 0.70 50 0%71.00 Retain
2,4-Dinitrotoluene 32.80 2 2% 0.061 Pass
2,6-Dinitrotoluene 32.80 10.5 0% 0.32 Pass
2-Amino-4,6-Dinitrotoluene 32.80 1.5 0% 0.046 Pass
2-Nitroaniline NSV 50 0%NA Uncertain
2-Nitrophenol 0.70 10.5 0%15.00 Retain
2-Nitrotoluene 32.80 0.14 0% 0.0043 Pass
3-Nitroaniline NSV 50 0%NA Uncertain
3-Nitrotoluene 32.80 0.15 0% 0.0046 Pass
4,6-Dinitro-2-methylphenol NSV 50 0%NA Uncertain
4-Nitroaniline NSV 50 0%NA Uncertain
4-Nitrophenol 0.70 50 0%71.00 Retain
4-Nitrotoluene 32.80 0.19 0% 0.0058 Pass
HMX 1.56 25 31%16.00 Retain
Nitrobenzene 4.00 10.5 0%2.6 Retain
Nitroglycerin NSV 0.34 0%NA Uncertain
Nitroguanidine NSV 0.3 5%NA Uncertain
PETN NSV 0.5 0%NA Uncertain
Picric acid NSV 0.5 7%NA Uncertain
RDX 27.40 1.5 0% 0.055 Pass
Tetryl NSV 0.23 0%NA Uncertain
HI - Energetics 16.00 Retain
Aluminum NSV 54000 100%NA Uncertain
Antimony 78.00 166.93 79%2.1 Retain
Arsenic 6.00 41.3 58%6.9 Retain
Barium 330.00 640 100%1.9 Retain
Beryllium 40.00 0.72 48% 0.018 Pass
Cadmium 140.00 32 44% 0.23 Pass
Carbon disulfide NSV 0.0011 5%NA Uncertain
Chromium 0.04 55.3 100%1400 Retain
Cobalt 300.00 4.9 79% 0.016 Pass
Copper 5.00 18000 85%3600.00 Retain
Iron NSV 15000 100%NA Uncertain
Lead 1700.00 48000 83%28.00 Retain
Magnesium NSV 24300 100%NA Uncertain
Manganese NSV 519 100%NA Uncertain
Mercury 0.01 0.07 27%7.0 Retain
Molybdenum NSV 17 91%NA Uncertain
Nickel 20.00 41.3 100%2.1 Retain
Nitrate NSV 22.8 92%NA Uncertain
Perchlorate 4.45 4.5 50%1.0 Retain
Phosphorus NSV 990 100%NA Uncertain
Selenium 7.00 5 0% 0.71 Pass
Silver NSV 4 8%NA Uncertain
Strontium NSV 484 100%NA Uncertain
Thallium 12.00 0.55 54% 0.046 Pass
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/15 Page 1 of 4
Table 15
Direct Toxicity Screening for Invertebrates Exposed to Soil Using Maximum Detected Concentrations
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Anal te
Soil NOEC Screening Value
mg/kg
Soil Ma imum Detection
Concentration1 (mg/kg) DF NOEC HQ
2
Screening
Conclusion
Vanadium NSV 25.7 100%NA Uncertain
Zinc 20.00 2300 100%120.00 Retain
HI - Inorganics 5100 Retain
2-Methylnaphthalene 3.00 170 14%57.00 Retain
Acenaphthene 3.10 0.04185 0% 0.014 Pass
Acenaphthylene 2.30 10.5 0%4.6 Retain
Anthracene 0.50 3.7 7%7.4 Retain
Benzo(a)anthracene 980.00 10.5 0% 0.011 Pass
Benzo(a)pyrene 840.00 10.5 0% 0.012 Pass
Benzo(b)fluoranthene 360.00 10.5 0% 0.029 Pass
Benzo(g,h,i)perylene 360.00 10.5 0% 0.029 Pass
Benzo(k)fluoranthene 560.00 10.5 0% 0.019 Pass
Chrysene 1030.00 10.5 0% 0.010 Pass
Dibenzo(a,h)anthracene 780.00 10.5 0% 0.013 Pass
Fluoranthene 4.70 0.144 4% 0.031 Pass
Fluorene 0.77 33 14%43.00 Retain
Indeno(1,2,3-c,d)pyrene 910.00 10.5 0% 0.012 Pass
Naphthalene 2.00 53 25%27.00 Retain
Phenanthrene 2.10 92 18%44.00 Retain
Pyrene 1.30 10.5 0%8.1 Retain
HI - PAHs 180 Retain
TPH 700.00 47000 100%67.00 Retain
HI - Petroleum 67.00 Retain
2,4,5-Trichlorophenol 0.90 50 0%56.00 Retain
2,4,6-Trichlorophenol 1.00 10.5 0%11.00 Retain
2,4-Dichlorophenol 1.00 10.5 0%11.00 Retain
2,4-Dimethylphenol NSV 10.5 0%NA Uncertain
2-Chloronaphthalene NSV 10.5 0%NA Uncertain
2-Methylphenol NSV 10.5 0%NA Uncertain
3,3-Dichlorobenzidine NSV 21 0%NA Uncertain
4-Chloro-3-methylphenol NSV 10.5 0%NA Uncertain
4-Chloroaniline 3.00 10.5 0%3.5 Retain
4-Methylphenol NSV 10.5 0%NA Uncertain
Benzoic acid NSV 50 0%NA Uncertain
Benzylalcohol NSV 10.5 0%NA Uncertain
bis(2-Ethylhexyl)phthalate 20.00 1.5 18% 0.075 Pass
Butyl benzylphthalate 20.00 10.5 0% 0.52 Pass
Dibenzofuran 1.40 12 14%8.6 Retain
Diethylphthalate 20.00 10.5 0% 0.52 Pass
Dimethylphthalate 20.00 10.5 0% 0.52 Pass
Di-n-butylphthalate 20.00 10.5 0% 0.52 Pass
Di-n-octylphthalate 20.00 10.5 0% 0.52 Pass
Hexachlorobenzene NSV 10.5 0%NA Uncertain
Hexachlorobutadiene NSV 0.0008 4%NA Uncertain
Hexachlorocyclopentadiene NSV 10.5 0%NA Uncertain
Hexachloroethane NSV 10.5 0%NA Uncertain
Isophorone NSV 10.5 0%NA Uncertain
n-Nitroso-di-n-propylamine 2.00 10.5 0%5.2 Retain
n-Nitrosodiphenylamine 2.00 10.5 0%5.2 Retain
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/15 Page 2 of 4
Table 15
Direct Toxicity Screening for Invertebrates Exposed to Soil Using Maximum Detected Concentrations
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Anal te
Soil NOEC Screening Value
mg/kg
Soil Ma imum Detection
Concentration1 (mg/kg) DF NOEC HQ
2
Screening
Conclusion
Pentachlorophenol 31.00 50 0%1.6 Retain
HI - SVOCs 8.6 Retain
1,1,1,2-Tetrachloroethane 2.00 0.0006 5% 0.00030 Pass
1,1,1-Trichloroethane 2.00 0.0009 5% 0.00045 Pass
1,1,2,2-Tetrachloroethane 2.00 0.001 5% 0.00050 Pass
1,1,2-Trichloroethane 2.00 0.0008 5% 0.00040 Pass
1,1-Dichloroethane 2.00 0.0007 5% 0.00035 Pass
1,1-Dichloroethene 2.00 0.0011 5% 0.00055 Pass
1,2,3-Trichlorobenzene 2.00 0.0028 5% 0.0014 Pass
1,2,3-Trichloropropane 70.00 0.0009 5% 0.000013 Pass
1,2,4-Trichlorobenzene 2.00 0.0032 4% 0.0016 Pass
1,2-Dibromo-3-chloropropane NSV 0.0039 5%NA Uncertain
1,2-Dichlorobenzene 2.00 0.0014 4% 0.00070 Pass
1,2-Dichloroethane 70.00 0.0008 5% 0.000011 Pass
1,2-Dichloropropane 70.00 0.0007 5% 0.0000100 Pass
1,2-Ethylene Dibromide NSV 0.0009 5%NA Uncertain
1,3-Dichlorobenzene 2.00 0.0019 4% 0.00095 Pass
1,4-Dichlorobenzene 2.00 0.0031 4% 0.0016 Pass
2-Butanone NSV 0.0159 18%NA Uncertain
2-ChloroethylVinylEther NSV 0.00595 0%NA Uncertain
2-Chlorophenol 1.00 10.5 0%11.00 Retain
2-Hexanone NSV 0.0038 5%NA Uncertain
4-Bromophenylphenylether NSV 10.5 0%NA Uncertain
4-Chlorophenylphenylether NSV 10.5 0%NA Uncertain
4-Methyl-2-pentanone NSV 0.0043 5%NA Uncertain
Acetone NSV 24 32%NA Uncertain
Benzene 1.61 0.0041 14% 0.0025 Pass
Bis(2-chloroethoxy)methane NSV 0.074 0%NA Uncertain
bis(2-chloroethyl)ether NSV 10.5 0%NA Uncertain
bis(2-chloroisopropyl)ether NSV 10.5 0%NA Uncertain
Bromodichloromethane NSV 0.0007 5%NA Uncertain
Bromoform NSV 0.0005 5%NA Uncertain
Bromomethane NSV 0.0015 5%NA Uncertain
Carbon tetrachloride NSV 0.0009 5%NA Uncertain
Chlorobenzene 4.00 0.0007 5% 0.00018 Pass
Chloroethane 4.00 0.001 5% 0.00025 Pass
Chloroform 4.00 0.0007 5% 0.00018 Pass
Chloromethane 4.00 0.001 5% 0.00025 Pass
cis-1,2-Dichloroethene 70.00 0.0007 5% 0.0000100 Pass
cis-1,3-Dichloropropene 70.00 0.0006 5% 0.0000086 Pass
Dibromochloromethane NSV 0.0007 5%NA Uncertain
Dibromomethane NSV 0.0005 5%NA Uncertain
Dichlorodifluoromethane NSV 0.0011 5%NA Uncertain
Ethylbenzene 1.13 0.0013 5% 0.0012 Pass
m,p-Xylene 0.56 0.002 5% 0.0036 Pass
Methylene chloride NSV 0.0032 5%NA Uncertain
o-Xylene 0.56 0.0027 14% 0.0048 Pass
Phenol 3.00 10.5 0%3.5 Retain
Styrene 0.56 0.0026 14% 0.0046 Pass
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/15 Page 3 of 4
Table 15
Direct Toxicity Screening for Invertebrates Exposed to Soil Using Maximum Detected Concentrations
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Anal te
Soil NOEC Screening Value
mg/kg
Soil Ma imum Detection
Concentration1 (mg/kg) DF NOEC HQ
2
Screening
Conclusion
tert-ButylMethylEther NSV 0.0007 5%NA Uncertain
Tetrachloroethene NSV 0.0009 5%NA Uncertain
Toluene 0.44 0.0187 23% 0.042 Pass
Trans-1,2-Dichloroethene 70.00 0.0007 5% 0.0000100 Pass
Trans-1,3-Dichloropropene 70.00 0.0008 5% 0.000011 Pass
Trichloroethylene (TCE) NSV 0.0007 5%NA Uncertain
Trichlorofluoromethane NSV 0.0011 5%NA Uncertain
Vinyl Acetate NSV 0.0012 5%NA Uncertain
Vinyl chloride NSV 0.0012 5%NA Uncertain
HI - VOCs 0.065 Pass
Notes:
1 EPC = Exposure Point Concentration. Maximum detected concentration or 1/2 detection limit for non-detected analytes
2 Hazard Indices (HI) calculated as the sum of HQs for detected analytes
Retain = screening value exceeded, chemical is retained for refined risk characterization
Pass = Screening value not exceeded and chemical passed screening evaluation; conclusion of no potential for risk; no further evaluation
Uncertain = uncertainty exists because no toxicological screening value was found for evaluating potential for risk
HQ = Hazard Quotient = Maximum Detect / Benchmark
DF = Detection Frequency
mg/kg = milligram per kilogram
NOEC = No observed Effect concentration
Hazard quotients in bold exceed one.
NA - not applicable
NSV - no screening value available
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/15 Page 4 of 4
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-

0

0

0

-

0
0
10
0

1
1
.
3

1
1
9
13
.
2

1
3
.
2
10
.
5

2
.
0
0
0.
0
2
3
3

1
3
.
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
4
2
8

0
.
0
5
9
9
0.
0
0
6
6
5

0
.
0
0
6
6
5
0.
1
4
0

2
.
0
0
0.
0
0
0
3
1
1

0
.
0
0
6
9
7
2.
0

<
0
.
0
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
3-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
6
.
8

8
4
0
93
.
3

9
3
.
3
50

2
.
0
0
0.
1
1
1

9
3
.
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

6
.
1
2

0
.
9
1
9
0.
1
0
2

0
.
1
0
2
0.
1
5
0

2
.
0
0
0.
0
0
0
3
3
3

0
.
1
0
2
2.
0

0
.
0
5
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
1
8
2

9
.
0
8
1.
0
1

1
.
0
1
50

2
.
0
0
0.
1
1
1

1
.
1
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
0
4

1
5
2
16
.
9

1
6
.
9
50

2
.
0
0
0.
1
1
1

1
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
N
i
t
r
o
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
9
9
2

4
9
.
6
5.
5
1

5
.
5
1
50

2
.
0
0
0.
1
1
1

5
.
6
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

6
.
6
6

1
.
2
7
0.
1
4
1

0
.
1
4
1
0.
1
9
0

2
.
0
0
0.
0
0
0
4
2
2

0
.
1
4
1
2.
0

0
.
0
7
0

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

H
M
X

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
7
9.
7
4

9
.
7
4
25

2
.
0
0
0.
0
5
5
5

9
.
7
9
1.
0
9.
8
31
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ni
t
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
1
3

1
1
.
9
1.
3
2

1
.
3
2
10
.
5

2
.
0
0
0.
0
2
3
3

1
.
3
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ni
t
r
o
g
l
y
c
e
r
i
n
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
4
.
7

5
.
0
1
0.
5
5
6

0
.
5
5
6
0.
3
4
0

2
.
0
0
0.
0
0
0
7
5
5

0
.
5
5
7
3.
0

0
.
1
9

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

N
i
t
r
o
g
u
a
n
i
d
i
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
3
9

4
1
.
6
4.
6
2

4
.
6
2
0.
3
0
0

2
.
0
0
0.
0
0
0
6
6
6

4
.
6
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
PE
T
N
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

6
.
5
4

3
.
2
7
0.
3
6
3

0
.
3
6
3
0.
5
0
0

2
.
0
0
0.
0
0
1
1
1

0
.
3
6
4
17
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

P
i
c
r
i
c

a
c
i
d

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
7
.
4

8
.
7
2
0.
9
6
8

0
.
9
6
8
0.
5
0
0

2
.
0
0
0.
0
0
1
1
1

0
.
9
6
9
NS
V
--
7%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
RD
X
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
4.
1
8

4
.
1
8
1.
5
0

2
.
0
0
0.
0
0
3
3
3

4
.
1
8
2.
0
2.
1
0%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Te
t
r
y
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
7
8

0
.
4
0
8
0.
0
4
5
4

0
.
0
4
5
4
0.
2
3
0

2
.
0
0
0.
0
0
0
5
1
1

0
.
0
4
5
9
1.
3

0
.
0
3
5

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

E
n
e
r
g
e
t
i
c
s
9.
9
(d
e
t
s
)
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
l
u
m
i
n
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
4
0
0

2
1
6
24

2
4
54
0
0
0

2
.
0
0
12
0

1
4
4
1.
9
75
10
0
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
n
t
i
m
o
n
y

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
5
0
0

8
.
3
5
0.
9
2
7

0
.
9
2
7
16
7

2
.
0
0
0.
3
7
1

1
.
3
0
0.
1
22
79
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
r
s
e
n
i
c

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
1
1
0.
1
2
4

0
.
1
2
4
41
.
3

2
.
0
0
0.
0
9
1
7

0
.
2
1
5
0.
4

0
.
5
4

5
8
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

B
a
r
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
1
0
0

6
4
7.
1
1

7
.
1
1
64
0

2
.
0
0
1.
4
2

8
.
5
3
45
.
0

0
.
1
9

1
0
0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

B
e
r
y
l
l
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

0
.
0
0
7
2
0
0.
0
0
0
8
0
0

0
.
0
0
0
8
0
0
0.
7
2
0

2
.
0
0
0.
0
0
1
6
0

0
.
0
0
2
4
0
0.
5
3

<
0
.
0
1

4
8
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

C
a
d
m
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
.
1
2
0.
4
5
8

0
.
4
5
8
32

2
.
0
0
0.
0
7
1
1

0
.
5
2
9
0.
8

0
.
6
9

4
4
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

9
.
3
2

0
.
0
1
0
3
0.
0
0
1
1
4

0
.
0
0
1
1
4
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
2
4
4

0
.
0
0
1
1
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

C
h
r
o
m
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
4
0
0

2
.
2
1
0.
2
4
6

0
.
2
4
6
55
.
3

2
.
0
0
0.
1
2
3

0
.
3
6
8
3.
3

0
.
1
1

1
0
0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

C
o
b
a
l
t

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
5
4
0

0
.
2
6
5
0.
0
2
9
4

0
.
0
2
9
4
4.
9
0

2
.
0
0
0.
0
1
0
9

0
.
0
4
0
3
1.
1

0
.
0
3
5

7
9
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

C
o
p
p
e
r

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

9
2
.
7
10
.
3

1
0
.
3
18
0
0
0

2
.
0
0
40

5
0
.
3
11
.
7
4.
3
85
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

I
r
o
n

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

1
5
0
16
.
7

1
6
.
7
15
0
0
0

2
.
0
0
33
.
3

5
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

L
e
a
d

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
1
2
12
.
4

1
2
.
4
48
0
0
0

2
.
0
0
10
7

1
1
9
0.
9
13
0
83
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

M
a
g
n
e
s
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
0
6

5
0
1
0
0
55
6
0

5
5
6
0
24
3
0
0

2
.
0
0
54

5
6
1
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

M
a
n
g
a
n
e
s
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
6
8
0

3
5
3
39
.
2

3
9
.
2
51
9

2
.
0
0
1.
1
5

4
0
.
3
88
.
0

0
.
4
6

1
0
0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

M
e
r
c
u
r
y

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
0
8
6
9
0.
0
0
9
6
5

0
.
0
0
9
6
5
0.
0
7
0
0

2
.
0
0
0.
0
0
0
1
5
5

0
.
0
0
9
8
1
0.
0

0
.
3
1

2
7
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

M
o
l
y
b
d
e
n
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

6
.
8
0
0.
7
5
5

0
.
7
5
5
17

2
.
0
0
0.
0
3
7
8

0
.
7
9
3
0.
3
3.
0
91
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

N
i
c
k
e
l

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
7
5
0.
1
9
4

0
.
1
9
4
41
.
3

2
.
0
0
0.
0
9
1
7

0
.
2
8
6
40
.
0

<
0
.
0
1

1
0
0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

N
i
t
r
a
t
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
0
0

2
2
.
8
2.
5
3

2
.
5
3
22
.
8

2
.
0
0
0.
0
5
0
6

2
.
5
8
50
7
.
0

<
0
.
0
1

9
2
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

P
e
r
c
h
l
o
r
a
t
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
8
2

1
2
7
0
14
1

1
4
1
4.
5
0

2
.
0
0
0.
0
1
0
0
0

1
4
1
2.
6
54
50
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

P
h
o
s
p
h
o
r
u
s

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
0
0

9
9
0
11
0

1
1
0
99
0

2
.
0
0
2.
2
0

1
1
2
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Se
l
e
n
i
u
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
3
3
3

0
.
3
3
3
5.
0
0

2
.
0
0
0.
0
1
1
1

0
.
3
4
4
0.
2
1.
7
0%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

S
i
l
v
e
r

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
0
0

4
.
0
0
0.
4
4
4

0
.
4
4
4
4.
0
0

2
.
0
0
0.
0
0
8
8
8

0
.
4
5
3
2.
4

0
.
1
9

8
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

S
t
r
o
n
t
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
1
0

5
3
2
59
.
1

5
9
.
1
48
4

2
.
0
0
1.
0
8

6
0
.
2
26
3
.
0

0
.
2
3

1
0
0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

T
h
a
ll
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
4
0
0

0
.
0
0
2
2
0
0.
0
0
0
2
4
4

0
.
0
0
0
2
4
4
0.
5
5
0

2
.
0
0
0.
0
0
1
2
2

0
.
0
0
1
4
7
0.
0

0
.
2
0

5
4
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

V
a
n
a
d
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
5
0

0
.
1
4
1
0.
0
1
5
7

0
.
0
1
5
7
25
.
7

2
.
0
0
0.
0
5
7
1

0
.
0
7
2
8
0.
2

0
.
3
5

1
0
0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

Z
i
n
c

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
5
5
39
.4
39
.4
23
0
0

2
.
0
0
5.
1
1

4
4
.
5
16
0
.
0

0
.
2
8

1
0
0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

I
n
o
r
g
a
n
i
c
s
29
0
(d
e
t
s
)
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
8
7

3
1
8
35
.
3

3
5
.
3
17
0

2
.
0
0
0.
3
7
8

3
5
.
7
5.
0
7.
1
14
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
c
e
n
a
p
h
t
h
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
7
.
2
1.
9
1

1
.
9
1
0.
0
4
1
8

2
.
0
0
0.
0
0
0
0
9
3
0

1
.
9
1
17
5
.
0

0
.
0
1
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ac
e
n
a
p
h
t
h
y
l
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
0
.
2
2.
2
4

2
.
2
4
10
.
5

2
.
0
0
0.
0
2
3
3

2
.
2
6
17
5
.
0

0
.
0
1
3

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
n
t
h
r
a
c
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
8
2
6

0
.
8
2
6
3.
7
0

2
.
0
0
0.
0
0
8
2
2

0
.
8
3
5
10
0
0
.
0

<
0
.
0
1

7
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
9
1
2

0
.
9
1
2
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
9
3
5
1.
0

0
.
9
4

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
.
5
1.
1
7

1
.
1
7
10
.
5

2
.
0
0
0.
0
2
3
3

1
.
1
9
1.
0
1.
2
0%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
1
0

3
.
2
6
0.
3
6
1

0
.
3
6
1
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
3
8
5
1.
0

0
.
3
8

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
4.
5
5

4
.
5
5
10
.
5

2
.
0
0
0.
0
2
3
3

4
.
5
7
1.
0
4.
6
0%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
8
4
0.
9
8
1

0
.
9
8
1
10
.
5

2
.
0
0
0.
0
2
3
3

1
.
0
0
1.
0
1.
0
0%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
r
y
s
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
9
1
2

0
.
9
1
2
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
9
3
5
1.
0

0
.
9
4

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
1
3
0

1
.
3
6
0.
1
5
2

0
.
1
5
2
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
1
7
5
1.
0

0
.
1
7

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
8
0
0

0
.
0
0
8
0
0
0.
1
4
4

2
.
0
0
0.
0
0
0
3
2
0

0
.
0
0
8
3
2
12
5
.
0

<
0
.
0
1

4
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

F
l
u
o
r
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
1
9
0
57
6

5
7
6
33

2
.
0
0
0.
0
7
3
3

5
7
6
12
5
.
0
4.
6
14
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
1
1
0

1
.
1
6
0.
1
2
8

0
.
1
2
8
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
1
5
2
1.
0

0
.
1
5

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

N
a
p
h
t
h
a
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
2
.
2

6
4
7
71
.
8

7
1
.
8
53

2
.
0
0
0.
1
1
8

7
1
.
9
50
.
0
1.
4
25
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
9
.
5
2.
1
7

2
.
1
7
92

2
.
0
0
0.
2
0
4

2
.
3
7
17
5
.
0

0
.
0
1
4

1
8
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Py
r
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
7
2
0

7
.
5
6
0.
8
4
0

0
.
8
4
0
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
8
6
3
75
.
0

0
.
0
1
2

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

P
A
H
s
13
(d
e
t
s
)
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

T
P
H

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

-

0
00
47
0
0
0

2
.
0
0
10
4

1
0
4
10
0
0
.
0

0
.
1
0

1
0
0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

P
e
t
r
o
l
e
u
m
0.
1
0
(d
e
t
s
)
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
2
0
2

1
.
0
1
0.
1
1
2

0
.
1
1
2
50

2
.
0
0
0.
1
1
1

0
.
2
2
3
0.
2

0
.
9
3

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
7

0
.
1
5
4
0.
0
1
7
1

0
.
0
1
7
1
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
0
4
0
4
0.
2

0
.
1
7

0
%
Pa
s
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d
y

W
e
i
g
h
t

(k
g
)
Da
i
l
y

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
bw
/
d
a
y
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l
y

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
bw
/
d
a
y
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b
w
/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b
w
/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b
w
/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b
w
/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
bw
/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a
y
)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b
w
/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c
y

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
1
1
8

1
.
2
4
0.
1
3
8

0
.
1
3
8
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
1
6
1
0.
2

0
.
6
7

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
1
4
3

1
.
5
0
0.
1
6
7

0
.
1
6
7
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
1
9
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
.
1
1
6
0.
0
1
2
9

0
.
0
1
2
9
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
0
3
6
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2-
M
e
t
h
y
l
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

9
.
7
7

1
0
3
11
.
4

1
1
.
4
10
.
5

2
.
0
0
0.
0
2
3
3

1
1
.
4
34
0
.
0

0
.
0
3
4

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
2
8

4
7
.
8
5.
3
1

5
.
3
1
21

2
.
0
0
0.
0
4
6
6

5
.
3
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
7
6
7

0
.
8
0
5
0.
0
8
9
4

0
.
0
8
9
4
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
1
1
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
C
h
l
o
r
o
a
n
i
l
i
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
1
8

1
2
.
4
1.
3
7

1
.
3
7
10
.
5

2
.
0
0
0.
0
2
3
3

1
.
4
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
M
e
t
h
y
l
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
9
5
1

9
.
9
8
1.
1
1

1
.
1
1
10
.
5

2
.
0
0
0.
0
2
3
3

1
.
1
3
34
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
i
c

a
c
i
d
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
0
8

5
4
.
1
6.
0
1

6
.
0
1
50

2
.
0
0
0.
1
1
1

6
.
1
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
y
l
a
l
c
o
h
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

5
.
6
7

5
9
.
5
6.
6
1

6
.
6
1
10
.
5

2
.
0
0
0.
0
2
3
3

6
.
6
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
6
6
0

0
.
0
9
9
0
0.
0
1
1
0

0
.
0
1
1
0
1.
5
0

2
.
0
0
0.
0
0
3
3
3

0
.
0
1
4
3
18
.
3

<
0
.
0
1

1
8
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
1
8
2

0
.
0
1
9
1
0.
0
0
2
1
2

0
.
0
0
2
1
2
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
0
2
5
4
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

D
i
b
e
n
z
o
f
u
r
a
n

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
8
9

2
2
.
6
2.
5
2

2
.
5
2
12

2
.
0
0
0.
0
2
6
7

2
.
5
4
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
0
4

3
.
2
0
0.
3
5
5

0
.
3
5
5
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
3
7
8
45
8
3
.
0

<
0
.
0
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
1
1

2
2
.
1
2.
4
6

2
.
4
6
10
.
5

2
.
0
0
0.
0
2
3
3

2
.
4
8
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
2
9
8

0
.
0
3
1
3
0.
0
0
3
4
8

0
.
0
0
3
4
8
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
0
2
6
8
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
4
6
1

4
.
8
4
0.
5
3
7

0
.
5
3
7
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
5
6
0
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
0
7
8
5

0
.
0
0
8
2
4
0.
0
0
0
9
1
6

0
.
0
0
0
9
1
6
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
0
2
4
2
1.
6

0
.
0
1
5

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
2
0
7

#
#
#
#
#
#
#
#
#
0.
0
0
0
0
0
0
1
8
4

0
.
0
0
0
0
0
0
1
8
4
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
1
7
8

0
.
0
0
0
0
0
1
9
6
1.
6

<
0
.
0
1

4
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
.
1
1
6
0.
0
1
2
9

0
.
0
1
2
9
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
0
3
6
2
1.
6

0
.
0
2
3

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
3
0
5

0
.
0
3
2
0
0.
0
0
3
5
5

0
.
0
0
3
5
5
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
0
2
6
9
1.
6

0
.
0
1
7

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Is
o
p
h
o
r
o
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
4
6
7

4
.
9
1
0.
5
4
5

0
.
5
4
5
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
5
6
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
4
5

2
5
.
7
2.
8
6

2
.
8
6
10
.
5

2
.
0
0
0.
0
2
3
3

2
.
8
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
7
1
9

0
.
7
5
5
0.
0
8
3
9

0
.
0
8
3
9
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
1
0
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
1
2
9

0
.
0
6
4
4
0.
0
0
7
1
6

0
.
0
0
7
1
6
50

2
.
0
0
0.
1
1
1

0
.
1
1
8
0.
2

0
.
4
9

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

S
V
O
C
s
<0
.
0
1

(
d
e
t
s
)
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
2
1
4
0.
0
0
0
2
3
7

0
.
0
0
0
2
3
7
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
2
3
9
1.
4

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
2
7
9

0
.
0
0
0
2
5
1
0.
0
0
0
0
2
7
9

0
.
0
0
0
0
2
7
9
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
2
0
0

0
.
0
0
0
0
2
9
9
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
3
5
4
0.
0
0
0
0
3
9
3

0
.
0
0
0
0
3
9
3
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
2
2
2

0
.
0
0
0
0
4
1
5
1.
4

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
2
9
8

0
.
0
0
0
2
3
8
0.
0
0
0
0
2
6
5

0
.
0
0
0
0
2
6
5
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
1
7
8

0
.
0
0
0
0
2
8
2
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
8
9
9
0.
0
0
0
0
9
9
8

0
.
0
0
0
0
9
9
8
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
1
0
1
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
9
0
8
0.
0
0
1
0
1

0
.
0
0
1
0
1
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
2
4
4

0
.
0
0
1
0
1
2.
5

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
3
7

0
.
0
0
3
8
5
0.
0
0
0
4
2
7

0
.
0
0
0
4
2
7
0.
0
0
2
8
0

2
.
0
0
0.
0
0
0
0
0
6
2
2

0
.
0
0
0
4
3
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
5
2
6
0.
0
0
0
5
8
4

0
.
0
0
0
5
8
4
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
2
0
0

0
.
0
0
0
5
8
6
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
8
0

0
.
0
0
0
0
1
8
5
0.
0
0
0
0
0
2
0
6

0
.
0
0
0
0
0
2
0
6
0.
0
0
3
2
0

2
.
0
0
0.
0
0
0
0
0
7
1
1

0
.
0
0
0
0
0
9
1
7
NS
V
--
4%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
4
3
8

0
.
0
0
1
7
1
0.
0
0
0
1
9
0

0
.
0
0
0
1
9
0
0.
0
0
3
9
0

2
.
0
0
0.
0
0
0
0
0
8
6
6

0
.
0
0
0
1
9
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
5
7

0
.
0
0
3
6
0
0.
0
0
0
3
9
9

0
.
0
0
0
3
9
9
0.
0
0
1
4
0

2
.
0
0
0.
0
0
0
0
0
3
1
1

0
.
0
0
0
4
0
3
NS
V
--
4%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
2
0
0
0.
0
0
0
2
2
2

0
.
0
0
0
2
2
2
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
1
7
8

0
.
0
0
0
2
2
4
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
5
7
3
0.
0
0
0
0
6
3
6

0
.
0
0
0
0
6
3
6
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
0
6
5
1
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
1
.
7

0
.
0
1
0
5
0.
0
0
1
1
7

0
.
0
0
1
1
7
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
2
0
0

0
.
0
0
1
1
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
4
9
8
0.
0
0
0
0
0
5
5
3

0
.
0
0
0
0
0
5
5
3
0.
0
0
1
9
0

2
.
0
0
0.
0
0
0
0
0
4
2
2

0
.
0
0
0
0
0
9
7
5
NS
V
--
4%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
8
1
2
0.
0
0
0
0
0
9
0
2

0
.
0
0
0
0
0
9
0
2
0.
0
0
3
1
0

2
.
0
0
0.
0
0
0
0
0
6
8
9

0
.
0
0
0
0
1
5
9
NS
V
--
4%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

2
-
B
u
t
a
n
o
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
7
3
2
0.
0
8
1
3

0
.
0
8
1
3
0.
0
1
5
9

2
.
0
0
0.
0
0
0
0
3
5
3

0
.
0
8
1
4
10
.
0

<
0
.
0
1

1
8
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
0
.
2

0
.
1
2
0
0.
0
1
3
4

0
.
0
1
3
4
0.
0
0
5
9
5

2
.
0
0
0.
0
0
0
0
1
3
2

0
.
0
1
3
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2-
C
h
l
o
r
o
p
h
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
5
5
7

5
.
8
4
0.
6
4
9

0
.
6
4
9
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
6
7
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2-
H
e
x
a
n
o
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
6
3
2
0.
0
0
7
0
2

0
.
0
0
7
0
2
0.
0
0
3
8
0

2
.
0
0
0.
0
0
0
0
0
8
4
4

0
.
0
0
7
0
3
10
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
5
6
6

5
.
9
4
0.
6
6
0

0
.
6
6
0
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
6
8
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
9
3
4

0
.
0
9
8
1
0.
0
1
0
9

0
.
0
1
0
9
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
0
3
4
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
8
5
4
0.
0
0
9
4
9

0
.
0
0
9
4
9
0.
0
0
4
3
0

2
.
0
0
0.
0
0
0
0
0
9
5
5

0
.
0
0
9
5
0
25
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
c
e
t
o
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

7
5
.
6

1
8
1
0
20
1

2
0
1
24

2
.
0
0
0.
0
5
3
3

2
0
1
10
.
0
20
32
%
Re
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

B
e
n
z
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
3
3
9
0.
0
0
3
7
6

0
.
0
0
3
7
6
0.
0
0
4
1
0

2
.
0
0
0.
0
0
0
0
0
9
1
1

0
.
0
0
3
7
7
0.
7

<
0
.
0
1

1
4
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
7
.
9

1
.
3
3
0.
1
4
7

0
.
1
4
7
0.
0
7
4
0

2
.
0
0
0.
0
0
0
1
6
4

0
.
1
4
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
4
0

2
5
.
2
2.
8
0

2
.
8
0
10
.
5

2
.
0
0
0.
0
2
3
3

2
.
8
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
6
5
9

6
.
9
2
0.
7
6
9

0
.
7
6
9
10
.
5

2
.
0
0
0.
0
2
3
3

0
.
7
9
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

8
.
4
9

0
.
0
0
5
9
4
0.
0
0
0
6
6
0

0
.
0
0
0
6
6
0
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
6
6
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Br
o
m
o
f
o
r
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
4
6

0
.
0
0
0
1
7
3
0.
0
0
0
0
1
9
2

0
.
0
0
0
0
1
9
2
0.
0
0
0
5
0
0

2
.
0
0
0.
0
0
0
0
0
1
1
1

0
.
0
0
0
0
2
0
3
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Br
o
m
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
2
9
8
0.
0
0
3
3
1

0
.
0
0
3
3
1
0.
0
0
1
5
0

2
.
0
0
0.
0
0
0
0
0
3
3
3

0
.
0
0
3
3
1
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
.
2
9

0
.
0
0
3
8
6
0.
0
0
0
4
2
9

0
.
0
0
0
4
2
9
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
2
0
0

0
.
0
0
0
4
3
1
16
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
9
4
0
0.
0
0
0
0
1
0
4

0
.
0
0
0
0
1
0
4
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
0
1
2
0
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
7
9
0.
0
0
0
3
1
0

0
.
0
0
0
3
1
0
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
2
2
2

0
.
0
0
0
3
1
2
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
f
o
r
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
8
7
3

0
.
0
0
0
6
1
1
0.
0
0
0
0
6
7
8

0
.
0
0
0
0
6
7
8
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
0
6
9
4
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
8
6
9

0
.
0
0
0
8
6
9
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
2
2
2

0
.
0
0
0
8
7
2
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
7
4
4
0.
0
0
0
8
2
6

0
.
0
0
0
8
2
6
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
8
2
8
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
4
2
7
0.
0
0
0
4
7
4

0
.
0
0
0
4
7
4
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
4
7
5
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
6
7
4

0
.
0
0
0
4
7
2
0.
0
0
0
0
5
2
4

0
.
0
0
0
0
5
2
4
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
0
5
4
0
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Di
b
r
o
m
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
3
.
3

0
.
0
0
6
6
5
0.
0
0
0
7
3
8

0
.
0
0
0
7
3
8
0.
0
0
0
5
0
0

2
.
0
0
0.
0
0
0
0
0
1
1
1

0
.
0
0
0
7
3
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
5
8
0

0
.
0
0
0
6
3
8
0.
0
0
0
0
7
0
8

0
.
0
0
0
0
7
0
8
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
2
4
4

0
.
0
0
0
0
7
3
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Et
h
y
l
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
8
9
8
0.
0
0
0
0
0
9
9
7

0
.
0
0
0
0
0
9
9
7
0.
0
0
1
3
0

2
.
0
0
0.
0
0
0
0
0
2
8
9

0
.
0
0
0
0
1
2
9
97
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
m,
p
-
X
y
l
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
6
0
8
0.
0
0
0
6
7
5

0
.
0
0
0
6
7
5
0.
0
0
2
0
0

2
.
0
0
0.
0
0
0
0
0
4
4
4

0
.
0
0
0
6
7
9
17
9
.
0

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
.
1
0

0
.
0
1
3
1
0.
0
0
1
4
6

0
.
0
0
1
4
6
0.
0
0
3
2
0

2
.
0
0
0.
0
0
0
0
0
7
1
1

0
.
0
0
1
4
6
5.
9

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

o
-
X
y
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
3
4

0
.
0
0
9
0
1
0.
0
0
1
0
0

0
.
0
0
1
0
0
0.
0
0
2
7
0

2
.
0
0
0.
0
0
0
0
0
6
0
0

0
.
0
0
1
0
1
17
9
.
0

<
0
.
0
1

1
4
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ph
e
n
o
l
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
6
2

2
7
.
5
3.
0
5

3
.
0
5
10
.
5

2
.
0
0
0.
0
2
3
3

3
.
0
7
17
.
1

0
.
1
8

0
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

S
t
y
r
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
.
0
2

0
.
0
1
0
5
0.
0
0
1
1
6

0
.
0
0
1
1
6
0.
0
0
2
6
0

2
.
0
0
0.
0
0
0
0
0
5
7
7

0
.
0
0
1
1
7
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
9

0
.
0
1
3
3
0.
0
0
1
4
7

0
.
0
0
1
4
7
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
1
4
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

2

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
2
2
7
0.
0
0
0
2
5
2

0
.
0
0
0
2
5
2
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
2
0
0

0
.
0
0
0
2
5
4
1.
4

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

T
o
l
u
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
8
8
2
0.
0
0
9
7
9

0
.
0
0
9
7
9
0.
0
1
8
7

2
.
0
0
0.
0
0
0
0
4
1
5

0
.
0
0
9
8
3
52
.
0

<
0
.
0
1

2
3
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
1
9
5

0
.
0
0
0
1
9
5
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
1
9
6
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
6
5
4
0.
0
0
0
0
7
2
7

0
.
0
0
0
0
7
2
7
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
1
7
8

0
.
0
0
0
0
7
4
4
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
3
1

0
.
0
0
0
2
3
2
0.
0
0
0
0
2
5
8

0
.
0
0
0
0
2
5
8
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
0
2
7
3
0.
7

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
2
6
1

0
.
0
0
0
2
8
8
0.
0
0
0
0
3
1
9

0
.
0
0
0
0
3
1
9
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
2
4
4

0
.
0
0
0
0
3
4
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Vi
n
y
l

A
c
e
t
a
t
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
2

0
.
0
2
6
4
0.
0
0
2
9
3

0
.
0
0
2
9
3
0.
0
0
1
2
0

2
.
0
0
0.
0
0
0
0
0
2
6
7

0
.
0
0
2
9
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
1
0

0
.
0
0
3
7
2
0.
0
0
0
4
1
3

0
.
0
0
0
4
1
3
0.
0
0
1
2
0

2
.
0
0
0.
0
0
0
0
0
2
6
7

0
.
0
0
0
4
1
6
0.
2

<
0
.
0
1

5
%
Pa
s
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

V
O
C
s
20
(d
e
t
s
)
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

4
.
7
8

0
.
5
0
2
0.
0
2
5
1

0
.
0
2
5
1
0.
1
0
5

2
.
0
0
0.
0
0
0
1
0
5

0
.
0
2
5
2
2.
7

<
0
.
0
1

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
5

1
.
2
0
0.
0
6
0
0

0
.
0
6
0
0
0.
0
8
0
0

2
.
0
0
0.
0
0
0
0
7
9
9

0
.
0
6
0
1
0.
0
1.
5
0%
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

4
.
2
3

6
.
3
4
0.
3
1
7

0
.
3
1
7
1.
5
0

2
.
0
0
0.
0
0
1
5
0

0
.
3
1
8
2.
0

0
.
1
6

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

2
.
4
0

1
2
0
5.
9
9

5
.
9
9
50

2
.
0
0
0.
0
5
0
0

6
.
0
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
6
0
7

1
.
2
1
0.
0
6
0
6

0
.
0
6
0
6
2.
0
0

2
.
0
0
0.
0
0
2
0
0

0
.
0
6
2
6
2.
0

0
.
0
3
1

2
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
1

1
1
6
5.
7
7

5
.
7
7
10
.
5

2
.
0
0
0.
0
1
0
5

5
.
7
8
2.
0
2.
9
0%
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
.
7
2
0.
1
3
6

0
.
1
3
6
1.
5
0

2
.
0
0
0.
0
0
1
5
0

0
.
1
3
7
9.
0

0
.
0
1
5

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2-
N
i
t
r
o
a
n
i
l
i
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
0
.
7

5
3
6
26
.
8

2
6
.
8
50

2
.
0
0
0.
0
5
0
0

2
6
.
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2-
N
i
t
r
o
p
h
e
n
o
l
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
1
.
3

1
1
9
5.
9
5

5
.
9
5
10
.
5

2
.
0
0
0.
0
1
0
5

5
.
9
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
4
2
8

0
.
0
5
9
9
0.
0
0
2
9
9

0
.
0
0
2
9
9
0.
1
4
0

2
.
0
0
0.
0
0
0
1
4
0

0
.
0
0
3
1
3
2.
0

<
0
.
0
1

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
3-
N
i
t
r
o
a
n
i
l
i
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
6
.
8

8
4
0
41
.
9

4
1
.
9
50

2
.
0
0
0.
0
5
0
0

4
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

6
.
1
2

0
.
9
1
9
0.
0
4
5
9

0
.
0
4
5
9
0.
1
5
0

2
.
0
0
0.
0
0
0
1
5
0

0
.
0
4
6
0
2.
0

0
.
0
2
3

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
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5
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To
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2
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3
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--
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n
To
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6
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2
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0

0
.
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3
2

0
%
Pa
s
s
To
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d
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s

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R
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g
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8
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2
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4
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4
0
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0
4.
4
31
%
Re
t
a
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n
To
w
n
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d
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s

G
r
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u
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d

S
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5

0
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6
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3
NS
V
--
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t
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n
To
w
n
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d
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s

G
r
o
u
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d

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1
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0

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8
4

0
%
Pa
s
s
To
w
n
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d
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s

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r
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d

S
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2
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8
NS
V
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Un
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t
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n
To
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17
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0
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0
1

0
%
Pa
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s
To
w
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d
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r
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2
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0
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4
3
6
NS
V
--
7%
Un
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t
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n
To
w
n
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d
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10
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R
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s
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n

B
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d

3
7
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6
1.
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8

1
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5
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0
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8
8
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0

0
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9
4

0
%
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s
To
w
n
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d
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r
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d

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7
8

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4
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3

0
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1
6

0
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s
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d
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s

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r
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d

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4
(d
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s
)
Re
t
a
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n
To
w
n
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d
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s

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r
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d

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A
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5
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4
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2
1
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10
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8

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8
54
0
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2
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0
0
53
.
9

6
4
.
7
1.
9
34
10
0
%
Re
t
a
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n
To
w
n
s
e
n
d
'
s

G
r
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u
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d

S
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A
n
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0
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0
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8
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3
5
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4
1
7

0
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4
1
7
16
7

2
.
0
0
0.
1
6
7

0
.
5
8
4
0.
1
9.
9
79
%
Re
t
a
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n
To
w
n
s
e
n
d
'
s

G
r
o
u
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d

S
q
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A
r
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0
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3
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0
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5
0

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0

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0
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10
0

R
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g
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s
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n

B
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d

1
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1
1
0.
0
5
5
6

0
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5
5
6
41
.
3

2
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0
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4
1
3

0
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0
9
6
8
0.
4

0
.
2
4

5
8
%
Pa
s
s
To
w
n
s
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n
d
'
s

G
r
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d

S
q
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0
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3
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6
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64
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2
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6
3
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3
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8
4
45
.
0

0
.
0
8
5

1
0
0
%
Pa
s
s
To
w
n
s
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n
d
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s

G
r
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d

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0
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0
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0
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7
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2
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9

0
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0
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5

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0
.
0
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4
8
%
Pa
s
s
To
w
n
s
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d
'
s

G
r
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u
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d

S
q
u
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a
d
m
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m

0
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3
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5

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0
5
0

1

0
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5
0

0

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0

0

0

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0
0
10
0

R
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g
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s
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n

B
a
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d

4
.
1
2
0.
2
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6

0
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2
0
6
32

2
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0
0
0.
0
3
2
0

0
.
2
3
8
0.
8

0
.
3
1

4
4
%
Pa
s
s
To
w
n
s
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n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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d
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s
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f
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e
0.
3
2
5

0
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0
5
0

1

0
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0
5
0

0

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0

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0

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0
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10
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9
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3
2

0
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0
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3
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5
1
2

0
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0
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5
1
2
0.
0
0
1
1
0

2
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0
0
0.
0
0
0
0
0
1
1
0

0
.
0
0
0
5
1
3
NS
V
--
5%
Un
c
e
r
t
a
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n
To
w
n
s
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n
d
'
s

G
r
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u
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d

S
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C
h
r
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m
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0
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3
2
5

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0
5
0

1

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5
0

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0

0

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0
0
10
0

0
.
0
4
0
0

2
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2
1
0.
1
1
0

0
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1
1
0
55
.
3

2
.
0
0
0.
0
5
5
2

0
.
1
6
6
3.
3

0
.
0
5
1

1
0
0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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l

C
o
b
a
l
t

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

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0

0

0

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0
0
10
0

0
.
0
5
4
0

0
.
2
6
5
0.
0
1
3
2

0
.
0
1
3
2
4.
9
0

2
.
0
0
0.
0
0
4
9
0

0
.
0
1
8
1
1.
1

0
.
0
1
6

7
9
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
r
e
l

C
o
p
p
e
r

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

9
2
.
7
4.
6
3

4
.
6
3
18
0
0
0

2
.
0
0
18

2
2
.
6
11
.
7
1.
9
85
%
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
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l

I
r
o
n

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

1
5
0
7.
4
9

7
.
4
9
15
0
0
0

2
.
0
0
15

2
2
.
5
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

L
e
a
d

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
1
2
5.
6
0

5
.
6
0
48
0
0
0

2
.
0
0
48

5
3
.
5
0.
9
58
83
%
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

M
a
g
n
e
s
i
u
m

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

2
.
0
6

5
0
1
0
0
25
0
0

2
5
0
0
24
3
0
0

2
.
0
0
24
.
3

2
5
2
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l

M
a
n
g
a
n
e
s
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

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0

0

0

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0
0
10
0

0
.
6
8
0

3
5
3
17
.
6

1
7
.
6
51
9

2
.
0
0
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5
1
8

1
8
.
1
88
.
0

0
.
2
1

1
0
0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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l

M
e
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u
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0
.
3
2
5

0
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0
5
0

1

0
.
0
5
0

0

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0

0

0

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0
0
10
0

R
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g
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s
s
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n

B
a
s
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d

0
.
0
8
6
9
0.
0
0
4
3
4

0
.
0
0
4
3
4
0.
0
7
0
0

2
.
0
0
0.
0
0
0
0
6
9
9

0
.
0
0
4
4
1
0.
0

0
.
1
4

2
7
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l

M
o
l
y
b
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m

0
.
3
2
5

0
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0
5
0

1

0
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0
5
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0

0

0

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0
0
10
0

0
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4
0
0

6
.
8
0
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3
4
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0
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3
4
0
17

2
.
0
0
0.
0
1
7
0

0
.
3
5
7
0.
3
1.
4
91
%
Re
t
a
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n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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N
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k
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l

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

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0

0

0

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0
0
10
0

R
e
g
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s
s
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o
n

B
a
s
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d

1
.
7
5
0.
0
8
7
4

0
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0
8
7
4
41
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3

2
.
0
0
0.
0
4
1
3

0
.
1
2
9
40
.
0

<
0
.
0
1

1
0
0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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l

N
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t
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t
e

0
.
3
2
5

0
.
0
5
0

1

0
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0
5
0

0

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0

0

0

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0
0
10
0

1
.
0
0

2
2
.
8
1.
1
4

1
.
1
4
22
.
8

2
.
0
0
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0
2
2
8

1
.
1
6
50
7
.
0

<
0
.
0
1

9
2
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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l

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h
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0
.
3
2
5

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0
5
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1

0
.
0
5
0

0

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0

0

0

-

0
0
10
0

2
8
2

1
2
7
0
63
.
4

6
3
.
4
4.
5
0

2
.
0
0
0.
0
0
4
5
0

6
3
.
4
2.
6
24
50
%
Re
t
a
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n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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P
h
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s
p
h
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0
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3
2
5

0
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0
5
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5
0

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0

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0
0
10
0

1
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0
0

9
9
0
49
.
5

4
9
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5
99
0

2
.
0
0
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9
8
9

5
0
.
4
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
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d

S
q
u
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l
Se
l
e
n
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m
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
1
5
0

0
.
1
5
0
5.
0
0

2
.
0
0
0.
0
0
5
0
0

0
.
1
5
5
0.
2

0
.
7
7

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
r
e
l

S
i
l
v
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r

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
.
0
0

4
.
0
0
0.
2
0
0

0
.
2
0
0
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0
0

2
.
0
0
0.
0
0
4
0
0

0
.
2
0
4
2.
4

0
.
0
8
6

8
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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l

S
t
r
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n
t
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m

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
.
1
0

5
3
2
26
.
6

2
6
.
6
48
4

2
.
0
0
0.
4
8
4

2
7
.
1
26
3
.
0

0
.
1
0

1
0
0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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l

T
h
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m

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

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0
0
10
0

0
.
0
0
4
0
0

0
.
0
0
2
2
0
0.
0
0
0
1
1
0

0
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0
0
0
1
1
0
0.
5
5
0

2
.
0
0
0.
0
0
0
5
4
9

0
.
0
0
0
6
5
9
0.
0

0
.
0
8
9

5
4
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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l

V
a
n
a
d
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m

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
5
0

0
.
1
4
1
0.
0
0
7
0
6

0
.
0
0
7
0
6
25
.
7

2
.
0
0
0.
0
2
5
7

0
.
0
3
2
7
0.
2

0
.
1
6

1
0
0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
r
e
l

Z
i
n
c

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
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d

3
5
5
17
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17
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23
0
0

2
.
0
0
2.
3
0

2
0
16
0
.
0

0
.
1
3

1
0
0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

I
n
o
r
g
a
n
i
c
s
13
0
(d
e
t
s
)
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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e
l

2
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M
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t
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l
n
a
p
h
t
h
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l
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
.
8
7

3
1
8
15
.
9

1
5
.
9
17
0

2
.
0
0
0.
1
7
0

1
6
5.
0
3.
2
14
%
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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e
l

A
c
e
n
a
p
h
t
h
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
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s
s
i
o
n

B
a
s
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d

1
7
.
2
0.
8
6
1

0
.
8
6
1
0.
0
4
1
8

2
.
0
0
0.
0
0
0
0
4
1
8

0
.
8
6
1
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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l
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p
h
t
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l
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n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
0
.
2
1.
0
1

1
.
0
1
10
.
5

2
.
0
0
0.
0
1
0
5

1
.
0
2
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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e
l

A
n
t
h
r
a
c
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
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o
n

B
a
s
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d

7
.
4
4
0.
3
7
2

0
.
3
7
2
3.
7
0

2
.
0
0
0.
0
0
3
7
0

0
.
3
7
5
10
0
0
.
0

<
0
.
0
1

7
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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e
l
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n
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o
(
a
)
a
n
t
h
r
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c
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
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s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
4
1
0

0
.
4
1
0
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
4
2
1
1.
0

0
.
4
2

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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e
l
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n
z
o
(
a
)
p
y
r
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
.
5
0.
5
2
6

0
.
5
2
6
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
5
3
6
1.
0

0
.
5
4

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
3
1
0

3
.
2
6
0.
1
6
3

0
.
1
6
3
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
1
7
3
1.
0

0
.
1
7

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
2.
0
5

2
.
0
5
10
.
5

2
.
0
0
0.
0
1
0
5

2
.
0
6
1.
0
2.
1
0%
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
8
4
0.
4
4
1

0
.
4
4
1
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
4
5
2
1.
0

0
.
4
5

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Ch
r
y
s
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
4
1
0

0
.
4
1
0
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
4
2
1
1.
0

0
.
4
2

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
1
3
0

1
.
3
6
0.
0
6
8
2

0
.
0
6
8
2
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
0
7
8
7
1.
0

0
.
0
7
9

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

F
l
u
o
r
a
n
t
h
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
3
6
0

0
.
0
0
3
6
0
0.
1
4
4

2
.
0
0
0.
0
0
0
1
4
4

0
.
0
0
3
7
4
12
5
.
0

<
0
.
0
1

4
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

F
l
u
o
r
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
1
9
0
25
9

2
5
9
33

2
.
0
0
0.
0
3
3
0

2
5
9
12
5
.
0
2.
1
14
%
Re
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

3

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
1
1
0

1
.
1
6
0.
0
5
7
7

0
.
0
5
7
7
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
0
6
8
2
1.
0

0
.
0
6
8

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

N
a
p
h
t
h
a
l
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
2
.
2

6
4
7
32
.
3

3
2
.
3
53

2
.
0
0
0.
0
5
2
9

3
2
.
4
50
.
0

0
.
6
5

2
5
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

P
h
e
n
a
n
t
h
r
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
9
.
5
0.
9
7
5

0
.
9
7
5
92

2
.
0
0
0.
0
9
1
9

1
.
0
7
17
5
.
0

<
0
.
0
1

1
8
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Py
r
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
7
2
0

7
.
5
6
0.
3
7
8

0
.
3
7
8
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
3
8
8
75
.
0

<
0
.
0
1

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

P
A
H
s
5.
9
(d
e
t
s
)
Re
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

T
P
H

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

-

0
00
47
0
0
0

2
.
0
0
47

4
7
10
0
0
.
0

0
.
0
4
7

1
0
0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

P
e
t
r
o
l
e
u
m
0.
0
4
7
(d
e
t
s
)
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
2
0
2

1
.
0
1
0.
0
5
0
5

0
.
0
5
0
5
50

2
.
0
0
0.
0
5
0
0

0
.
1
0
0
0.
2

0
.
4
2

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
7

0
.
1
5
4
0.
0
0
7
6
9

0
.
0
0
7
6
9
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
0
1
8
2
0.
2

0
.
0
7
6

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
1
1
8

1
.
2
4
0.
0
6
1
9

0
.
0
6
1
9
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
0
7
2
4
0.
2

0
.
3
0

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
1
4
3

1
.
5
0
0.
0
7
5
1

0
.
0
7
5
1
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
0
8
5
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
.
1
1
6
0.
0
0
5
8
1

0
.
0
0
5
8
1
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
0
1
6
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2-
M
e
t
h
y
l
p
h
e
n
o
l
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

9
.
7
7

1
0
3
5.
1
2

5
.
1
2
10
.
5

2
.
0
0
0.
0
1
0
5

5
.
1
3
34
0
.
0

0
.
0
1
5

0
%
Pa
s
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

2
.
2
8

4
7
.
8
2.
3
9

2
.
3
9
21

2
.
0
0
0.
0
2
1
0

2
.
4
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
7
6
7

0
.
8
0
5
0.
0
4
0
2

0
.
0
4
0
2
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
0
5
0
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
4-
C
h
l
o
r
o
a
n
i
l
i
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
.
1
8

1
2
.
4
0.
6
1
8

0
.
6
1
8
10
.
5

2
.
0
0
0.
0
1
0
5

0
.
6
2
9
NS
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--
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0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
6
0
7

1
.
2
1
0.
0
8
6
7

0
.
0
8
6
7
2.
0
0

6
.
3
0
0.
0
0
9
0
0

0
.
0
9
5
8
2.
0

0
.
0
4
8

2
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
1

1
1
6
8.
2
5

8
.
2
5
10
.
5

6
.
3
0
0.
0
4
7
3

8
.
3
0
2.
0
4.
2
0%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
.
7
2
0.
1
9
4

0
.
1
9
4
1.
5
0

6
.
3
0
0.
0
0
6
7
5

0
.
2
0
1
9.
0

0
.
0
2
2

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2-
N
i
t
r
o
a
n
i
l
i
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
0
.
7

5
3
6
38
.
3

3
8
.
3
50

6
.
3
0
0.
2
2
5

3
8
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2-
N
i
t
r
o
p
h
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
1
.
3

1
1
9
8.
5
1

8
.
5
1
10
.
5

6
.
3
0
0.
0
4
7
3

8
.
5
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2-
N
i
t
r
o
t
o
l
u
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
4
2
8

0
.
0
5
9
9
0.
0
0
4
2
8

0
.
0
0
4
2
8
0.
1
4
0

6
.
3
0
0.
0
0
0
6
3
0

0
.
0
0
4
9
1
2.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
3-
N
i
t
r
o
a
n
i
l
i
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
6
.
8

8
4
0
60

6
0
50

6
.
3
0
0.
2
2
5

6
0
.
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
3-
N
i
t
r
o
t
o
l
u
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

6
.
1
2

0
.
9
1
9
0.
0
6
5
6

0
.
0
6
5
6
0.
1
5
0

6
.
3
0
0.
0
0
0
6
7
5

0
.
0
6
6
3
2.
0

0
.
0
3
3

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
1
8
2

9
.
0
8
0.
6
4
9

0
.
6
4
9
50

6
.
3
0
0.
2
2
5

0
.
8
7
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4-
N
i
t
r
o
a
n
i
l
i
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
0
4

1
5
2
10
.
9

1
0
.
9
50

6
.
3
0
0.
2
2
5

1
1
.
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4-
N
i
t
r
o
p
h
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
9
9
2

4
9
.
6
3.
5
5

3
.
5
5
50

6
.
3
0
0.
2
2
5

3
.
7
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4-
N
i
t
r
o
t
o
l
u
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

6
.
6
6

1
.
2
7
0.
0
9
0
4

0
.
0
9
0
4
0.
1
9
0

6
.
3
0
0.
0
0
0
8
5
5

0
.
0
9
1
3
2.
0

0
.
0
4
6

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

H
M
X

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
7
6.
2
7

6
.
2
7
25

6
.
3
0
0.
1
1
3

6
.
3
8
1.
0
6.
4
31
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ni
t
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
1
3

1
1
.
9
0.
8
4
7

0
.
8
4
7
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
8
9
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ni
t
r
o
g
l
y
c
e
r
i
n
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
4
.
7

5
.
0
1
0.
3
5
8

0
.
3
5
8
0.
3
4
0

6
.
3
0
0.
0
0
1
5
3

0
.
3
6
0
3.
0

0
.
1
2

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

N
i
t
r
o
g
u
a
n
i
d
i
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
3
9

4
1
.
6
2.
9
7

2
.
9
7
0.
3
0
0

6
.
3
0
0.
0
0
1
3
5

2
.
9
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
PE
T
N
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

6
.
5
4

3
.
2
7
0.
2
3
4

0
.
2
3
4
0.
5
0
0

6
.
3
0
0.
0
0
2
2
5

0
.
2
3
6
17
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

P
i
c
r
i
c

a
c
i
d

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
7
.
4

8
.
7
2
0.
6
2
3

0
.
6
2
3
0.
5
0
0

6
.
3
0
0.
0
0
2
2
5

0
.
6
2
5
NS
V
--
7%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
RD
X
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
2.
6
9

2
.
6
9
1.
5
0

6
.
3
0
0.
0
0
6
7
5

2
.
6
9
2.
0
1.
3
0%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Te
t
r
y
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
7
8

0
.
4
0
8
0.
0
2
9
2

0
.
0
2
9
2
0.
2
3
0

6
.
3
0
0.
0
0
1
0
4

0
.
0
3
0
2
1.
3

0
.
0
2
3

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

E
n
e
r
g
e
t
i
c
s
6.
4
(d
e
t
s
)
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
l
u
m
i
n
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
4
0
0

2
1
6
15
.
4

1
5
.
4
54
0
0
0

6
.
3
0
24
3

2
5
9
1.
9
13
0
10
0
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
n
t
i
m
o
n
y

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
5
0
0

8
.
3
5
0.
5
9
6

0
.
5
9
6
16
7

6
.
3
0
0.
7
5
1

1
.
3
5
0.
1
23
79
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
r
s
e
n
i
c

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
1
1
0.
0
7
9
5

0
.
0
7
9
5
41
.
3

6
.
3
0
0.
1
8
6

0
.
2
6
5
0.
4

0
.
6
7

5
8
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

B
a
r
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
1
0
0

6
4
4.
5
7

4
.
5
7
64
0

6
.
3
0
2.
8
8

7
.
4
5
45
.
0

0
.
1
7

1
0
0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

B
e
r
y
l
l
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

0
.
0
0
7
2
0
0.
0
0
0
5
1
4

0
.
0
0
0
5
1
4
0.
7
2
0

6
.
3
0
0.
0
0
3
2
4

0
.
0
0
3
7
6
0.
5

<
0
.
0
1

4
8
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

C
a
d
m
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
.
1
2
0.
2
9
5

0
.
2
9
5
32

6
.
3
0
0.
1
4
4

0
.
4
3
9
0.
8

0
.
5
7

4
4
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

9
.
3
2

0
.
0
1
0
3
0.
0
0
0
7
3
3

0
.
0
0
0
7
3
3
0.
0
0
1
1
0

6
.
3
0
0.
0
0
0
0
0
4
9
5

0
.
0
0
0
7
3
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

C
h
r
o
m
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
4
0
0

2
.
2
1
0.
1
5
8

0
.
1
5
8
55
.
3

6
.
3
0
0.
2
4
9

0
.
4
0
7
3.
3

0
.
1
2

1
0
0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

C
o
b
a
l
t

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
5
4
0

0
.
2
6
5
0.
0
1
8
9

0
.
0
1
8
9
4.
9
0

6
.
3
0
0.
0
2
2
1

0
.
0
4
1
0
1.
1

0
.
0
3
6

7
9
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

C
o
p
p
e
r

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

9
2
.
7
6.
6
2

6
.
6
2
18
0
0
0

6
.
3
0
81

8
7
.
7
11
.
7
7.
5
85
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

I
r
o
n

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

1
5
0
10
.
7

1
0
.
7
15
0
0
0

6
.
3
0
67
.
5

7
8
.
2
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

L
e
a
d

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
1
2
8.
0
1

8
.
0
1
48
0
0
0

6
.
3
0
21
6

2
2
4
0.
9
24
0
83
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

M
a
g
n
e
s
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
0
6

5
0
1
0
0
35
8
0

3
5
8
0
24
3
0
0

6
.
3
0
10
9

3
6
9
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

M
a
n
g
a
n
e
s
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
6
8
0

3
5
3
25
.
2

2
5
.
2
51
9

6
.
3
0
2.
3
4

2
7
.
6
88
.
0

0
.
3
1

1
0
0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

M
e
r
c
u
r
y

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
0
8
6
9
0.
0
0
6
2
1

0
.
0
0
6
2
1
0.
0
7
0
0

6
.
3
0
0.
0
0
0
3
1
5

0
.
0
0
6
5
3
0.
0

0
.
2
0

2
7
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

M
o
l
y
b
d
e
n
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

6
.
8
0
0.
4
8
6

0
.
4
8
6
17

6
.
3
0
0.
0
7
6
5

0
.
5
6
2
0.
3
2.
2
91
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

N
i
c
k
e
l

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
7
5
0.
1
2
5

0
.
1
2
5
41
.
3

6
.
3
0
0.
1
8
6

0
.
3
1
1
40
.
0

<
0
.
0
1

1
0
0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

N
i
t
r
a
t
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
0
0

2
2
.
8
1.
6
3

1
.
6
3
22
.
8

6
.
3
0
0.
1
0
3

1
.
7
3
50
7
.
0

<
0
.
0
1

9
2
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

P
e
r
c
h
l
o
r
a
t
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
8
2

1
2
7
0
90
.
7

9
0
.
7
4.
5
0

6
.
3
0
0.
0
2
0
3

9
0
.
7
2.
6
35
50
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

P
h
o
s
p
h
o
r
u
s

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
0
0

9
9
0
70
.
7

7
0
.
7
99
0

6
.
3
0
4.
4
6

7
5
.
2
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Se
l
e
n
i
u
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
2
1
4

0
.
2
1
4
5.
0
0

6
.
3
0
0.
0
2
2
5

0
.
2
3
7
0.
2
1.
2
0%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

S
i
l
v
e
r

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
0
0

4
.
0
0
0.
2
8
6

0
.
2
8
6
4.
0
0

6
.
3
0
0.
0
1
8
0

0
.
3
0
4
2.
4

0
.
1
3

8
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

S
t
r
o
n
t
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
1
0

5
3
2
38

3
8
48
4

6
.
3
0
2.
1
8

4
0
.
2
26
3
.
0

0
.
1
5

1
0
0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

T
h
a
l
l
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
4
0
0

0
.
0
0
2
2
0
0.
0
0
0
1
5
7

0
.
0
0
0
1
5
7
0.
5
5
0

6
.
3
0
0.
0
0
2
4
8

0
.
0
0
2
6
3
0.
0

0
.
3
6

5
4
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

V
a
n
a
d
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
5
0

0
.
1
4
1
0.
0
1
0
1

0
.
0
1
0
1
25
.
7

6
.
3
0
0.
1
1
6

0
.
1
2
6
0.
2

0
.
6
0

1
0
0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

Z
i
n
c

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
5
5
25
.3
25
.3
23
0
0

6
.
3
0
10
.
4

3
5
.
7
16
0
.
0

0
.
2
2

1
0
0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

I
n
o
r
g
a
n
i
c
s
45
0
(d
e
t
s
)
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
8
7

3
1
8
22
.
7

2
2
.
7
17
0

6
.
3
0
0.
7
6
5

2
3
.
5
5.
0
4.
7
14
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
c
e
n
a
p
h
t
h
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
7
.
2
1.
2
3

1
.
2
3
0.
0
4
1
8

6
.
3
0
0.
0
0
0
1
8
8

1
.
2
3
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ac
e
n
a
p
h
t
h
y
l
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
0
.
2
1.
4
4

1
.
4
4
10
.
5

6
.
3
0
0.
0
4
7
3

1
.
4
9
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
n
t
h
r
a
c
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
5
3
2

0
.
5
3
2
3.
7
0

6
.
3
0
0.
0
1
6
7

0
.
5
4
8
10
0
0
.
0

<
0
.
0
1

7
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

5

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
5
8
7

0
.
5
8
7
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
6
3
4
1.
0

0
.
6
3

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Be
n
z
o
(
a
)
p
y
r
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
.
5
0.
7
5
2

0
.
7
5
2
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
8
0
0
1.
0

0
.
8
0

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
1
0

3
.
2
6
0.
2
3
3

0
.
2
3
3
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
2
8
0
1.
0

0
.
2
8

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
2.
9
3

2
.
9
3
10
.
5

6
.
3
0
0.
0
4
7
3

2
.
9
7
1.
0
3.
0
0%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
8
4
0.
6
3
1

0
.
6
3
1
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
6
7
9
1.
0

0
.
6
8

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
r
y
s
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
5
8
7

0
.
5
8
7
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
6
3
4
1.
0

0
.
6
3

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
1
3
0

1
.
3
6
0.
0
9
7
5

0
.
0
9
7
5
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
1
4
5
1.
0

0
.
1
4

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

F
l
u
o
r
a
n
t
h
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
5
1
4

0
.
0
0
5
1
4
0.
1
4
4

6
.
3
0
0.
0
0
0
6
4
8

0
.
0
0
5
7
9
12
5
.
0

<
0
.
0
1

4
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

F
l
u
o
r
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
1
9
0
37
1

3
7
1
33

6
.
3
0
0.
1
4
9

3
7
1
12
5
.
0
3.
0
14
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
1
1
0

1
.
1
6
0.
0
8
2
5

0
.
0
8
2
5
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
1
3
0
1.
0

0
.
1
3

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

N
a
p
h
t
h
a
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
2
.
2

6
4
7
46
.
2

4
6
.
2
53

6
.
3
0
0.
2
3
9

4
6
.
4
50
.
0

0
.
9
3

2
5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

P
h
e
n
a
n
t
h
r
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
9
.
5
1.
3
9

1
.
3
9
92

6
.
3
0
0.
4
1
4

1
.
8
1
17
5
.
0

0
.
0
1
0

1
8
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Py
r
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
7
2
0

7
.
5
6
0.
5
4
0

0
.
5
4
0
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
5
8
7
75
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

P
A
H
s
8.
6
(d
e
t
s
)
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

T
P
H

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

-

0
00
47
0
0
0

6
.
3
0
21
2

2
1
2
10
0
0
.
0

0
.
2
1

1
0
0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

P
e
t
r
o
l
e
u
m
0.
2
1
(d
e
t
s
)
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
2
0
2

1
.
0
1
0.
0
7
2
2

0
.
0
7
2
2
50

6
.
3
0
0.
2
2
5

0
.
2
9
7
0.
2
1.
2
0%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
7

0
.
1
5
4
0.
0
1
1
0

0
.
0
1
1
0
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
0
5
8
3
0.
2

0
.
2
4

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
1
1
8

1
.
2
4
0.
0
8
8
6

0
.
0
8
8
6
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
1
3
6
0.
2

0
.
5
7

0
%
Pa
s
s
Bl
a
c
k
-
t
a
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d

J
a
c
k
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a
b
b
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4
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D
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2.
1
0
0

0
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0
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1

0
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0
7
1

0

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0

0

0

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0
0
10
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0
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1
4
3

1
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5
0
0.
1
0
7

0
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1
0
7
10
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5

6
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3
0
0.
0
4
7
3

0
.
1
5
5
NS
V
--
0%
Un
c
e
r
t
a
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n
Bl
a
c
k
-
t
a
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l
e
d

J
a
c
k
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a
b
b
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C
h
l
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n
a
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

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0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
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1
1
6
0.
0
0
8
3
1

0
.
0
0
8
3
1
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
0
5
5
6
NS
V
--
0%
Un
c
e
r
t
a
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n
Bl
a
c
k
-
t
a
i
l
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d

J
a
c
k
r
a
b
b
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M
e
t
h
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p
h
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n
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l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

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0
0
10
0

9
.
7
7

1
0
3
7.
3
3

7
.
3
3
10
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5

6
.
3
0
0.
0
4
7
3

7
.
3
8
34
0
.
0

0
.
0
2
2

0
%
Pa
s
s
Bl
a
c
k
-
t
a
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l
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d

J
a
c
k
r
a
b
b
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t
3,
3
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D
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c
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b
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2.
1
0
0

0
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0
7
1

1

0
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0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
2
8

4
7
.
8
3.
4
1

3
.
4
1
21

6
.
3
0
0.
0
9
4
5

3
.
5
1
NS
V
--
0%
Un
c
e
r
t
a
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n
Bl
a
c
k
-
t
a
i
l
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d

J
a
c
k
r
a
b
b
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t
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C
h
l
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3
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m
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t
h
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p
h
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n
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l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
7
6
7

0
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8
0
5
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0
5
7
5

0
.
0
5
7
5
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
1
0
5
NS
V
--
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Un
c
e
r
t
a
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n
Bl
a
c
k
-
t
a
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l
e
d

J
a
c
k
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a
b
b
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C
h
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n
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2.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

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0

0

0

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0
0
10
0

1
.
1
8

1
2
.
4
0.
8
8
5

0
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8
8
5
10
.
5

6
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3
0
0.
0
4
7
3

0
.
9
3
2
NS
V
--
0%
Un
c
e
r
t
a
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n
Bl
a
c
k
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t
a
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l
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d

J
a
c
k
r
a
b
b
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t
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M
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t
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p
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2.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

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0
0
10
0

0
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9
5
1

9
.
9
8
0.
7
1
3

0
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7
1
3
10
.
5

6
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3
0
0.
0
4
7
3

0
.
7
6
1
34
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
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l
e
d

J
a
c
k
r
a
b
b
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Be
n
z
o
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c

a
c
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d
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

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0
0
10
0

1
.
0
8

5
4
.
1
3.
8
7

3
.
8
7
50

6
.
3
0
0.
2
2
5

4
.
0
9
NS
V
--
0%
Un
c
e
r
t
a
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n
Bl
a
c
k
-
t
a
i
l
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d

J
a
c
k
r
a
b
b
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t
Be
n
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y
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a
l
c
o
h
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2.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

5
.
6
7

5
9
.
5
4.
2
5

4
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2
5
10
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5

6
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3
0
0.
0
4
7
3

4
.
3
0
NS
V
--
0%
Un
c
e
r
t
a
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n
Bl
a
c
k
-
t
a
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l
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d

J
a
c
k
r
a
b
b
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t

b
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s
(
2
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t
h
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)
p
h
t
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a
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a
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2
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1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

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0
0
10
0

0
.
0
6
6
0

0
.
0
9
9
0
0.
0
0
7
0
7

0
.
0
0
7
0
7
1.
5
0

6
.
3
0
0.
0
0
6
7
5

0
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0
1
3
8
18
.
3

<
0
.
0
1

1
8
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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Bu
t
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l

b
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y
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h
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h
a
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a
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
1
8
2

0
.
0
1
9
1
0.
0
0
1
3
6

0
.
0
0
1
3
6
10
.
5

6
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3
0
0.
0
4
7
3

0
.
0
4
8
6
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t

D
i
b
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n
z
o
f
u
r
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n

2
.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
8
9

2
2
.
6
1.
6
2

1
.
6
2
12

6
.
3
0
0.
0
5
4
0

1
.
6
7
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
Di
e
t
h
y
l
p
h
t
h
a
l
a
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
0
4

3
.
2
0
0.
2
2
8

0
.
2
2
8
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
2
7
6
45
8
3
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
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l
e
d

J
a
c
k
r
a
b
b
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m
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a
l
a
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2.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

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0
0
10
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2
.
1
1

2
2
.
1
1.
5
8

1
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5
8
10
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5

6
.
3
0
0.
0
4
7
3

1
.
6
3
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
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l
e
d

J
a
c
k
r
a
b
b
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n
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b
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2.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

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0
0
10
0

0
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0
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9
8

0
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0
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1
3
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0
0
2
2
4

0
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0
0
2
2
4
10
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5

6
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3
0
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0
4
7
3

0
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0
4
9
5
55
0
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0

<
0
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0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
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l
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d

J
a
c
k
r
a
b
b
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2.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
4
6
1

4
.
8
4
0.
3
4
6

0
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3
4
6
10
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5

6
.
3
0
0.
0
4
7
3

0
.
3
9
3
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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x
a
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b
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2.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
0
7
8
5

0
.
0
0
8
2
4
0.
0
0
0
5
8
9

0
.
0
0
0
5
8
9
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
0
4
7
9
1.
6

0
.
0
3
0

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
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x
a
c
h
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b
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d
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
2
0
7

#
#
#
#
#
#
#
#
#
0.
0
0
0
0
0
0
1
1
8

0
.
0
0
0
0
0
0
1
1
8
0.
0
0
0
8
0
0

6
.
3
0
0.
0
0
0
0
0
3
6
0

0
.
0
0
0
0
0
3
7
2
1.
6

<
0
.
0
1

4
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
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x
a
c
h
l
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c
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c
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p
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

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0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
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1
1
6
0.
0
0
8
3
1

0
.
0
0
8
3
1
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
0
5
5
6
1.
6

0
.
0
3
5

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
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x
a
c
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l
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h
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
3
0
5

0
.
0
3
2
0
0.
0
0
2
2
9

0
.
0
0
2
2
9
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
0
4
9
6
1.
6

0
.
0
3
1

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
Is
o
p
h
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r
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n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
4
6
7

4
.
9
1
0.
3
5
1

0
.
3
5
1
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
3
9
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
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a
b
b
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t
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N
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t
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p
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m
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2.
1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
4
5

2
5
.
7
1.
8
4

1
.
8
4
10
.
5

6
.
3
0
0.
0
4
7
3

1
.
8
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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N
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
7
1
9

0
.
7
5
5
0.
0
5
4
0

0
.
0
5
4
0
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
1
0
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
Pe
n
t
a
c
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l
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p
h
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n
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l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
1
2
9

0
.
0
6
4
4
0.
0
0
4
6
0

0
.
0
0
4
6
0
50

6
.
3
0
0.
2
2
5

0
.
2
3
0
0.
2

0
.
9
6

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

S
V
O
C
s
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.
0
1

(
d
e
t
s
)
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
1
,
1
,
2
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e
t
r
a
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h
a
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1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
2
1
4
0.
0
0
0
1
5
3

0
.
0
0
0
1
5
3
0.
0
0
0
6
0
0

6
.
3
0
0.
0
0
0
0
0
2
7
0

0
.
0
0
0
1
5
5
1.
4

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
1
,
1
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T
r
i
c
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t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
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2
7
9

0
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0
0
0
2
5
1
0.
0
0
0
0
1
8
0

0
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0
0
0
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1
8
0
0.
0
0
0
9
0
0

6
.
3
0
0.
0
0
0
0
0
4
0
5

0
.
0
0
0
0
2
2
0
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
1
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2
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2
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l
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r
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h
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1
0
0

0
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0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
3
5
4
0.
0
0
0
0
2
5
3

0
.
0
0
0
0
2
5
3
0.
0
0
1
0
0

6
.
3
0
0.
0
0
0
0
0
4
5
0

0
.
0
0
0
0
2
9
8
1.
4

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
1
,
2
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r
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l
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r
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h
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1
0
0

0
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0
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1

1

0
.
0
7
1

0

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0

0

0

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0
0
10
0

0
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2
9
8

0
.
0
0
0
2
3
8
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0
0
0
0
1
7
0

0
.
0
0
0
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1
7
0
0.
0
0
0
8
0
0

6
.
3
0
0.
0
0
0
0
0
3
6
0

0
.
0
0
0
0
2
0
6
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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1
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D
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h
l
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t
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1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
8
9
9
0.
0
0
0
0
6
4
2

0
.
0
0
0
0
6
4
2
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
6
7
4
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
1
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D
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c
h
l
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r
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e
t
h
e
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
9
0
8
0.
0
0
0
6
4
9

0
.
0
0
0
6
4
9
0.
0
0
1
1
0

6
.
3
0
0.
0
0
0
0
0
4
9
5

0
.
0
0
0
6
5
4
2.
5

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
2
,
3
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T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
3
7

0
.
0
0
3
8
5
0.
0
0
0
2
7
5

0
.
0
0
0
2
7
5
0.
0
0
2
8
0

6
.
3
0
0.
0
0
0
0
1
2
6

0
.
0
0
0
2
8
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
,
3
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T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
5
2
6
0.
0
0
0
3
7
6

0
.
0
0
0
3
7
6
0.
0
0
0
9
0
0

6
.
3
0
0.
0
0
0
0
0
4
0
5

0
.
0
0
0
3
8
0
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
8
0

0
.
0
0
0
0
1
8
5
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
0
0
1
3
3
0.
0
0
3
2
0

6
.
3
0
0.
0
0
0
0
1
4
4

0
.
0
0
0
0
1
5
7
NS
V
--
4%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
2
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D
i
b
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m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
4
3
8

0
.
0
0
1
7
1
0.
0
0
0
1
2
2

0
.
0
0
0
1
2
2
0.
0
0
3
9
0

6
.
3
0
0.
0
0
0
0
1
7
6

0
.
0
0
0
1
4
0
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
2
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D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
5
7

0
.
0
0
3
6
0
0.
0
0
0
2
5
7

0
.
0
0
0
2
5
7
0.
0
0
1
4
0

6
.
3
0
0.
0
0
0
0
0
6
3
0

0
.
0
0
0
2
6
3
NS
V
--
4%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
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D
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
2
0
0
0.
0
0
0
1
4
3

0
.
0
0
0
1
4
3
0.
0
0
0
8
0
0

6
.
3
0
0.
0
0
0
0
0
3
6
0

0
.
0
0
0
1
4
7
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
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D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
5
7
3
0.
0
0
0
0
4
0
9

0
.
0
0
0
0
4
0
9
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
4
4
1
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
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E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
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e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
1
.
7

0
.
0
1
0
5
0.
0
0
0
7
5
0

0
.
0
0
0
7
5
0
0.
0
0
0
9
0
0

6
.
3
0
0.
0
0
0
0
0
4
0
5

0
.
0
0
0
7
5
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
4
9
8
0.
0
0
0
0
0
3
5
6

0
.
0
0
0
0
0
3
5
6
0.
0
0
1
9
0

6
.
3
0
0.
0
0
0
0
0
8
5
5

0
.
0
0
0
0
1
2
1
NS
V
--
4%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
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t
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
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n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
8
1
2
0.
0
0
0
0
0
5
8
0

0
.
0
0
0
0
0
5
8
0
0.
0
0
3
1
0

6
.
3
0
0.
0
0
0
0
1
4
0

0
.
0
0
0
0
1
9
8
NS
V
--
4%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

2
-
B
u
t
a
n
o
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
7
3
2
0.
0
5
2
3

0
.
0
5
2
3
0.
0
1
5
9

6
.
3
0
0.
0
0
0
0
7
1
6

0
.
0
5
2
4
10
.
0

<
0
.
0
1

1
8
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2-
C
h
l
o
r
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e
t
h
y
l
V
i
n
y
l
E
t
h
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r
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
0
.
2

0
.
1
2
0
0.
0
0
8
6
1

0
.
0
0
8
6
1
0.
0
0
5
9
5

6
.
3
0
0.
0
0
0
0
2
6
8

0
.
0
0
8
6
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2-
C
h
l
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r
o
p
h
e
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o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
5
5
7

5
.
8
4
0.
4
1
8

0
.
4
1
8
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
4
6
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
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a
b
b
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t
2-
H
e
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a
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2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

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0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
6
3
2
0.
0
0
4
5
2

0
.
0
0
4
5
2
0.
0
0
3
8
0

6
.
3
0
0.
0
0
0
0
1
7
1

0
.
0
0
4
5
4
10
.
0

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0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
5
6
6

5
.
9
4
0.
4
2
4

0
.
4
2
4
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
4
7
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
0
9
3
4

0
.
0
9
8
1
0.
0
0
7
0
1

0
.
0
0
7
0
1
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
0
5
4
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
8
5
4
0.
0
0
6
1
1

0
.
0
0
6
1
1
0.
0
0
4
3
0

6
.
3
0
0.
0
0
0
0
1
9
4

0
.
0
0
6
1
2
25
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
c
e
t
o
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

7
5
.
6

1
8
1
0
13
0

1
3
0
24

6
.
3
0
0.
1
0
8

1
3
0
10
.
0
13
32
%
Re
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

B
e
n
z
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
3
3
9
0.
0
0
2
4
2

0
.
0
0
2
4
2
0.
0
0
4
1
0

6
.
3
0
0.
0
0
0
0
1
8
5

0
.
0
0
2
4
4
0.
7

<
0
.
0
1

1
4
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
7
.
9

1
.
3
3
0.
0
9
4
8

0
.
0
9
4
8
0.
0
7
4
0

6
.
3
0
0.
0
0
0
3
3
3

0
.
0
9
5
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
4
0

2
5
.
2
1.
8
0

1
.
8
0
10
.
5

6
.
3
0
0.
0
4
7
3

1
.
8
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
6
5
9

6
.
9
2
0.
4
9
4

0
.
4
9
4
10
.
5

6
.
3
0
0.
0
4
7
3

0
.
5
4
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

8
.
4
9

0
.
0
0
5
9
4
0.
0
0
0
4
2
5

0
.
0
0
0
4
2
5
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
4
2
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Br
o
m
o
f
o
r
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
4
6

0
.
0
0
0
1
7
3
0.
0
0
0
0
1
2
4

0
.
0
0
0
0
1
2
4
0.
0
0
0
5
0
0

6
.
3
0
0.
0
0
0
0
0
2
2
5

0
.
0
0
0
0
1
4
6
15
.
0

<
0
.
0
1

5
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

6

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Br
o
m
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
2
9
8
0.
0
0
2
1
3

0
.
0
0
2
1
3
0.
0
0
1
5
0

6
.
3
0
0.
0
0
0
0
0
6
7
5

0
.
0
0
2
1
4
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
.
2
9

0
.
0
0
3
8
6
0.
0
0
0
2
7
6

0
.
0
0
0
2
7
6
0.
0
0
0
9
0
0

6
.
3
0
0.
0
0
0
0
0
4
0
5

0
.
0
0
0
2
8
0
16
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
9
4
0
0.
0
0
0
0
0
6
7
1

0
.
0
0
0
0
0
6
7
1
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
0
9
8
7
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
7
9
0.
0
0
0
1
9
9

0
.
0
0
0
1
9
9
0.
0
0
1
0
0

6
.
3
0
0.
0
0
0
0
0
4
5
0

0
.
0
0
0
2
0
4
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
f
o
r
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
8
7
3

0
.
0
0
0
6
1
1
0.
0
0
0
0
4
3
6

0
.
0
0
0
0
4
3
6
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
4
6
8
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
5
5
9

0
.
0
0
0
5
5
9
0.
0
0
1
0
0

6
.
3
0
0.
0
0
0
0
0
4
5
0

0
.
0
0
0
5
6
4
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
7
4
4
0.
0
0
0
5
3
2

0
.
0
0
0
5
3
2
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
5
3
5
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
4
2
7
0.
0
0
0
3
0
5

0
.
0
0
0
3
0
5
0.
0
0
0
6
0
0

6
.
3
0
0.
0
0
0
0
0
2
7
0

0
.
0
0
0
3
0
8
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
6
7
4

0
.
0
0
0
4
7
2
0.
0
0
0
0
3
3
7

0
.
0
0
0
0
3
3
7
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
3
6
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Di
b
r
o
m
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
3
.
3

0
.
0
0
6
6
5
0.
0
0
0
4
7
5

0
.
0
0
0
4
7
5
0.
0
0
0
5
0
0

6
.
3
0
0.
0
0
0
0
0
2
2
5

0
.
0
0
0
4
7
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
5
8
0

0
.
0
0
0
6
3
8
0.
0
0
0
0
4
5
6

0
.
0
0
0
0
4
5
6
0.
0
0
1
1
0

6
.
3
0
0.
0
0
0
0
0
4
9
5

0
.
0
0
0
0
5
0
5
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Et
h
y
l
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
8
9
8
0.
0
0
0
0
0
6
4
1

0
.
0
0
0
0
0
6
4
1
0.
0
0
1
3
0

6
.
3
0
0.
0
0
0
0
0
5
8
5

0
.
0
0
0
0
1
2
3
97
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
m,
p
-
X
y
l
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
6
0
8
0.
0
0
0
4
3
4

0
.
0
0
0
4
3
4
0.
0
0
2
0
0

6
.
3
0
0.
0
0
0
0
0
9
0
0

0
.
0
0
0
4
4
3
17
9
.
0

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
.
1
0

0
.
0
1
3
1
0.
0
0
0
9
3
8

0
.
0
0
0
9
3
8
0.
0
0
3
2
0

6
.
3
0
0.
0
0
0
0
1
4
4

0
.
0
0
0
9
5
2
5.
9

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

o
-
X
y
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
3
4

0
.
0
0
9
0
1
0.
0
0
0
6
4
4

0
.
0
0
0
6
4
4
0.
0
0
2
7
0

6
.
3
0
0.
0
0
0
0
1
2
2

0
.
0
0
0
6
5
6
17
9
.
0

<
0
.
0
1

1
4
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ph
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
6
2

2
7
.
5
1.
9
6

1
.
9
6
10
.
5

6
.
3
0
0.
0
4
7
3

2
.
0
1
17
.
1

0
.
1
2

0
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

S
t
y
r
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
.
0
2

0
.
0
1
0
5
0.
0
0
0
7
4
7

0
.
0
0
0
7
4
7
0.
0
0
2
6
0

6
.
3
0
0.
0
0
0
0
1
1
7

0
.
0
0
0
7
5
9
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
9

0
.
0
1
3
3
0.
0
0
0
9
4
9

0
.
0
0
0
9
4
9
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
9
5
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
2
2
7
0.
0
0
0
1
6
2

0
.
0
0
0
1
6
2
0.
0
0
0
9
0
0

6
.
3
0
0.
0
0
0
0
0
4
0
5

0
.
0
0
0
1
6
6
1.
4

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

T
o
l
u
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
8
8
2
0.
0
0
6
3
0

0
.
0
0
6
3
0
0.
0
1
8
7

6
.
3
0
0.
0
0
0
0
8
4
2

0
.
0
0
6
3
8
52
.
0

<
0
.
0
1

2
3
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
1
2
5

0
.
0
0
0
1
2
5
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
1
2
8
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
6
5
4
0.
0
0
0
0
4
6
8

0
.
0
0
0
0
4
6
8
0.
0
0
0
8
0
0

6
.
3
0
0.
0
0
0
0
0
3
6
0

0
.
0
0
0
0
5
0
4
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
3
1

0
.
0
0
0
2
3
2
0.
0
0
0
0
1
6
6

0
.
0
0
0
0
1
6
6
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
1
9
7
0.
7

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
2
6
1

0
.
0
0
0
2
8
8
0.
0
0
0
0
2
0
6

0
.
0
0
0
0
2
0
6
0.
0
0
1
1
0

6
.
3
0
0.
0
0
0
0
0
4
9
5

0
.
0
0
0
0
2
5
5
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Vi
n
y
l

A
c
e
t
a
t
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
2

0
.
0
2
6
4
0.
0
0
1
8
9

0
.
0
0
1
8
9
0.
0
0
1
2
0

6
.
3
0
0.
0
0
0
0
0
5
4
0

0
.
0
0
1
8
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Vi
n
y
l

c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
1
0

0
.
0
0
3
7
2
0.
0
0
0
2
6
6

0
.
0
0
0
2
6
6
0.
0
0
1
2
0

6
.
3
0
0.
0
0
0
0
0
5
4
0

0
.
0
0
0
2
7
1
0.
2

<
0
.
0
1

5
%
Pa
s
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

V
O
C
s
13
(d
e
t
s
)
Re
t
a
i
n
Pr
o
n
g
h
o
r
n
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
7
8

0
.
5
0
2
0.
0
1
7
3

0
.
0
1
7
3
0.
1
0
5

2
.
0
0
0.
0
0
0
0
7
2
2

0
.
0
1
7
3
2.
7

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
5

1
.
2
0
0.
0
4
1
3

0
.
0
4
1
3
0.
0
8
0
0

2
.
0
0
0.
0
0
0
0
5
5
0

0
.
0
4
1
4
0.
0
1.
0
0%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
2
3

6
.
3
4
0.
2
1
8

0
.
2
1
8
1.
5
0

2
.
0
0
0.
0
0
1
0
3

0
.
2
1
9
2.
0

0
.
1
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
4
0

1
2
0
4.
1
3

4
.
1
3
50

2
.
0
0
0.
0
3
4
4

4
.
1
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
6
0
7

1
.
2
1
0.
0
4
1
8

0
.
0
4
1
8
2.
0
0

2
.
0
0
0.
0
0
1
3
8

0
.
0
4
3
1
2.
0

0
.
0
2
2

2
%
Pa
s
s
Pr
o
n
g
h
o
r
n
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
1

1
1
6
3.
9
7

3
.
9
7
10
.
5

2
.
0
0
0.
0
0
7
2
2

3
.
9
8
2.
0
2.
0
0%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
.
7
2
0.
0
9
3
5

0
.
0
9
3
5
1.
5
0

2
.
0
0
0.
0
0
1
0
3

0
.
0
9
4
6
9.
0

0
.
0
1
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
2-
N
i
t
r
o
a
n
i
l
i
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
0
.
7

5
3
6
18
.
4

1
8
.
4
50

2
.
0
0
0.
0
3
4
4

1
8
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
2-
N
i
t
r
o
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
1
.
3

1
1
9
4.
1
0

4
.
1
0
10
.
5

2
.
0
0
0.
0
0
7
2
2

4
.
1
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
2-
N
i
t
r
o
t
o
l
u
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
4
2
8

0
.
0
5
9
9
0.
0
0
2
0
6

0
.
0
0
2
0
6
0.
1
4
0

2
.
0
0
0.
0
0
0
0
9
6
3

0
.
0
0
2
1
6
2.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
3-
N
i
t
r
o
a
n
i
l
i
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
6
.
8

8
4
0
28
.
9

2
8
.
9
50

2
.
0
0
0.
0
3
4
4

2
8
.
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
3-
N
i
t
r
o
t
o
l
u
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

6
.
1
2

0
.
9
1
9
0.
0
3
1
6

0
.
0
3
1
6
0.
1
5
0

2
.
0
0
0.
0
0
0
1
0
3

0
.
0
3
1
7
2.
0

0
.
0
1
6

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
1
8
2

9
.
0
8
0.
3
1
2

0
.
3
1
2
50

2
.
0
0
0.
0
3
4
4

0
.
3
4
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
4-
N
i
t
r
o
a
n
i
l
i
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
0
4

1
5
2
5.
2
3

5
.
2
3
50

2
.
0
0
0.
0
3
4
4

5
.
2
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
4-
N
i
t
r
o
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
9
9
2

4
9
.
6
1.
7
1

1
.
7
1
50

2
.
0
0
0.
0
3
4
4

1
.
7
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
4-
N
i
t
r
o
t
o
l
u
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

6
.
6
6

1
.
2
7
0.
0
4
3
5

0
.
0
4
3
5
0.
1
9
0

2
.
0
0
0.
0
0
0
1
3
1

0
.
0
4
3
7
2.
0

0
.
0
2
2

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

H
M
X

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
7
3.
0
2

3
.
0
2
25

2
.
0
0
0.
0
1
7
2

3
.
0
3
1.
0
3.
0
31
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n
Ni
t
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
1
3

1
1
.
9
0.
4
0
8

0
.
4
0
8
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
4
1
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Ni
t
r
o
g
l
y
c
e
r
i
n
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
4
.
7

5
.
0
1
0.
1
7
2

0
.
1
7
2
0.
3
4
0

2
.
0
0
0.
0
0
0
2
3
4

0
.
1
7
3
3.
0

0
.
0
5
8

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

N
i
t
r
o
g
u
a
n
i
d
i
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
3
9

4
1
.
6
1.
4
3

1
.
4
3
0.
3
0
0

2
.
0
0
0.
0
0
0
2
0
6

1
.
4
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
PE
T
N
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

6
.
5
4

3
.
2
7
0.
1
1
2

0
.
1
1
2
0.
5
0
0

2
.
0
0
0.
0
0
0
3
4
4

0
.
1
1
3
17
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

P
i
c
r
i
c

a
c
i
d

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
7
.
4

8
.
7
2
0.
3
0
0

0
.
3
0
0
0.
5
0
0

2
.
0
0
0.
0
0
0
3
4
4

0
.
3
0
0
NS
V
--
7%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
RD
X
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
1.
2
9

1
.
2
9
1.
5
0

2
.
0
0
0.
0
0
1
0
3

1
.
2
9
2.
0

0
.
6
5

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Te
t
r
y
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
7
8

0
.
4
0
8
0.
0
1
4
0

0
.
0
1
4
0
0.
2
3
0

2
.
0
0
0.
0
0
0
1
5
8

0
.
0
1
4
2
1.
3

0
.
0
1
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
HI

-

E
n
e
r
g
e
t
i
c
s
3.
1
(d
e
t
s
)
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

A
l
u
m
i
n
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
4
0
0

2
1
6
7.
4
3

7
.
4
3
54
0
0
0

2
.
0
0
37
.
1

4
4
.
6
1.
9
23
10
0
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

A
n
t
i
m
o
n
y

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
5
0
0

8
.
3
5
0.
2
8
7

0
.
2
8
7
16
7

2
.
0
0
0.
1
1
5

0
.
4
0
2
0.
1
6.
8
79
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

A
r
s
e
n
i
c

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
1
1
0.
0
3
8
3

0
.
0
3
8
3
41
.
3

2
.
0
0
0.
0
2
8
4

0
.
0
6
6
7
0.
4

0
.
1
7

5
8
%
Pa
s
s
Pr
o
n
g
h
o
r
n

B
a
r
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
1
0
0

6
4
2.
2
0

2
.
2
0
64
0

2
.
0
0
0.
4
4
0

2
.
6
4
45
.
0

0
.
0
5
9

1
0
0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

B
e
r
y
l
l
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

0
.
0
0
7
2
0
0.
0
0
0
2
4
8

0
.
0
0
0
2
4
8
0.
7
2
0

2
.
0
0
0.
0
0
0
4
9
5

0
.
0
0
0
7
4
3
0.
5

<
0
.
0
1

4
8
%
Pa
s
s
Pr
o
n
g
h
o
r
n

C
a
d
m
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
.
1
2
0.
1
4
2

0
.
1
4
2
32

2
.
0
0
0.
0
2
2
0

0
.
1
6
4
0.
8

0
.
2
1

4
4
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

9
.
3
2

0
.
0
1
0
3
0.
0
0
0
3
5
3

0
.
0
0
0
3
5
3
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
7
5
7

0
.
0
0
0
3
5
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

C
h
r
o
m
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
4
0
0

2
.
2
1
0.
0
7
6
1

0
.
0
7
6
1
55
.
3

2
.
0
0
0.
0
3
8
0

0
.
1
1
4
3.
3

0
.
0
3
5

1
0
0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

C
o
b
a
l
t

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
5
4
0

0
.
2
6
5
0.
0
0
9
1
0

0
.
0
0
9
1
0
4.
9
0

2
.
0
0
0.
0
0
3
3
7

0
.
0
1
2
5
1.
1

0
.
0
1
1

7
9
%
Pa
s
s
Pr
o
n
g
h
o
r
n

C
o
p
p
e
r

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

9
2
.
7
3.
1
9

3
.
1
9
18
0
0
0

2
.
0
0
12
.
4

1
5
.
6
11
.
7
1.
3
85
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

I
r
o
n

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

1
5
0
5.
1
6

5
.
1
6
15
0
0
0

2
.
0
0
10
.
3

1
5
.
5
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

L
e
a
d

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
1
2
3.
8
5

3
.
8
5
48
0
0
0

2
.
0
0
33

3
6
.
9
0.
9
40
83
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

M
a
g
n
e
s
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
0
6

5
0
1
0
0
17
2
0

1
7
2
0
24
3
0
0

2
.
0
0
16
.
7

1
7
4
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

M
a
n
g
a
n
e
s
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
6
8
0

3
5
3
12
.
1

1
2
.
1
51
9

2
.
0
0
0.
3
5
7

1
2
.
5
88
.
0

0
.
1
4

1
0
0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

M
e
r
c
u
r
y

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
0
8
6
9
0.
0
0
2
9
9

0
.
0
0
2
9
9
0.
0
7
0
0

2
.
0
0
0.
0
0
0
0
4
8
2

0
.
0
0
3
0
4
0.
0

0
.
0
9
5

2
7
%
Pa
s
s
Pr
o
n
g
h
o
r
n

M
o
l
y
b
d
e
n
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

6
.
8
0
0.
2
3
4

0
.
2
3
4
17

2
.
0
0
0.
0
1
1
7

0
.
2
4
6
0.
3

0
.
9
4

9
1
%
Pa
s
s
Pr
o
n
g
h
o
r
n

N
i
c
k
e
l

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
7
5
0.
0
6
0
2

0
.
0
6
0
2
41
.
3

2
.
0
0
0.
0
2
8
4

0
.
0
8
8
6
40
.
0

<
0
.
0
1

1
0
0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

N
i
t
r
a
t
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
0
0

2
2
.
8
0.
7
8
4

0
.
7
8
4
22
.
8

2
.
0
0
0.
0
1
5
7

0
.
8
0
0
50
7
.
0

<
0
.
0
1

9
2
%
Pa
s
s
Pr
o
n
g
h
o
r
n

P
e
r
c
h
l
o
r
a
t
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
8
2

1
2
7
0
43
.
6

4
3
.
6
4.
5
0

2
.
0
0
0.
0
0
3
1
0

4
3
.
6
2.
6
17
50
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

P
h
o
s
p
h
o
r
u
s

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
0
0

9
9
0
34

3
4
99
0

2
.
0
0
0.
6
8
1

3
4
.
7
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Se
l
e
n
i
u
m
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
1
0
3

0
.
1
0
3
5.
0
0

2
.
0
0
0.
0
0
3
4
4

0
.
1
0
7
0.
2

0
.
5
3

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

S
i
l
v
e
r

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
0
0

4
.
0
0
0.
1
3
8

0
.
1
3
8
4.
0
0

2
.
0
0
0.
0
0
2
7
5

0
.
1
4
0
2.
4

0
.
0
5
9

8
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

7

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Pr
o
n
g
h
o
r
n

S
t
r
o
n
t
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
1
0

5
3
2
18
.
3

1
8
.
3
48
4

2
.
0
0
0.
3
3
3

1
8
.
6
26
3
.
0

0
.
0
7
1

1
0
0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

T
h
a
ll
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
4
0
0

0
.
0
0
2
2
0
0.
0
0
0
0
7
5
7

0
.
0
0
0
0
7
5
7
0.
5
5
0

2
.
0
0
0.
0
0
0
3
7
8

0
.
0
0
0
4
5
4
0.
0

0
.
0
6
1

5
4
%
Pa
s
s
Pr
o
n
g
h
o
r
n

V
a
n
a
d
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
5
0

0
.
1
4
1
0.
0
0
4
8
6

0
.
0
0
4
8
6
25
.
7

2
.
0
0
0.
0
1
7
7

0
.
0
2
2
5
0.
2

0
.
1
1

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0
0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

Z
i
n
c

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
5
5
12
.2
12
.2
23
0
0

2
.
0
0
1.
5
8

1
3
.
8
16
0
.
0

0
.
0
8
6

1
0
0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
HI

-

I
n
o
r
g
a
n
i
c
s
90
(d
e
t
s
)
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
8
7

3
1
8
10
.
9

1
0
.
9
17
0

2
.
0
0
0.
1
1
7

1
1
5.
0
2.
2
14
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

A
c
e
n
a
p
h
t
h
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
7
.
2
0.
5
9
3

0
.
5
9
3
0.
0
4
1
8

2
.
0
0
0.
0
0
0
0
2
8
8

0
.
5
9
3
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ac
e
n
a
p
h
t
h
y
l
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
0
.
2
0.
6
9
4

0
.
6
9
4
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
7
0
1
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

A
n
t
h
r
a
c
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
2
5
6

0
.
2
5
6
3.
7
0

2
.
0
0
0.
0
0
2
5
5

0
.
2
5
8
10
0
0
.
0

<
0
.
0
1

7
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
2
8
2

0
.
2
8
2
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
2
9
0
1.
0

0
.
2
9

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Be
n
z
o
(
a
)
p
y
r
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
.
5
0.
3
6
2

0
.
3
6
2
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
3
6
9
1.
0

0
.
3
7

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
1
0

3
.
2
6
0.
1
1
2

0
.
1
1
2
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
1
1
9
1.
0

0
.
1
2

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
1.
4
1

1
.
4
1
10
.
5

2
.
0
0
0.
0
0
7
2
2

1
.
4
2
1.
0
1.
4
0%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
8
4
0.
3
0
4

0
.
3
0
4
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
3
1
1
1.
0

0
.
3
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ch
r
y
s
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
2
8
2

0
.
2
8
2
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
2
9
0
1.
0

0
.
2
9

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
1
3
0

1
.
3
6
0.
0
4
6
9

0
.
0
4
6
9
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
5
4
2
1.
0

0
.
0
5
4

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

F
l
u
o
r
a
n
t
h
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
2
4
8

0
.
0
0
2
4
8
0.
1
4
4

2
.
0
0
0.
0
0
0
0
9
9
1

0
.
0
0
2
5
8
12
5
.
0

<
0
.
0
1

4
%
Pa
s
s
Pr
o
n
g
h
o
r
n

F
l
u
o
r
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
1
9
0
17
8

1
7
8
33

2
.
0
0
0.
0
2
2
7

1
7
8
12
5
.
0
1.
4
14
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
1
1
0

1
.
1
6
0.
0
3
9
7

0
.
0
3
9
7
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
4
6
9
1.
0

0
.
0
4
7

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

N
a
p
h
t
h
a
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
2
.
2

6
4
7
22
.
2

2
2
.
2
53

2
.
0
0
0.
0
3
6
5

2
2
.
3
50
.
0

0
.
4
5

2
5
%
Pa
s
s
Pr
o
n
g
h
o
r
n

P
h
e
n
a
n
t
h
r
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
9
.
5
0.
6
7
1

0
.
6
7
1
92

2
.
0
0
0.
0
6
3
3

0
.
7
3
5
17
5
.
0

<
0
.
0
1

1
8
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Py
r
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
7
2
0

7
.
5
6
0.
2
6
0

0
.
2
6
0
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
2
6
7
75
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
HI

-

P
A
H
s
4.
1
(d
e
t
s
)
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

T
P
H

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

-

0
00
47
0
0
0

2
.
0
0
32
.
3

3
2
.
3
10
0
0
.
0

0
.
0
3
2

1
0
0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
HI

-

P
e
t
r
o
l
e
u
m
0.
0
3
2
(d
e
t
s
)
Pa
s
s
Pr
o
n
g
h
o
r
n
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
2
0
2

1
.
0
1
0.
0
3
4
8

0
.
0
3
4
8
50

2
.
0
0
0.
0
3
4
4

0
.
0
6
9
2
0.
2

0
.
2
9

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
7

0
.
1
5
4
0.
0
0
5
2
9

0
.
0
0
5
2
9
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
1
2
5
0.
2

0
.
0
5
2

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
1
1
8

1
.
2
4
0.
0
4
2
6

0
.
0
4
2
6
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
4
9
9
0.
2

0
.
2
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
1
4
3

1
.
5
0
0.
0
5
1
7

0
.
0
5
1
7
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
5
8
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
.
1
1
6
0.
0
0
4
0
0

0
.
0
0
4
0
0
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
1
1
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
2-
M
e
t
h
y
l
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

9
.
7
7

1
0
3
3.
5
3

3
.
5
3
10
.
5

2
.
0
0
0.
0
0
7
2
2

3
.
5
4
34
0
.
0

0
.
0
1
0

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
2
8

4
7
.
8
1.
6
4

1
.
6
4
21

2
.
0
0
0.
0
1
4
4

1
.
6
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
7
6
7

0
.
8
0
5
0.
0
2
7
7

0
.
0
2
7
7
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
3
4
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
4-
C
h
l
o
r
o
a
n
i
l
i
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
1
8

1
2
.
4
0.
4
2
6

0
.
4
2
6
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
4
3
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
4-
M
e
t
h
y
l
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
9
5
1

9
.
9
8
0.
3
4
3

0
.
3
4
3
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
3
5
1
34
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Be
n
z
o
i
c

a
c
i
d
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
0
8

5
4
.
1
1.
8
6

1
.
8
6
50

2
.
0
0
0.
0
3
4
4

1
.
9
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Be
n
z
y
l
a
l
c
o
h
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

5
.
6
7

5
9
.
5
2.
0
5

2
.
0
5
10
.
5

2
.
0
0
0.
0
0
7
2
2

2
.
0
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
6
6
0

0
.
0
9
9
0
0.
0
0
3
4
0

0
.
0
0
3
4
0
1.
5
0

2
.
0
0
0.
0
0
1
0
3

0
.
0
0
4
4
4
18
.
3

<
0
.
0
1

1
8
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
1
8
2

0
.
0
1
9
1
0.
0
0
0
6
5
7

0
.
0
0
0
6
5
7
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
0
7
8
8
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

D
i
b
e
n
z
o
f
u
r
a
n

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
8
9

2
2
.
6
0.
7
7
9

0
.
7
7
9
12

2
.
0
0
0.
0
0
8
2
5

0
.
7
8
7
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
0
4

3
.
2
0
0.
1
1
0

0
.
1
1
0
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
1
1
7
45
8
3
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
1
1

2
2
.
1
0.
7
6
1

0
.
7
6
1
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
7
6
8
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
2
9
8

0
.
0
3
1
3
0.
0
0
1
0
8

0
.
0
0
1
0
8
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
0
8
3
0
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
4
6
1

4
.
8
4
0.
1
6
6

0
.
1
6
6
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
1
7
4
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
0
7
8
5

0
.
0
0
8
2
4
0.
0
0
0
2
8
4

0
.
0
0
0
2
8
4
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
0
7
5
1
1.
6

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
2
0
7

#
#
#
#
#
#
#
#
#
0.
0
0
0
0
0
0
0
5
6
9

0
.
0
0
0
0
0
0
0
5
6
9
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
5
0

0
.
0
0
0
0
0
0
6
0
7
1.
6

<
0
.
0
1

4
%
Pa
s
s
Pr
o
n
g
h
o
r
n
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
.
1
1
6
0.
0
0
4
0
0

0
.
0
0
4
0
0
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
1
1
2
1.
6

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
3
0
5

0
.
0
3
2
0
0.
0
0
1
1
0

0
.
0
0
1
1
0
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
0
8
3
2
1.
6

<
0
.
0
1

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Is
o
p
h
o
r
o
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
4
6
7

4
.
9
1
0.
1
6
9

0
.
1
6
9
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
1
7
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
4
5

2
5
.
7
0.
8
8
5

0
.
8
8
5
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
8
9
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
7
1
9

0
.
7
5
5
0.
0
2
6
0

0
.
0
2
6
0
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
3
3
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
1
2
9

0
.
0
6
4
4
0.
0
0
2
2
2

0
.
0
0
2
2
2
50

2
.
0
0
0.
0
3
4
4

0
.
0
3
6
6
0.
2

0
.
1
5

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n
HI

-

S
V
O
C
s
<0
.
0
1

(
d
e
t
s
)
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
2
1
4
0.
0
0
0
0
7
3
5

0
.
0
0
0
0
7
3
5
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
1
3

0
.
0
0
0
0
7
3
9
1.
4

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
2
7
9

0
.
0
0
0
2
5
1
0.
0
0
0
0
0
8
6
4

0
.
0
0
0
0
0
8
6
4
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
1
9

0
.
0
0
0
0
0
9
2
6
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
3
5
4
0.
0
0
0
0
1
2
2

0
.
0
0
0
0
1
2
2
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
8
8

0
.
0
0
0
0
1
2
9
1.
4

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
2
9
8

0
.
0
0
0
2
3
8
0.
0
0
0
0
0
8
1
9

0
.
0
0
0
0
0
8
1
9
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
5
0

0
.
0
0
0
0
0
8
7
4
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
8
9
9
0.
0
0
0
0
3
0
9

0
.
0
0
0
0
3
0
9
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
3
1
4
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
9
0
8
0.
0
0
0
3
1
2

0
.
0
0
0
3
1
2
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
7
5
7

0
.
0
0
0
3
1
3
2.
5

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
3
7

0
.
0
0
3
8
5
0.
0
0
0
1
3
2

0
.
0
0
0
1
3
2
0.
0
0
2
8
0

2
.
0
0
0.
0
0
0
0
0
1
9
3

0
.
0
0
0
1
3
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
5
2
6
0.
0
0
0
1
8
1

0
.
0
0
0
1
8
1
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
1
9

0
.
0
0
0
1
8
2
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
8
0

0
.
0
0
0
0
1
8
5
0.
0
0
0
0
0
0
6
3
8

0
.
0
0
0
0
0
0
6
3
8
0.
0
0
3
2
0

2
.
0
0
0.
0
0
0
0
0
2
2
0

0
.
0
0
0
0
0
2
8
4
NS
V
--
4%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
4
3
8

0
.
0
0
1
7
1
0.
0
0
0
0
5
8
8

0
.
0
0
0
0
5
8
8
0.
0
0
3
9
0

2
.
0
0
0.
0
0
0
0
0
2
6
8

0
.
0
0
0
0
6
1
5
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
5
7

0
.
0
0
3
6
0
0.
0
0
0
1
2
4

0
.
0
0
0
1
2
4
0.
0
0
1
4
0

2
.
0
0
0.
0
0
0
0
0
0
9
6
3

0
.
0
0
0
1
2
5
NS
V
--
4%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
2
0
0
0.
0
0
0
0
6
8
9

0
.
0
0
0
0
6
8
9
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
5
0

0
.
0
0
0
0
6
9
4
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
5
7
3
0.
0
0
0
0
1
9
7

0
.
0
0
0
0
1
9
7
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
2
0
2
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
1
.
7

0
.
0
1
0
5
0.
0
0
0
3
6
1

0
.
0
0
0
3
6
1
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
1
9

0
.
0
0
0
3
6
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
4
9
8
0.
0
0
0
0
0
1
7
1

0
.
0
0
0
0
0
1
7
1
0.
0
0
1
9
0

2
.
0
0
0.
0
0
0
0
0
1
3
1

0
.
0
0
0
0
0
3
0
2
NS
V
--
4%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
8
1
2
0.
0
0
0
0
0
2
7
9

0
.
0
0
0
0
0
2
7
9
0.
0
0
3
1
0

2
.
0
0
0.
0
0
0
0
0
2
1
3

0
.
0
0
0
0
0
4
9
2
NS
V
--
4%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

2
-
B
u
t
a
n
o
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
7
3
2
0.
0
2
5
2

0
.
0
2
5
2
0.
0
1
5
9

2
.
0
0
0.
0
0
0
0
1
0
9

0
.
0
2
5
2
10
.
0

<
0
.
0
1

1
8
%
Pa
s
s
Pr
o
n
g
h
o
r
n
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
0
.
2

0
.
1
2
0
0.
0
0
4
1
4

0
.
0
0
4
1
4
0.
0
0
5
9
5

2
.
0
0
0.
0
0
0
0
0
4
0
9

0
.
0
0
4
1
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
2-
C
h
l
o
r
o
p
h
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
5
5
7

5
.
8
4
0.
2
0
1

0
.
2
0
1
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
2
0
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
2-
H
e
x
a
n
o
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
6
3
2
0.
0
0
2
1
7

0
.
0
0
2
1
7
0.
0
0
3
8
0

2
.
0
0
0.
0
0
0
0
0
2
6
1

0
.
0
0
2
1
8
10
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
5
6
6

5
.
9
4
0.
2
0
4

0
.
2
0
4
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
2
1
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

8

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
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r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Pr
o
n
g
h
o
r
n
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
0
9
3
4

0
.
0
9
8
1
0.
0
0
3
3
7

0
.
0
0
3
3
7
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
0
1
0
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
8
5
4
0.
0
0
2
9
4

0
.
0
0
2
9
4
0.
0
0
4
3
0

2
.
0
0
0.
0
0
0
0
0
2
9
6

0
.
0
0
2
9
4
25
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n

A
c
e
t
o
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

7
5
.
6

1
8
1
0
62
.
4

6
2
.
4
24

2
.
0
0
0.
0
1
6
5

6
2
.
4
10
.
0
6.
2
32
%
Re
t
a
i
n
Pr
o
n
g
h
o
r
n

B
e
n
z
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
3
3
9
0.
0
0
1
1
6

0
.
0
0
1
1
6
0.
0
0
4
1
0

2
.
0
0
0.
0
0
0
0
0
2
8
2

0
.
0
0
1
1
7
0.
7

<
0
.
0
1

1
4
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
7
.
9

1
.
3
3
0.
0
4
5
6

0
.
0
4
5
6
0.
0
7
4
0

2
.
0
0
0.
0
0
0
0
5
0
9

0
.
0
4
5
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
4
0

2
5
.
2
0.
8
6
6

0
.
8
6
6
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
8
7
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
6
5
9

6
.
9
2
0.
2
3
8

0
.
2
3
8
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
2
4
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

8
.
4
9

0
.
0
0
5
9
4
0.
0
0
0
2
0
4

0
.
0
0
0
2
0
4
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
2
0
5
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Br
o
m
o
f
o
r
m
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
4
6

0
.
0
0
0
1
7
3
0.
0
0
0
0
0
5
9
5

0
.
0
0
0
0
0
5
9
5
0.
0
0
0
5
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
4
4

0
.
0
0
0
0
0
6
3
0
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Br
o
m
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
2
9
8
0.
0
0
1
0
3

0
.
0
0
1
0
3
0.
0
0
1
5
0

2
.
0
0
0.
0
0
0
0
0
1
0
3

0
.
0
0
1
0
3
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
2
9

0
.
0
0
3
8
6
0.
0
0
0
1
3
3

0
.
0
0
0
1
3
3
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
1
9

0
.
0
0
0
1
3
4
16
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
9
4
0
0.
0
0
0
0
0
3
2
3

0
.
0
0
0
0
0
3
2
3
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
0
3
7
1
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
7
9
0.
0
0
0
0
9
5
9

0
.
0
0
0
0
9
5
9
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
8
8

0
.
0
0
0
0
9
6
6
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
f
o
r
m
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
8
7
3

0
.
0
0
0
6
1
1
0.
0
0
0
0
2
1
0

0
.
0
0
0
0
2
1
0
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
2
1
5
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
2
6
9

0
.
0
0
0
2
6
9
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
8
8

0
.
0
0
0
2
7
0
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
7
4
4
0.
0
0
0
2
5
6

0
.
0
0
0
2
5
6
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
2
5
6
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
4
2
7
0.
0
0
0
1
4
7

0
.
0
0
0
1
4
7
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
1
3

0
.
0
0
0
1
4
7
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
6
7
4

0
.
0
0
0
4
7
2
0.
0
0
0
0
1
6
2

0
.
0
0
0
0
1
6
2
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
1
6
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Di
b
r
o
m
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
3
.
3

0
.
0
0
6
6
5
0.
0
0
0
2
2
9

0
.
0
0
0
2
2
9
0.
0
0
0
5
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
4
4

0
.
0
0
0
2
2
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
5
8
0

0
.
0
0
0
6
3
8
0.
0
0
0
0
2
1
9

0
.
0
0
0
0
2
1
9
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
7
5
7

0
.
0
0
0
0
2
2
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Et
h
y
l
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
8
9
8
0.
0
0
0
0
0
3
0
9

0
.
0
0
0
0
0
3
0
9
0.
0
0
1
3
0

2
.
0
0
0.
0
0
0
0
0
0
8
9
4

0
.
0
0
0
0
0
3
9
8
97
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
m,
p
-
X
y
l
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
6
0
8
0.
0
0
0
2
0
9

0
.
0
0
0
2
0
9
0.
0
0
2
0
0

2
.
0
0
0.
0
0
0
0
0
1
3
8

0
.
0
0
0
2
1
0
17
9
.
0

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
1
0

0
.
0
1
3
1
0.
0
0
0
4
5
1

0
.
0
0
0
4
5
1
0.
0
0
3
2
0

2
.
0
0
0.
0
0
0
0
0
2
2
0

0
.
0
0
0
4
5
4
5.
9

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n

o
-
X
y
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
3
4

0
.
0
0
9
0
1
0.
0
0
0
3
1
0

0
.
0
0
0
3
1
0
0.
0
0
2
7
0

2
.
0
0
0.
0
0
0
0
0
1
8
6

0
.
0
0
0
3
1
2
17
9
.
0

<
0
.
0
1

1
4
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Ph
e
n
o
l
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
6
2

2
7
.
5
0.
9
4
5

0
.
9
4
5
10
.
5

2
.
0
0
0.
0
0
7
2
2

0
.
9
5
2
17
.
1

0
.
0
5
6

0
%
Pa
s
s
Pr
o
n
g
h
o
r
n

S
t
y
r
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
0
2

0
.
0
1
0
5
0.
0
0
0
3
6
0

0
.
0
0
0
3
6
0
0.
0
0
2
6
0

2
.
0
0
0.
0
0
0
0
0
1
7
9

0
.
0
0
0
3
6
1
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
9

0
.
0
1
3
3
0.
0
0
0
4
5
7

0
.
0
0
0
4
5
7
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
4
5
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
2
2
7
0.
0
0
0
0
7
8
0

0
.
0
0
0
0
7
8
0
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
1
9

0
.
0
0
0
0
7
8
7
1.
4

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n

T
o
l
u
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
8
8
2
0.
0
0
3
0
3

0
.
0
0
3
0
3
0.
0
1
8
7

2
.
0
0
0.
0
0
0
0
1
2
9

0
.
0
0
3
0
5
52
.
0

<
0
.
0
1

2
3
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
0
6
0
3

0
.
0
0
0
0
6
0
3
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
6
0
7
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
6
5
4
0.
0
0
0
0
2
2
5

0
.
0
0
0
0
2
2
5
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
5
0

0
.
0
0
0
0
2
3
1
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
3
1

0
.
0
0
0
2
3
2
0.
0
0
0
0
0
7
9
8

0
.
0
0
0
0
0
7
9
8
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
0
8
4
6
0.
7

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
2
6
1

0
.
0
0
0
2
8
8
0.
0
0
0
0
0
9
8
9

0
.
0
0
0
0
0
9
8
9
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
7
5
7

0
.
0
0
0
0
1
0
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Vi
n
y
l

A
c
e
t
a
t
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
2

0
.
0
2
6
4
0.
0
0
0
9
0
7

0
.
0
0
0
9
0
7
0.
0
0
1
2
0

2
.
0
0
0.
0
0
0
0
0
0
8
2
5

0
.
0
0
0
9
0
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n
Vi
n
y
l

c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
1
0

0
.
0
0
3
7
2
0.
0
0
0
1
2
8

0
.
0
0
0
1
2
8
0.
0
0
1
2
0

2
.
0
0
0.
0
0
0
0
0
0
8
2
5

0
.
0
0
0
1
2
9
0.
2

<
0
.
0
1

5
%
Pa
s
s
Pr
o
n
g
h
o
r
n
HI

-

V
O
C
s
6.
3
(d
e
t
s
)
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
9

2
.
9
3
0.
7
3
3
0-
0
00
.
7
3
3
0.
1
0
5

1
3
0.
0
0
3
4
1

0
.
7
3
6
2.
7

0
.
2
7

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
6

2
.
1
3
0.
5
3
2
0-
0
00
.
5
3
2
0.
0
8
0
0

1
3
0.
0
0
2
6
0

0
.
5
3
5
0.
0
13
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
1
7
0

0
.
2
5
5
0.
0
6
3
8
0-
0
00
.
0
6
3
8
1.
5
0

1
3
0.
0
4
8
8

0
.
1
1
2
2.
0

0
.
0
5
6

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

1
4
4
0
35
9
0-
0
03
5
9
50

1
3
1.
6
2

3
6
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

5
.
1
0

1
0
.
2
2.
5
5
0-
0
02
.
5
5
2.
0
0

1
3
0.
0
6
5
0

2
.
6
2
2.
0
1.
3
2%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
1
6

3
3
.
2
8.
3
0
0-
0
08
.
3
0
10
.
5

1
3
0.
3
4
1

8
.
6
4
2.
0
4.
3
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
1
1.
6
8
0-
0
01
.
6
8
1.
5
0

1
3
0.
0
4
8
8

1
.
7
3
9.
0

0
.
1
9

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7

1
3
5
0
33
7
0-
0
03
3
7
50

1
3
1.
6
2

3
3
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
N
i
t
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
9

2
8
3
70
.
7
0-
0
07
0
.
7
10
.
5

1
3
0.
3
4
1

7
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
9

4
.
3
2
1.
0
8
0-
0
01
.
0
8
0.
1
4
0

1
3
0.
0
0
4
5
5

1
.
0
9
2.
0

0
.
5
4

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
3-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
5

1
3
2
0
33
1
0-
0
03
3
1
50

1
3
1.
6
2

3
3
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
6

4
.
1
4
1.
0
4
0-
0
01
.
0
4
0.
1
5
0

1
3
0.
0
0
4
8
8

1
.
0
4
2.
0

0
.
5
2

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
2

1
6
0
0
40
0
0-
0
04
0
0
50

1
3
1.
6
2

4
0
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
5

1
4
2
0
35
6
0-
0
03
5
6
50

1
3
1.
6
2

3
5
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
N
i
t
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
8

1
4
9
0
37
3
0-
0
03
7
3
50

1
3
1.
6
2

3
7
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
5

5
.
2
3
1.
3
1
0-
0
01
.
3
1
0.
1
9
0

1
3
0.
0
0
6
1
8

1
.
3
1
2.
0

0
.
6
6

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

H
M
X
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
0
0

2
5
6.
2
5
0-
0
06
.
2
5
25

1
3
0.
8
1
2

7
.
0
6
1.
0
7.
1
31
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ni
t
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
7

3
1
1
77
.
9
0-
0
07
7
.
9
10
.
5

1
3
0.
3
4
1

7
8
.
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ni
t
r
o
g
l
y
c
e
r
i
n
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
6

9
.
0
5
2.
2
6
0-
0
02
.
2
6
0.
3
4
0

1
3
0.
0
1
1
0

2
.
2
7
3.
0

0
.
7
6

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

N
i
t
r
o
g
u
a
n
i
d
i
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
4
.
2

7
.
2
7
1.
8
2
0-
0
01
.
8
2
0.
3
0
0

1
3
0.
0
0
9
7
5

1
.
8
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
PE
T
N
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
6

1
3
.
8
3.
4
4
0-
0
03
.
4
4
0.
5
0
0

1
3
0.
0
1
6
2

3
.
4
6
17
0
.
0

0
.
0
2
0

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

P
i
c
r
i
c

a
c
i
d
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
4

1
3
.
2
3.
3
1
0-
0
03
.
3
1
0.
5
0
0

1
3
0.
0
1
6
2

3
.
3
2
NS
V
--
7%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
RD
X
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
3
21
.
8
0-
0
02
1
.
8
1.
5
0

1
3
0.
0
4
8
8

2
1
.
9
2.
0
11
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Te
t
r
y
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
1

6
.
6
9
1.
6
7
0-
0
01
.
6
7
0.
2
3
0

1
3
0.
0
0
7
4
8

1
.
6
8
1.
3
1.
3
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

E
n
e
r
g
e
t
i
c
s
8.
4
(d
e
t
s
)
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
l
u
m
i
n
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
3
4
0

1
8
4
0
0
45
9
0
0-
0
04
5
9
0
54
0
0
0

1
3
17
6
0

6
3
5
0
1.
9
33
0
0
10
0
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
n
t
i
m
o
n
y
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
0
2
5
0

4
.
1
7
1.
0
4
0-
0
01
.
0
4
16
7

1
3
5.
4
3

6
.
4
7
0.
1
11
0
79
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
r
s
e
n
i
c
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
3
4
0.
8
3
5
0-
0
00
.
8
3
5
41
.
3

1
3
1.
3
4

2
.
1
8
0.
4
5.
5
58
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

B
a
r
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
3
6
0

2
3
0
57
.
6
0-
0
05
7
.
6
64
0

1
3
20
.
8

7
8
.
4
45
.
0
1.
7
10
0
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

B
e
r
y
ll
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
1
8

0
.
8
5
1
0.
2
1
3
0-
0
00
.
2
1
3
0.
7
2
0

1
3
0.
0
2
3
4

0
.
2
3
6
0.
5
3

0
.
4
4

4
8
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

C
a
d
m
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u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
3
0
32
.
6
0-
0
03
2
.
6
32

1
3
1.
0
4

3
3
.
6
0.
8
44
44
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
1

0
.
0
2
9
9
0.
0
0
7
4
7
0-
0
0

0
.
0
0
7
4
7
0.
0
0
1
1
0

1
3
0.
0
0
0
0
3
5
8

0
.
0
0
7
5
0
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

C
h
r
o
m
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
1
6

1
7
5
43
.
7
0-
0
04
3
.
7
55
.
3

1
3
1.
8
0

4
5
.
5
3.
3
14
10
0
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

C
o
b
a
l
t
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
2
9
1

1
.
4
3
0.
3
5
6
0-
0
00
.
3
5
6
4.
9
0

1
3
0.
1
5
9

0
.
5
1
6
1.
1

0
.
4
5

7
9
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

C
o
p
p
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
0
.
9
17
.
7
0-
0
01
7
.
7
18
0
0
0

1
3
58
5

6
0
3
11
.
7
52
85
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

I
r
o
n
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
3
8
0

5
7
0
0
14
3
0
0-
0
01
4
3
0
15
0
0
0

1
3
48
8

1
9
1
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

L
e
a
d
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
8
2
0
12
1
0
0-
0
01
2
1
0
48
0
0
0

1
3
15
6
0

2
7
7
0
0.
9
30
0
0
83
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

M
a
g
n
e
s
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
4
2
5

1
0
3
0
0
25
8
0
0-
0
02
5
8
0
24
3
0
0

1
3
79
0

3
3
7
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

9

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

M
a
n
g
a
n
e
s
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
.
7
7.
9
1
0-
0
07
.
9
1
51
9

1
3
16
.
9

2
4
.
8
88
.
0

0
.
2
8

1
0
0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

M
e
r
c
u
r
y
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
3
6
9
0.
0
9
2
2
0-
0
00
.
0
9
2
2
0.
0
7
0
0

1
3
0.
0
0
2
2
8

0
.
0
9
4
4
0.
0
3.
0
27
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

M
o
l
y
b
d
e
n
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
0
9

3
5
.
5
8.
8
9
0-
0
08
.
8
9
17

1
3
0.
5
5
2

9
.
4
4
0.
3
36
91
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

N
i
c
k
e
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

4
.
7
3

1
9
5
48
.
8
0-
0
04
8
.
8
41
.
3

1
3
1.
3
4

5
0
.
2
40
.
0
1.
3
10
0
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

N
i
t
r
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
0
0

2
2
.
8
5.
7
0
0-
0
05
.
7
0
22
.
8

1
3
0.
7
4
1

6
.
4
4
50
7
.
0

0
.
0
1
3

9
2
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

P
e
r
c
h
l
o
r
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
0
0

4
.
5
0
1.
1
2
0-
0
01
.
1
2
4.
5
0

1
3
0.
1
4
6

1
.
2
7
2.
6

0
.
4
9

5
0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

P
h
o
s
p
h
o
r
u
s
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
0
0

9
9
0
24
8
0-
0
02
4
8
99
0

1
3
32
.
2

2
8
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Se
l
e
n
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
2
0.
7
5
5
0-
0
00
.
7
5
5
5.
0
0

1
3
0.
1
6
2

0
.
9
1
7
0.
2
4.
6
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

S
i
l
v
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
5
.
3

6
1
.
4
15
.
3
0-
0
01
5
.
3
4.
0
0

1
3
0.
1
3
0

1
5
.
5
2.
4
6.
5
8%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

S
t
r
o
n
t
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
2
7
8

1
3
5
33
.
6
0-
0
03
3
.
6
48
4

1
3
15
.
7

4
9
.
4
26
3
.
0

0
.
1
9

1
0
0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

T
h
a
ll
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
2
5
6

0
.
1
4
1
0.
0
3
5
2
0-
0
00
.
0
3
5
2
0.
5
5
0

1
3
0.
0
1
7
9

0
.
0
5
3
1
0.
0
7.
2
54
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

V
a
n
a
d
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
0
8
8
0

2
.
2
6
0.
5
6
5
0-
0
00
.
5
6
5
25
.
7

1
3
0.
8
3
5

1
.
4
0
0.
2
6.
7
10
0
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

Z
i
n
c
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
8
0
27
1
0-
0
0
27
1
23
0
0

1
3
74
.
8

3
4
6
16
0
.
0
2.
2
10
0
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

I
n
o
r
g
a
n
i
c
s
66
0
0
(d
e
t
s
)
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e
0.
0
4
1

0
.
2
5
0
10.250
0
-

0

0
1
0
0
2
9
4
9
4
0
12
3
0
0-
0
01
2
3
0
17
0

1
3
5.
5
2

1
2
4
0
5.
0
25
0
14
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
c
e
n
a
p
h
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
4
7

0
.
0
6
1
5
0.
0
1
5
4
0-
0
00
.
0
1
5
4
0.
0
4
1
8

1
3
0.
0
0
1
3
6

0
.
0
1
6
7
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ac
e
n
a
p
h
t
h
y
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
2
.
9

2
4
0
60
.
1
0-
0
06
0
.
1
10
.
5

1
3
0.
3
4
1

6
0
.
5
17
5
.
0

0
.
3
5

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
4
2

8
.
9
5
2.
2
4
0-
0
02
.
2
4
3.
7
0

1
3
0.
1
2
0

2
.
3
6
10
0
0
.
0

<
0
.
0
1

7
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
5
9

1
6
.
7
4.
1
7
0-
0
04
.
1
7
10
.
5

1
3
0.
3
4
1

4
.
5
1
1.
0
4.
5
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
3
3

1
4
3.
4
9
0-
0
03
.
4
9
10
.
5

1
3
0.
3
4
1

3
.
8
3
1.
0
3.
8
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
6
0

2
7
.
3
6.
8
2
0-
0
06
.
8
2
10
.
5

1
3
0.
3
4
1

7
.
1
7
1.
0
7.
2
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
9
4

3
0
.
9
7.
7
2
0-
0
07
.
7
2
10
.
5

1
3
0.
3
4
1

8
.
0
6
1.
0
8.
1
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
6
0

2
7
.
3
6.
8
2
0-
0
06
.
8
2
10
.
5

1
3
0.
3
4
1

7
.
1
7
1.
0
7.
2
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
r
y
s
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
2
9

2
4
6.
0
1
0-
0
06
.
0
1
10
.
5

1
3
0.
3
4
1

6
.
3
5
1.
0
6.
4
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
3
1

2
4
.
3
6.
0
6
0-
0
06
.
0
6
10
.
5

1
3
0.
3
4
1

6
.
4
0
1.
0
6.
4
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

F
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
0
4

0
.
4
3
8
0.
1
0
9
0-
0
00
.
1
0
9
0.
1
4
4

1
3
0.
0
0
4
6
8

0
.
1
1
4
12
5
.
0

<
0
.
0
1

4
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

F
l
u
o
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

9
.
5
7

3
1
6
79
0-
0
07
9
33

1
3
1.
0
7

8
0
12
5
.
0

0
.
6
4

1
4
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
8
6

3
0
7.
5
1
0-
0
07
.
5
1
10
.
5

1
3
0.
3
4
1

7
.
8
5
1.
0
7.
8
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

N
a
p
h
t
h
a
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

4
.
4
0

2
3
3
58
.
3
0-
0
05
8
.
3
53

1
3
1.
7
2

6
0
50
.
0
1.
2
25
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

P
h
e
n
a
n
t
h
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
7
2

1
5
8
39
.
6
0-
0
03
9
.
6
92

1
3
2.
9
9

4
2
.
6
17
5
.
0

0
.
2
4

1
8
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Py
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
7
5

1
8
.
4
4.
5
9
0-
0
04
.
5
9
10
.
5

1
3
0.
3
4
1

4
.
9
3
75
.
0

0
.
0
6
6

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

P
A
H
s
25
0
(d
e
t
s
)
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

T
P
H
0.
0
4
1

0
.
2
5
0
10
.
2
5
0
0

-

0

0

1
0
0

-

0
0
0-
0
00
47
0
0
0

1
3
15
3
0

1
5
3
0
10
0
0
.
0
1.
5
10
0
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

P
e
t
r
o
l
e
u
m
1.
5
(d
e
t
s
)
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
5
.
1

1
7
6
0
43
9
0-
0
04
3
9
50

1
3
1.
6
2

4
4
0
0.
2
18
0
0
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
5
.
6

3
7
4
93
.
4
0-
0
09
3
.
4
10
.
5

1
3
0.
3
4
1

9
3
.
7
0.
2
39
0
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
2
.
6

3
4
2
85
.
6
0-
0
08
5
.
6
10
.
5

1
3
0.
3
4
1

8
5
.
9
0.
2
36
0
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
2
.
3

3
4
0
84
.
9
0-
0
08
4
.
9
10
.
5

1
3
0.
3
4
1

8
5
.
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
6

3
7
8
94
.
5
0-
0
09
4
.
5
10
.
5

1
3
0.
3
4
1

9
4
.
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
M
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
1

2
8
4
71
.
1
0-
0
07
1
.
1
10
.
5

1
3
0.
3
4
1

7
1
.
5
34
0
.
0

0
.
2
1

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
8

6
0
5
15
1
0-
0
01
5
1
21

1
3
0.
6
8
2

1
5
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
3
.
2

3
4
9
87
.
1
0-
0
08
7
.
1
10
.
5

1
3
0.
3
4
1

8
7
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
C
h
l
o
r
o
a
n
i
l
i
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
6

3
1
1
77
.
7
0-
0
07
7
.
7
10
.
5

1
3
0.
3
4
1

7
8
.
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
M
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
9

3
1
4
78
.
4
0-
0
07
8
.
4
10
.
5

1
3
0.
3
4
1

7
8
.
8
34
0
.
0

0
.
2
3

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
i
c

a
c
i
d
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
7

1
4
9
0
37
1
0-
0
03
7
1
50

1
3
1.
6
2

3
7
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
y
l
a
l
c
o
h
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
7

2
9
1
72
.
8
0-
0
07
2
.
8
10
.
5

1
3
0.
3
4
1

7
3
.
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
3
.
4

5
0
.
1
12
.
5
0-
0
01
2
.
5
1.
5
0

1
3
0.
0
4
8
8

1
2
.
6
18
.
3

0
.
6
9

1
8
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
8
.
8

4
0
8
10
2
0-
0
01
0
2
10
.
5

1
3
0.
3
4
1

1
0
2
55
0
.
0

0
.
1
9

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

D
i
b
e
n
z
o
f
u
r
a
n
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9

3
4
8
87
.
1
0-
0
08
7
.
1
12

1
3
0.
3
9
0

8
7
.
5
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
3

3
2
9
82
.
2
0-
0
08
2
.
2
10
.
5

1
3
0.
3
4
1

8
2
.
6
45
8
3
.
0

0
.
0
1
8

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
9

3
0
3
75
.
8
0-
0
07
5
.
8
10
.
5

1
3
0.
3
4
1

7
6
.
2
55
0
.
0

0
.
1
4

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
8

3
9
9
99
.
8
0-
0
09
9
.
8
10
.
5

1
3
0.
3
4
1

1
0
0
55
0
.
0

0
.
1
8

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
8

3
2
3
80
.
8
0-
0
08
0
.
8
10
.
5

1
3
0.
3
4
1

8
1
.
2
55
0
.
0

0
.
1
5

0
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

4
0
.
2

4
2
2
10
6
0-
0
01
0
6
10
.
5

1
3
0.
3
4
1

1
0
6
1.
6
66
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
8
.
6

0
.
0
3
0
9
0.
0
0
7
7
2
0-
0
0

0
.
0
0
7
7
2
0.
0
0
0
8
0
0

1
3
0.
0
0
0
0
2
6
0

0
.
0
0
7
7
5
1.
6

<
0
.
0
1

4
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
6

3
7
8
94
.
5
0-
0
09
4
.
5
10
.
5

1
3
0.
3
4
1

9
4
.
8
1.
6
59
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
8

3
9
9
99
.
7
0-
0
09
9
.
7
10
.
5

1
3
0.
3
4
1

1
0
0
1.
6
63
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Is
o
p
h
o
r
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
8

3
2
3
80
.
8
0-
0
08
0
.
8
10
.
5

1
3
0.
3
4
1

8
1
.
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

3
0
1
75
.
4
0-
0
07
5
.
4
10
.
5

1
3
0.
3
4
1

7
5
.
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
3
.
3

3
4
9
87
.
4
0-
0
08
7
.
4
10
.
5

1
3
0.
3
4
1

8
7
.
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

5
.
9
3

2
9
7
74
.
1
0-
0
07
4
.
1
50

1
3
1.
6
2

7
5
.
8
0.
2
32
0
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

S
V
O
C
s
0.
6
9
(d
e
t
s
)
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
3

0
.
0
1
7
0
0.
0
0
4
2
4
0-
0
0

0
.
0
0
4
2
4
0.
0
0
0
6
0
0

1
3
0.
0
0
0
0
1
9
5

0
.
0
0
4
2
6
1.
4

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
4

0
.
0
2
8
3
0.
0
0
7
0
8
0-
0
0

0
.
0
0
7
0
8
0.
0
0
0
9
0
0

1
3
0.
0
0
0
0
2
9
2

0
.
0
0
7
1
0
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
1

0
.
0
3
1
1
0.
0
0
7
7
8
0-
0
0

0
.
0
0
7
7
8
0.
0
0
1
0
0

1
3
0.
0
0
0
0
3
2
5

0
.
0
0
7
8
2
1.
4

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
4

0
.
0
2
5
1
0.
0
0
6
2
7
0-
0
0

0
.
0
0
6
2
7
0.
0
0
0
8
0
0

1
3
0.
0
0
0
0
2
6
0

0
.
0
0
6
3
0
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
5

0
.
0
2
0
6
0.
0
0
5
1
6
0-
0
0

0
.
0
0
5
1
6
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
5
1
8
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
3
0
0
0.
0
0
7
5
0
0-
0
0

0
.
0
0
7
5
0
0.
0
0
1
1
0

1
3
0.
0
0
0
0
3
5
8

0
.
0
0
7
5
4
2.
5

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
4

0
.
0
8
2
4
0.
0
2
0
6
0-
0
00
.
0
2
0
6
0.
0
0
2
8
0

1
3
0.
0
0
0
0
9
1
0

0
.
0
2
0
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
7

0
.
0
2
4
9
0.
0
0
6
2
3
0-
0
0

0
.
0
0
6
2
3
0.
0
0
0
9
0
0

1
3
0.
0
0
0
0
2
9
2

0
.
0
0
6
2
6
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
7

0
.
1
1
8
0.
0
2
9
6
0-
0
00
.
0
2
9
6
0.
0
0
3
2
0

1
3
0.
0
0
0
1
0
4

0
.
0
2
9
7
NS
V
--
4%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
9

0
.
1
2
0
0.
0
3
0
1
0-
0
00
.
0
3
0
1
0.
0
0
3
9
0

1
3
0.
0
0
0
1
2
7

0
.
0
3
0
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
4
0
1
0.
0
1
0
0
0-
0
00
.
0
1
0
0
0.
0
0
1
4
0

1
3
0.
0
0
0
0
4
5
5

0
.
0
1
0
1
NS
V
--
4%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
2
2
9
0.
0
0
5
7
4
0-
0
0

0
.
0
0
5
7
4
0.
0
0
0
8
0
0

1
3
0.
0
0
0
0
2
6
0

0
.
0
0
5
7
6
50
.
0

<
0
.
0
1

5
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
0

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
1

0
.
0
2
1
0
0.
0
0
5
2
6
0-
0
0

0
.
0
0
5
2
6
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
5
2
8
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
9

0
.
0
2
4
2
0.
0
0
6
0
5
0-
0
0

0
.
0
0
6
0
5
0.
0
0
0
9
0
0

1
3
0.
0
0
0
0
2
9
2

0
.
0
0
6
0
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
4
.
7

0
.
0
6
6
0
0.
0
1
6
5
0-
0
00
.
0
1
6
5
0.
0
0
1
9
0

1
3
0.
0
0
0
0
6
1
8

0
.
0
1
6
6
NS
V
--
4%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
4
.
7

0
.
1
0
8
0.
0
2
6
9
0-
0
00
.
0
2
6
9
0.
0
0
3
1
0

1
3
0.
0
0
0
1
0
1

0
.
0
2
7
0
NS
V
--
4%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
-
B
u
t
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
5
.
4

0
.
4
0
4
0.
1
0
1
0-
0
00
.
1
0
1
0.
0
1
5
9

1
3
0.
0
0
0
5
1
7

0
.
1
0
1
10
.
0

0
.
0
1
0

1
8
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
3

0
.
1
5
6
0.
0
3
9
1
0-
0
00
.
0
3
9
1
0.
0
0
5
9
5

1
3
0.
0
0
0
1
9
3

0
.
0
3
9
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
C
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
6

3
2
1
80
.
2
0-
0
08
0
.
2
10
.
5

1
3
0.
3
4
1

8
0
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
H
e
x
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
5

0
.
1
0
1
0.
0
2
5
2
0-
0
00
.
0
2
5
2
0.
0
0
3
8
0

1
3
0.
0
0
0
1
2
4

0
.
0
2
5
3
10
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
5

3
2
1
80
.
1
0-
0
08
0
.
1
10
.
5

1
3
0.
3
4
1

8
0
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
6
.
3

3
8
1
95
.
2
0-
0
09
5
.
2
10
.
5

1
3
0.
3
4
1

9
5
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
3

0
.
1
1
3
0.
0
2
8
3
0-
0
00
.
0
2
8
3
0.
0
0
4
3
0

1
3
0.
0
0
0
1
4
0

0
.
0
2
8
4
25
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
c
e
t
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
4
.
9

5
9
7
14
9
0-
0
01
4
9
24

1
3
0.
7
8
0

1
5
0
10
.
0
15
32
%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

B
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
1
1
2
0.
0
2
8
0
0-
0
00
.
0
2
8
0
0.
0
0
4
1
0

1
3
0.
0
0
0
1
3
3

0
.
0
2
8
1
0.
7

0
.
0
4
0

1
4
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
4

1
.
9
5
0.
4
8
9
0-
0
00
.
4
8
9
0.
0
7
4
0

1
3
0.
0
0
2
4
0

0
.
4
9
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

3
0
2
75
.
4
0-
0
07
5
.
4
10
.
5

1
3
0.
3
4
1

7
5
.
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
3

3
1
9
79
.
6
0-
0
07
9
.
6
10
.
5

1
3
0.
3
4
1

8
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
1
9
1
0.
0
0
4
7
7
0-
0
0

0
.
0
0
4
7
7
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
4
7
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Br
o
m
o
f
o
r
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
2

0
.
0
1
5
6
0.
0
0
3
9
0
0-
0
0

0
.
0
0
3
9
0
0.
0
0
0
5
0
0

1
3
0.
0
0
0
0
1
6
3

0
.
0
0
3
9
1
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Br
o
m
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
3

0
.
0
3
9
4
0.
0
0
9
8
6
0-
0
0

0
.
0
0
9
8
6
0.
0
0
1
5
0

1
3
0.
0
0
0
0
4
8
8

0
.
0
0
9
9
1
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8

0
.
0
2
5
2
0.
0
0
6
3
1
0-
0
0

0
.
0
0
6
3
1
0.
0
0
0
9
0
0

1
3
0.
0
0
0
0
2
9
2

0
.
0
0
6
3
4
16
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
2
.
4

0
.
0
2
2
7
0.
0
0
5
6
7
0-
0
0

0
.
0
0
5
6
7
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
5
7
0
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
6

0
.
0
2
8
6
0.
0
0
7
1
4
0-
0
0

0
.
0
0
7
1
4
0.
0
0
1
0
0

1
3
0.
0
0
0
0
3
2
5

0
.
0
0
7
1
7
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
f
o
r
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0

0
.
0
2
1
0
0.
0
0
5
2
5
0-
0
0

0
.
0
0
5
2
5
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
5
2
7
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
2
7
3
0.
0
0
6
8
4
0-
0
0

0
.
0
0
6
8
4
0.
0
0
1
0
0

1
3
0.
0
0
0
0
3
2
5

0
.
0
0
6
8
7
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7

0
.
0
1
8
9
0.
0
0
4
7
2
0-
0
0

0
.
0
0
4
7
2
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
4
7
5
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
5

0
.
0
1
6
5
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0
0
4
1
2
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0
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0
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0
0
4
1
2
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0
0
0
6
0
0

1
3
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0
0
0
0
1
9
5

0
.
0
0
4
1
4
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
b
r
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m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
4
1

0
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2
5
0
1

0
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2
5
0

0

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0

0

1
0
0

3
0
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3

0
.
0
2
1
2
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0
0
5
3
0
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0
0

0
.
0
0
5
3
0
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
5
3
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
b
r
o
m
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
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2
6
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7

0
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0
1
3
4
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0
0
3
3
4
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0
0

0
.
0
0
3
3
4
0.
0
0
0
5
0
0

1
3
0.
0
0
0
0
1
6
3

0
.
0
0
3
3
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
c
h
l
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d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

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0

0

1
0
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3
0
.
5

0
.
0
3
3
5
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0
0
8
3
9
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0
0

0
.
0
0
8
3
9
0.
0
0
1
1
0

1
3
0.
0
0
0
0
3
5
8

0
.
0
0
8
4
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
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h
y
l
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
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2
5
0

0

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0

0

1
0
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3
3
.
3

0
.
0
4
3
3
0.
0
1
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8
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0
00
.
0
1
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8
0.
0
0
1
3
0

1
3
0.
0
0
0
0
4
2
2

0
.
0
1
0
9
97
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
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r

M
o
u
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e
m,
p
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X
y
l
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e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

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0

0

1
0
0

2
8
.
5

0
.
0
5
6
9
0.
0
1
4
2
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0
00
.
0
1
4
2
0.
0
0
2
0
0

1
3
0.
0
0
0
0
6
5
0

0
.
0
1
4
3
17
9
.
0

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
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r

M
o
u
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e
Me
t
h
y
l
e
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e

c
h
l
o
r
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d
e
0.
0
4
1

0
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2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
1

0
.
0
8
9
9
0.
0
2
2
5
0-
0
00
.
0
2
2
5
0.
0
0
3
2
0

1
3
0.
0
0
0
1
0
4

0
.
0
2
2
6
5.
9

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

o
-
X
y
l
e
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e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
3

0
.
0
7
6
5
0.
0
1
9
1
0-
0
00
.
0
1
9
1
0.
0
0
2
7
0

1
3
0.
0
0
0
0
8
7
7

0
.
0
1
9
2
17
9
.
0

<
0
.
0
1

1
4
%
Pa
s
s
Gr
a
s
s
h
o
p
p
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r

M
o
u
s
e
Ph
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
6

3
0
1
75
.
2
0-
0
07
5
.
2
10
.
5

1
3
0.
3
4
1

7
5
.
5
17
.
1
4.
4
0%
Re
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

S
t
y
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
1

0
.
0
7
3
1
0.
0
1
8
3
0-
0
00
.
0
1
8
3
0.
0
0
2
6
0

1
3
0.
0
0
0
0
8
4
5

0
.
0
1
8
4
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
4

0
.
0
1
8
4
0.
0
0
4
6
1
0-
0
0

0
.
0
0
4
6
1
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
4
6
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
2
5
8
0.
0
0
6
4
5
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0
0

0
.
0
0
6
4
5
0.
0
0
0
9
0
0

1
3
0.
0
0
0
0
2
9
2

0
.
0
0
6
4
8
1.
4

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

T
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
9

0
.
5
2
2
0.
1
3
1
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0
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.
1
3
1
0.
0
1
8
7

1
3
0.
0
0
0
6
0
8

0
.
1
3
1
52
.
0

<
0
.
0
1

2
3
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
a
n
s
-
1
,
2
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D
i
c
h
l
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r
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e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
2
0
1
0.
0
0
5
0
2
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0
0

0
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0
0
5
0
2
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
5
0
4
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
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r
o
p
r
o
p
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
1

0
.
0
2
4
0
0.
0
0
6
0
1
0-
0
0

0
.
0
0
6
0
1
0.
0
0
0
8
0
0

1
3
0.
0
0
0
0
2
6
0

0
.
0
0
6
0
4
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
2

0
.
0
2
1
9
0.
0
0
5
4
6
0-
0
0

0
.
0
0
5
4
6
0.
0
0
0
7
0
0

1
3
0.
0
0
0
0
2
2
8

0
.
0
0
5
4
9
0.
7

<
0
.
0
1

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
5

0
.
0
3
4
7
0.
0
0
8
6
7
0-
0
0

0
.
0
0
8
6
7
0.
0
0
1
1
0

1
3
0.
0
0
0
0
3
5
8

0
.
0
0
8
7
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Vi
n
y
l

A
c
e
t
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
2

0
.
0
3
1
4
0.
0
0
7
8
6
0-
0
0

0
.
0
0
7
8
6
0.
0
0
1
2
0

1
3
0.
0
0
0
0
3
9
0

0
.
0
0
7
9
0
NS
V
--
5%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
4

0
.
0
3
4
1
0.
0
0
8
5
3
0-
0
0

0
.
0
0
8
5
3
0.
0
0
1
2
0

1
3
0.
0
0
0
0
3
9
0

0
.
0
0
8
5
7
0.
2

0
.
0
5
0

5
%
Pa
s
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

V
O
C
s
20
(d
e
t
s
)
Re
t
a
i
n
Co
y
o
t
e
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
8
8
0

0
.
0
9
2
4

0
.
0
0
4
1
9

0

-

0
0
0-
0
0

0
.
0
0
4
1
9
0.
1
0
5

2
.
8
0
0.
0
0
0
1
3
3

0
.
0
0
4
3
2
2.
7

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
3
2

0
.
1
0
6

0
.
0
0
4
8
0

0

-

0
0
0-
0
0

0
.
0
0
4
8
0
0.
0
8
0
0

2
.
8
0
0.
0
0
0
1
0
2

0
.
0
0
4
9
0
0.
0

0
.
1
2

0
%
Pa
s
s
Co
y
o
t
e
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
1.
5
0

2
.
8
0
0.
0
0
1
9
0

0
.
0
0
1
9
0
2.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
8
8

3
4
.
4

1
.
5
6

0

-

0
0
0-
0
01
.
5
6
50

2
.
8
0
0.
0
6
3
5

1
.
6
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
5

2
.
1
1

0
.
0
9
5
5

0

-

0
0
0-
0
0

0
.
0
9
5
5
2.
0
0

2
.
8
0
0.
0
0
2
5
4

0
.
0
9
8
0
2.
0

0
.
0
4
9

2
%
Pa
s
s
Co
y
o
t
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
1
0

1
1
.
5

0
.
5
2
3

0

-

0
0
0-
0
00
.
5
2
3
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
5
3
6
2.
0

0
.
2
7

0
%
Pa
s
s
Co
y
o
t
e
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
1
8

1
.
7
7

0
.
0
8
0
1

0

-

0
0
0-
0
00
.
0
8
0
1
1.
5
0

2
.
8
0
0.
0
0
1
9
0

0
.
0
8
2
0
9.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
2-
N
i
t
r
o
a
n
i
l
i
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
1
7

5
8
.
7

2
.
6
6

0

-

0
0
0-
0
02
.
6
6
50

2
.
8
0
0.
0
6
3
5

2
.
7
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
2-
N
i
t
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
2
0

1
2
.
6

0
.
5
7
0

0

-

0
0
0-
0
00
.
5
7
0
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
5
8
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
2-
N
i
t
r
o
t
o
l
u
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
7
1

0
.
0
5
2
0

0
.
0
0
2
3
6

0

-

0
0
0-
0
0

0
.
0
0
2
3
6
0.
1
4
0

2
.
8
0
0.
0
0
0
1
7
8

0
.
0
0
2
5
3
2.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
3-
N
i
t
r
o
a
n
i
l
i
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
3
8

6
8
.
9

3
.
1
2

0

-

0
0
0-
0
03
.
1
2
50

2
.
8
0
0.
0
6
3
5

3
.
1
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
3-
N
i
t
r
o
t
o
l
u
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
9
6
1

0
.
1
4
4

0
.
0
0
6
5
4

0

-

0
0
0-
0
0

0
.
0
0
6
5
4
0.
1
5
0

2
.
8
0
0.
0
0
0
1
9
0

0
.
0
0
6
7
3
2.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
2
7
3

1
3
.
7

0
.
6
1
9

0

-

0
0
0-
0
00
.
6
1
9
50

2
.
8
0
0.
0
6
3
5

0
.
6
8
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
4-
N
i
t
r
o
a
n
i
l
i
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
4
9

3
7
.
4

1
.
7
0

0

-

0
0
0-
0
01
.
7
0
50

2
.
8
0
0.
0
6
3
5

1
.
7
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
4-
N
i
t
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
5
0
1

2
5
.
1

1
.
1
4

0

-

0
0
0-
0
01
.
1
4
50

2
.
8
0
0.
0
6
3
5

1
.
2
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
4-
N
i
t
r
o
t
o
l
u
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
9
9
0

0
.
1
8
8

0
.
0
0
8
5
3

0

-

0
0
0-
0
0

0
.
0
0
8
5
3
0.
1
9
0

2
.
8
0
0.
0
0
0
2
4
1

0
.
0
0
8
7
7
2.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e

H
M
X

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

2
.
1
3

5
3
.
4

2
.
4
2

0

-

0
0
0-
0
02
.
4
2
25

2
.
8
0
0.
0
3
1
7

2
.
4
5
1.
0
2.
5
31
%
Re
t
a
i
n
Co
y
o
t
e
Ni
t
r
o
b
e
n
z
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
5
2
5

5
.
5
1

0
.
2
5
0

0

-

0
0
0-
0
00
.
2
5
0
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
2
6
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Ni
t
r
o
g
l
y
c
e
r
i
n
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
3
2

0
.
4
4
7

0
.
0
2
0
3

0

-

0
0
0-
0
00
.
0
2
0
3
0.
3
4
0

2
.
8
0
0.
0
0
0
4
3
2

0
.
0
2
0
7
3.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e

N
i
t
r
o
g
u
a
n
i
d
i
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

2
.
9
3

0
.
8
7
9

0
.
0
3
9
9

0

-

0
0
0-
0
0

0
.
0
3
9
9
0.
3
0
0

2
.
8
0
0.
0
0
0
3
8
1

0
.
0
4
0
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
PE
T
N
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
9
8
4

0
.
4
9
2

0
.
0
2
2
3

0

-

0
0
0-
0
00
.
0
2
2
3
0.
5
0
0

2
.
8
0
0.
0
0
0
6
3
5

0
.
0
2
2
9
17
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e

P
i
c
r
i
c

a
c
i
d

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
4
0

0
.
6
9
8

0
.
0
3
1
7

0

-

0
0
0-
0
0

0
.
0
3
1
7
0.
5
0
0

2
.
8
0
0.
0
0
0
6
3
5

0
.
0
3
2
3
NS
V
--
7%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
RD
X
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
1.
5
0

2
.
8
0
0.
0
0
1
9
0

0
.
0
0
1
9
0
2.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
Te
t
r
y
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
1
7

0
.
1
4
2

0
.
0
0
6
4
4

0

-

0
0
0-
0
0

0
.
0
0
6
4
4
0.
2
3
0

2
.
8
0
0.
0
0
0
2
9
2

0
.
0
0
6
7
3
1.
3

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
HI

-

E
n
e
r
g
e
t
i
c
s
2.
5
(d
e
t
s
)
Re
t
a
i
n
Co
y
o
t
e

A
l
u
m
i
n
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
7
3
2

3
9
5
0

1
7
9

0

-

0
0
0-
0
0

1
7
9
54
0
0
0

2
.
8
0
68
.
5

2
4
8
1.
9
13
0
10
0
%
Re
t
a
i
n
Co
y
o
t
e

A
n
t
i
m
o
n
y

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
0

1
6
7

7
.
5
7

0

-

0
0
0-
0
07
.
5
7
16
7

2
.
8
0
0.
2
1
2

7
.
7
8
0.
1
13
0
79
%
Re
t
a
i
n
Co
y
o
t
e

A
r
s
e
n
i
c

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
1
6
5

0
.
0
0
7
4
9

0

-

0
0
0-
0
0

0
.
0
0
7
4
9
41
.
3

2
.
8
0
0.
0
5
2
4

0
.
0
5
9
9
0.
4

0
.
1
5

5
8
%
Pa
s
s
Co
y
o
t
e

B
a
r
i
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
1
2

7
1
.
7

3
.
2
5

0

-

0
0
0-
0
03
.
2
5
64
0

2
.
8
0
0.
8
1
2

4
.
0
7
45
.
0

0
.
0
9
0

1
0
0
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
1

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Co
y
o
t
e

B
e
r
y
l
l
i
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
1
0

0
.
2
9
5

0
.
0
1
3
4

0

-

0
0
0-
0
0

0
.
0
1
3
4
0.
7
2
0

2
.
8
0
0.
0
0
0
9
1
4

0
.
0
1
4
3
0.
5

0
.
0
2
7

4
8
%
Pa
s
s
Co
y
o
t
e

C
a
d
m
i
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
6
1

0
.
1
6
3

0

-

0
0
0-
0
00
.
1
6
3
32

2
.
8
0
0.
0
4
0
6

0
.
2
0
4
0.
8

0
.
2
7

4
4
%
Pa
s
s
Co
y
o
t
e
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
1
2

0
.
0
0
1
2
3

0
.
0
0
0
0
5
5
7

0

-

0
0
0-
0
0

0
.
0
0
0
0
5
5
7
0.
0
0
1
1
0

2
.
8
0
0.
0
0
0
0
0
1
4
0

0
.
0
0
0
0
5
7
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e

C
h
r
o
m
i
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
3
3

1
8
.
4

0
.
8
3
6

0

-

0
0
0-
0
00
.
8
3
6
55
.
3

2
.
8
0
0.
0
7
0
2

0
.
9
0
6
3.
3

0
.
2
8

1
0
0
%
Pa
s
s
Co
y
o
t
e

C
o
b
a
l
t

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
0
9
1
7

0
.
0
0
4
1
6

0

-

0
0
0-
0
0

0
.
0
0
4
1
6
4.
9
0

2
.
8
0
0.
0
0
6
2
2

0
.
0
1
0
4
1.
1

<
0
.
0
1

7
9
%
Pa
s
s
Co
y
o
t
e

C
o
p
p
e
r

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
.
7

1
.
4
4

0

-

0
0
0-
0
01
.
4
4
18
0
0
0

2
.
8
0
22
.
8

2
4
.
3
11
.
7
2.
1
85
%
Re
t
a
i
n
Co
y
o
t
e

I
r
o
n

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
3
3

1
0
.
6

0

-

0
0
0-
0
01
0
.
6
15
0
0
0

2
.
8
0
19

2
9
.
6
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Co
y
o
t
e

L
e
a
d

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
7

5
.
7
5

0

-

0
0
0-
0
05
.
7
5
48
0
0
0

2
.
8
0
60
.
9

6
6
.
7
0.
9
72
83
%
Re
t
a
i
n
Co
y
o
t
e

M
a
g
n
e
s
i
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
9
9
2

2
4
1
0
0

1
0
9
0

0

-

0
0
0-
0
0

1
0
9
0
24
3
0
0

2
.
8
0
30
.
8

1
1
2
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Co
y
o
t
e

M
a
n
g
a
n
e
s
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
7
9
0

4
1

1
.
8
6

0

-

0
0
0-
0
01
.
8
6
51
9

2
.
8
0
0.
6
5
9

2
.
5
2
88
.
0

0
.
0
2
9

1
0
0
%
Pa
s
s
Co
y
o
t
e

M
e
r
c
u
r
y

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
9
2

0
.
0
1
3
4

0
.
0
0
0
6
0
9

0

-

0
0
0-
0
0

0
.
0
0
0
6
0
9
0.
0
7
0
0

2
.
8
0
0.
0
0
0
0
8
8
9

0
.
0
0
0
6
9
8
0.
0

0
.
0
2
2

2
7
%
Pa
s
s
Co
y
o
t
e

M
o
l
y
b
d
e
n
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
0

1
7

0
.
7
7
1

0

-

0
0
0-
0
00
.
7
7
1
17

2
.
8
0
0.
0
2
1
6

0
.
7
9
2
0.
3
3.
0
91
%
Re
t
a
i
n
Co
y
o
t
e

N
i
c
k
e
l

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
5
8
9

2
4
.
3

1
.
1
0

0

-

0
0
0-
0
01
.
1
0
41
.
3

2
.
8
0
0.
0
5
2
4

1
.
1
6
40
.
0

0
.
0
2
9

1
0
0
%
Pa
s
s
Co
y
o
t
e

N
i
t
r
a
t
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
0

2
2
.
8

1
.
0
3

0

-

0
0
0-
0
01
.
0
3
22
.
8

2
.
8
0
0.
0
2
8
9

1
.
0
6
50
7
.
0

<
0
.
0
1

9
2
%
Pa
s
s
Co
y
o
t
e

P
e
r
c
h
l
o
r
a
t
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
0
0

0
.
4
5
0

0
.
0
2
0
4

0

-

0
0
0-
0
0

0
.
0
2
0
4
4.
5
0

2
.
8
0
0.
0
0
5
7
1

0
.
0
2
6
1
2.
6

0
.
0
1
0

5
0
%
Pa
s
s
Co
y
o
t
e

P
h
o
s
p
h
o
r
u
s

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
0

9
9
0

4
4
.
9

0

-

0
0
0-
0
04
4
.
9
99
0

2
.
8
0
1.
2
6

4
6
.
1
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Se
l
e
n
i
u
m
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
2
1

0
.
0
5
4
8

0

-

0
0
0-
0
00
.
0
5
4
8
5.
0
0

2
.
8
0
0.
0
0
6
3
5

0
.
0
6
1
2
0.
2

0
.
3
1

0
%
Pa
s
s
Co
y
o
t
e

S
i
l
v
e
r

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
8
1
0

3
.
2
4

0
.
1
4
7

0

-

0
0
0-
0
00
.
1
4
7
4.
0
0

2
.
8
0
0.
0
0
5
0
8

0
.
1
5
2
2.
4

0
.
0
6
4

8
%
Pa
s
s
Co
y
o
t
e

S
t
r
o
n
t
i
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
0

4
8
4

2
1
.
9

0

-

0
0
0-
0
02
1
.
9
48
4

2
.
8
0
0.
6
1
4

2
2
.
6
26
3
.
0

0
.
0
8
6

1
0
0
%
Pa
s
s
Co
y
o
t
e

T
h
a
l
l
i
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
2
3

0
.
0
6
7
5

0
.
0
0
3
0
6

0

-

0
0
0-
0
0

0
.
0
0
3
0
6
0.
5
5
0

2
.
8
0
0.
0
0
0
6
9
8

0
.
0
0
3
7
6
0.
0

0
.
5
1

5
4
%
Pa
s
s
Co
y
o
t
e

V
a
n
a
d
i
u
m

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
1
9
5

0
.
5
0
0

0
.
0
2
2
7

0

-

0
0
0-
0
0

0
.
0
2
2
7
25
.
7

2
.
8
0
0.
0
3
2
6

0
.
0
5
5
3
0.
2

0
.
2
6

1
0
0
%
Pa
s
s
Co
y
o
t
e

Z
i
n
c

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
5
5

7
.
0
2

0

-

0
0
0-
0
0
7.02
23
0
0

2
.
8
0
2.
9
2

9
.
9
4
16
0
.
0

0
.
0
6
2

1
0
0
%
Pa
s
s
Co
y
o
t
e
HI

-

I
n
o
r
g
a
n
i
c
s
34
0
(d
e
t
s
)
Re
t
a
i
n
Co
y
o
t
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
2
9

1
0
7

4
.
8
5

0

-

0
0
0-
0
04
.
8
5
17
0

2
.
8
0
0.
2
1
6

5
.
0
6
5.
0
1.
0
14
%
Re
t
a
i
n
Co
y
o
t
e

A
c
e
n
a
p
h
t
h
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
0.
0
4
1
8

2
.
8
0
0.
0
0
0
0
5
3
1

0
.
0
0
0
0
5
3
1
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
Ac
e
n
a
p
h
t
h
y
l
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
17
5
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e

A
n
t
h
r
a
c
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
3.
7
0

2
.
8
0
0.
0
0
4
7
0

0
.
0
0
4
7
0
10
0
0
.
0

<
0
.
0
1

7
%
Pa
s
s
Co
y
o
t
e
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
1.
0

0
.
0
1
3

0
%
Pa
s
s
Co
y
o
t
e
Be
n
z
o
(
a
)
p
y
r
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
1.
0

0
.
0
1
3

0
%
Pa
s
s
Co
y
o
t
e
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
1.
0

0
.
0
1
3

0
%
Pa
s
s
Co
y
o
t
e
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
1.
0

0
.
0
1
3

0
%
Pa
s
s
Co
y
o
t
e
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
1.
0

0
.
0
1
3

0
%
Pa
s
s
Co
y
o
t
e
Ch
r
y
s
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
1.
0

0
.
0
1
3

0
%
Pa
s
s
Co
y
o
t
e
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
1.
0

0
.
0
1
3

0
%
Pa
s
s
Co
y
o
t
e

F
l
u
o
r
a
n
t
h
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
0.
1
4
4

2
.
8
0
0.
0
0
0
1
8
3

0
.
0
0
0
1
8
3
12
5
.
0

<
0
.
0
1

4
%
Pa
s
s
Co
y
o
t
e

F
l
u
o
r
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
33

2
.
8
0
0.
0
4
1
9

0
.
0
4
1
9
12
5
.
0

<
0
.
0
1

1
4
%
Pa
s
s
Co
y
o
t
e
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
1.
0

0
.
0
1
3

0
%
Pa
s
s
Co
y
o
t
e

N
a
p
h
t
h
a
l
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
53

2
.
8
0
0.
0
6
7
3

0
.
0
6
7
3
50
.
0

<
0
.
0
1

2
5
%
Pa
s
s
Co
y
o
t
e

P
h
e
n
a
n
t
h
r
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
92

2
.
8
0
0.
1
1
7

0
.
1
1
7
17
5
.
0

<
0
.
0
1

1
8
%
Pa
s
s
Co
y
o
t
e
Py
r
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
1
3
3
75
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
HI

-

P
A
H
s
1.
0
(d
e
t
s
)
Re
t
a
i
n
Co
y
o
t
e
TP
H
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

-

0

0

0

-

0
0
0-
0
00
47
0
0
0

2
.
8
0
59
.
7

5
9
.
7
10
0
0
.
0

0
.
0
6
0

1
0
0
%
Pa
s
s
Co
y
o
t
e
HI

-

P
e
t
r
o
l
e
u
m
0.
0
6
0
(d
e
t
s
)
Pa
s
s
Co
y
o
t
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
2
5

6
.
2
4

0
.
2
8
3

0

-

0
0
0-
0
00
.
2
8
3
50

2
.
8
0
0.
0
6
3
5

0
.
3
4
6
0.
2
1.
4
0%
Re
t
a
i
n
Co
y
o
t
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
1
1

1
.
1
7

0
.
0
5
2
9

0

-

0
0
0-
0
00
.
0
5
2
9
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
6
6
2
0.
2

0
.
2
8

0
%
Pa
s
s
Co
y
o
t
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
2
3
4

2
.
4
6

0
.
1
1
2

0

-

0
0
0-
0
00
.
1
1
2
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
1
2
5
0.
2

0
.
5
2

0
%
Pa
s
s
Co
y
o
t
e
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
2
5
1

2
.
6
4

0
.
1
2
0

0

-

0
0
0-
0
00
.
1
2
0
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
1
3
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
0
1

1
.
0
6

0
.
0
4
7
9

0

-

0
0
0-
0
00
.
0
4
7
9
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
6
1
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
2-
M
e
t
h
y
l
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
1
4

1
1
.
9

0
.
5
4
1

0

-

0
0
0-
0
00
.
5
4
1
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
5
5
4
34
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
7
5

1
4
.
2

0
.
6
4
2

0

-

0
0
0-
0
00
.
6
4
2
21

2
.
8
0
0.
0
2
6
7

0
.
6
6
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
2
0
1

2
.
1
1

0
.
0
9
5
6

0

-

0
0
0-
0
00
.
0
9
5
6
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
1
0
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
4-
C
h
l
o
r
o
a
n
i
l
i
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
5
3
3

5
.
6
0

0
.
2
5
4

0

-

0
0
0-
0
00
.
2
5
4
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
2
6
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
4-
M
e
t
h
y
l
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
9
4

5
.
1
9

0
.
2
3
5

0

-

0
0
0-
0
00
.
2
3
5
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
2
4
8
34
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
Be
n
z
o
i
c

a
c
i
d
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
5
1
7

2
5
.
9

1
.
1
7

0

-

0
0
0-
0
01
.
1
7
50

2
.
8
0
0.
0
6
3
5

1
.
2
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Be
n
z
y
l
a
l
c
o
h
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
9
3
5

9
.
8
2

0
.
4
4
5

0

-

0
0
0-
0
00
.
4
4
5
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
4
5
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
9
0

0
.
2
8
5

0
.
0
1
2
9

0

-

0
0
0-
0
0

0
.
0
1
2
9
1.
5
0

2
.
8
0
0.
0
0
1
9
0

0
.
0
1
4
8
18
.
3

<
0
.
0
1

1
8
%
Pa
s
s
Co
y
o
t
e
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
5
2
7

0
.
5
5
4

0
.
0
2
5
1

0

-

0
0
0-
0
00
.
0
2
5
1
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
3
8
4
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e

D
i
b
e
n
z
o
f
u
r
a
n

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
3
1

7
.
5
7

0
.
3
4
3

0

-

0
0
0-
0
00
.
3
4
3
12

2
.
8
0
0.
0
1
5
2

0
.
3
5
9
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
2
9

3
.
4
5

0
.
1
5
6

0

-

0
0
0-
0
00
.
1
5
6
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
1
7
0
45
8
3
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
5
6

6
.
8
9

0
.
3
1
2

0

-

0
0
0-
0
00
.
3
1
2
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
3
2
6
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
6
2
9

0
.
6
6
1

0
.
0
3
0
0

0

-

0
0
0-
0
00
.
0
3
0
0
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
4
3
3
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
8
1

4
.
0
0

0
.
1
8
1

0

-

0
0
0-
0
00
.
1
8
1
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
1
9
5
55
0
.
0

<
0
.
0
1

0
%
Pa
s
s
Co
y
o
t
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
3
9
1

0
.
4
1
0

0
.
0
1
8
6

0

-

0
0
0-
0
00
.
0
1
8
6
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
3
1
9
1.
6

0
.
0
2
0

0
%
Pa
s
s
Co
y
o
t
e
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
5
5
2

0
.
0
0
0
0
4
4
2

0
.
0
0
0
0
0
2
0
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
0
2
0
0
0.
0
0
0
8
0
0

2
.
8
0
0.
0
0
0
0
0
1
0
2

0
.
0
0
0
0
0
3
0
2
1.
6

<
0
.
0
1

4
%
Pa
s
s
Co
y
o
t
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
0
1

1
.
0
6

0
.
0
4
7
9

0

-

0
0
0-
0
00
.
0
4
7
9
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
6
1
2
1.
6

0
.
0
3
8

0
%
Pa
s
s
Co
y
o
t
e
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
6
3
4

0
.
6
6
6

0
.
0
3
0
2

0

-

0
0
0-
0
00
.
0
3
0
2
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
4
3
5
1.
6

0
.
0
2
7

0
%
Pa
s
s
Co
y
o
t
e
Is
o
p
h
o
r
o
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
8
3

4
.
0
2

0
.
1
8
2

0

-

0
0
0-
0
00
.
1
8
2
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
1
9
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
9
3

7
.
2
7

0
.
3
3
0

0

-

0
0
0-
0
00
.
3
3
0
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
3
4
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
9
6

2
.
0
6

0
.
0
9
3
4

0

-

0
0
0-
0
00
.
0
9
3
4
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
1
0
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
4
6
6

2
.
3
3

0
.
1
0
6

0

-

0
0
0-
0
00
.
1
0
6
50

2
.
8
0
0.
0
6
3
5

0
.
1
6
9
0.
2

0
.
7
0

0
%
Pa
s
s
Co
y
o
t
e
HI

-

S
V
O
C
s
<0
.
0
1

(
d
e
t
s
)
Pa
s
s
Co
y
o
t
e
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
9
2

0
.
0
0
0
4
7
5

0
.
0
0
0
0
2
1
5

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
1
5
0.
0
0
0
6
0
0

2
.
8
0
0.
0
0
0
0
0
0
7
6
2

0
.
0
0
0
0
2
2
3
1.
4

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
1
9

0
.
0
0
0
2
8
7

0
.
0
0
0
0
1
3
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
3
0
0.
0
0
0
9
0
0

2
.
8
0
0.
0
0
0
0
0
1
1
4

0
.
0
0
0
0
1
4
1
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
4
7

0
.
0
0
0
3
4
7

0
.
0
0
0
0
1
5
7

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
5
7
0.
0
0
1
0
0

2
.
8
0
0.
0
0
0
0
0
1
2
7

0
.
0
0
0
0
1
7
0
1.
4

<
0
.
0
1

5
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
2

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Co
y
o
t
e
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
2
6

0
.
0
0
0
2
6
1

0
.
0
0
0
0
1
1
8

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
1
8
0.
0
0
0
8
0
0

2
.
8
0
0.
0
0
0
0
0
1
0
2

0
.
0
0
0
0
1
2
8
10
0
0
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
5
5
0

0
.
0
0
0
3
8
5

0
.
0
0
0
0
1
7
5

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
7
5
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
1
8
3
50
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
7

0
.
0
0
1
1
8

0
.
0
0
0
0
5
3
3

0

-

0
0
0-
0
0

0
.
0
0
0
0
5
3
3
0.
0
0
1
1
0

2
.
8
0
0.
0
0
0
0
0
1
4
0

0
.
0
0
0
0
5
4
7
2.
5

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
5
6
3

0
.
0
0
1
5
8

0
.
0
0
0
0
7
1
5

0

-

0
0
0-
0
0

0
.
0
0
0
0
7
1
5
0.
0
0
2
8
0

2
.
8
0
0.
0
0
0
0
0
3
5
5

0
.
0
0
0
0
7
5
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
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9
4
5

0
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0
0
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8
5
1

0
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0
0
0
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8
6

0

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0
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0
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0
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8
6
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2
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8
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0
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1
4

0
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0
0
0
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9
7
10
0
0
.
0

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0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
1,
2
,
4
-
T
r
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c
h
l
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r
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b
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e
10
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3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
7
9
8

0
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0
0
0
2
5
5

0
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0
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1
6

0

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0
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0
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0
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1
6
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0
0
3
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2
.
8
0
0.
0
0
0
0
0
4
0
6

0
.
0
0
0
0
1
5
6
NS
V
--
4%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
1,
2
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D
i
b
r
o
m
o
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3
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c
h
l
o
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o
p
r
o
p
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
7
4

0
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0
0
1
4
6

0
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0
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6
2

0

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0
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0
0

0
.
0
0
0
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6
6
2
0.
0
0
3
9
0

2
.
8
0
0.
0
0
0
0
0
4
9
5

0
.
0
0
0
0
7
1
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
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n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
0
5

0
.
0
0
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9
8
6

0
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0
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4
7

0

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0
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0
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0
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4
4
7
0.
0
0
1
4
0

2
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8
0
0.
0
0
0
0
0
1
7
8

0
.
0
0
0
0
4
6
5
NS
V
--
4%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
1,
2
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D
i
c
h
l
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r
o
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t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
9
8

0
.
0
0
0
5
5
8

0
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0
0
0
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2
5
3

0

-

0
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0
0

0
.
0
0
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5
3
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0
0
0
8
0
0

2
.
8
0
0.
0
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0
0
0
1
0
2

0
.
0
0
0
0
2
6
3
50
.
0

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0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
1,
2
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D
i
c
h
l
o
r
o
p
r
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p
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
6
8

0
.
0
0
0
3
2
8

0
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0
0
0
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4
9

0

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0
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0
.
0
0
0
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4
9
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
1
5
7
50
.
0

<
0
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0
1

5
%
Pa
s
s
Co
y
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t
e
1,
2
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E
t
h
y
l
e
n
e

D
i
b
r
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m
i
d
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
2
1

0
.
0
0
1
0
9

0
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0
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0
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4
9
4

0

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0
0
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0

0
.
0
0
0
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4
9
4
0.
0
0
0
9
0
0

2
.
8
0
0.
0
0
0
0
0
1
1
4

0
.
0
0
0
0
5
0
5
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
1,
3
-
D
i
c
h
l
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r
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b
e
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z
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n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
3
7

0
.
0
0
0
2
6
0

0
.
0
0
0
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1
1
8

0

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0
0
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0
0

0
.
0
0
0
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1
1
8
0.
0
0
1
9
0

2
.
8
0
0.
0
0
0
0
0
2
4
1

0
.
0
0
0
0
1
4
2
NS
V
--
4%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
3
7

0
.
0
0
0
4
2
4

0
.
0
0
0
0
1
9
2

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
9
2
0.
0
0
3
1
0

2
.
8
0
0.
0
0
0
0
0
3
9
4

0
.
0
0
0
0
2
3
2
NS
V
--
4%
Un
c
e
r
t
a
i
n
Co
y
o
t
e

2
-
B
u
t
a
n
o
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e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
9
8

0
.
0
3
1
4

0
.
0
0
1
4
2

0

-

0
0
0-
0
0

0
.
0
0
1
4
2
0.
0
1
5
9

2
.
8
0
0.
0
0
0
0
2
0
2

0
.
0
0
1
4
5
10
.
0

<
0
.
0
1

1
8
%
Pa
s
s
Co
y
o
t
e
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
4
7

0
.
0
0
8
7
7

0
.
0
0
0
3
9
7

0

-

0
0
0-
0
0

0
.
0
0
0
3
9
7
0.
0
0
5
9
5

2
.
8
0
0.
0
0
0
0
0
7
5
5

0
.
0
0
0
4
0
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
2-
C
h
l
o
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
0
8

4
.
2
8

0
.
1
9
4

0

-

0
0
0-
0
00
.
1
9
4
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
2
0
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
2-
H
e
x
a
n
o
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
3
7

0
.
0
0
5
2
2

0
.
0
0
0
2
3
7

0

-

0
0
0-
0
0

0
.
0
0
0
2
3
7
0.
0
0
3
8
0

2
.
8
0
0.
0
0
0
0
0
4
8
2

0
.
0
0
0
2
4
1
10
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
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r
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
1
0

4
.
3
1

0
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1
9
5

0

-

0
0
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0
00
.
1
9
5
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
2
0
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
4-
C
h
l
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o
p
h
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n
y
l
p
h
e
n
y
l
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t
h
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r
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
0
9
4
6

0
.
9
9
4

0
.
0
4
5
1

0

-

0
0
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0
00
.
0
4
5
1
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
0
5
8
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
4
6

0
.
0
0
6
2
9

0
.
0
0
0
2
8
5

0

-

0
0
0-
0
0

0
.
0
0
0
2
8
5
0.
0
0
4
3
0

2
.
8
0
0.
0
0
0
0
0
5
4
6

0
.
0
0
0
2
9
1
25
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e

A
c
e
t
o
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

2
.
3
6

5
6
.
6

2
.
5
7

0

-

0
0
0-
0
02
.
5
7
24

2
.
8
0
0.
0
3
0
5

2
.
6
0
10
.
0

0
.
2
6

3
2
%
Pa
s
s
Co
y
o
t
e

B
e
n
z
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
7

0
.
0
0
4
3
8

0
.
0
0
0
1
9
9

0

-

0
0
0-
0
0

0
.
0
0
0
1
9
9
0.
0
0
4
1
0

2
.
8
0
0.
0
0
0
0
0
5
2
0

0
.
0
0
0
2
0
4
0.
7

<
0
.
0
1

1
4
%
Pa
s
s
Co
y
o
t
e
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
4
1

0
.
1
0
4

0
.
0
0
4
7
3

0

-

0
0
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0
0

0
.
0
0
4
7
3
0.
0
7
4
0

2
.
8
0
0.
0
0
0
0
9
3
9

0
.
0
0
4
8
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
8
8

7
.
2
2

0
.
3
2
7

0

-

0
0
0-
0
00
.
3
2
7
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
3
4
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
bi
s
(
2
-
c
h
l
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r
o
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s
o
p
r
o
p
y
l
)
e
t
h
e
r
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
3
3

4
.
5
5

0
.
2
0
6

0

-

0
0
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0
00
.
2
0
6
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
2
2
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
8

0
.
0
0
0
7
5
6

0
.
0
0
0
0
3
4
3

0

-

0
0
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0
0

0
.
0
0
0
0
3
4
3
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
3
5
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
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t
e
Br
o
m
o
f
o
r
m
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
4
4

0
.
0
0
0
1
7
2

0
.
0
0
0
0
0
7
8
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
0
7
8
0
0.
0
0
0
5
0
0

2
.
8
0
0.
0
0
0
0
0
0
6
3
5

0
.
0
0
0
0
0
8
4
4
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Br
o
m
o
m
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
4
6

0
.
0
0
2
2
0

0
.
0
0
0
0
9
9
5

0

-

0
0
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0
0

0
.
0
0
0
0
9
9
5
0.
0
0
1
5
0

2
.
8
0
0.
0
0
0
0
0
1
9
0

0
.
0
0
0
1
0
1
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Ca
r
b
o
n

t
e
t
r
a
c
h
l
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r
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d
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
8
4
7

0
.
0
0
0
7
6
2

0
.
0
0
0
0
3
4
5

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
4
5
0.
0
0
0
9
0
0

2
.
8
0
0.
0
0
0
0
0
1
1
4

0
.
0
0
0
0
3
5
7
16
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Ch
l
o
r
o
b
e
n
z
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
2
4
5

0
.
0
0
0
1
7
2

0
.
0
0
0
0
0
7
7
9

0

-

0
0
0-
0
0

0
.
0
0
0
0
0
7
7
9
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
0
8
6
7
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Ch
l
o
r
o
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
2
6

0
.
0
0
0
7
2
6

0
.
0
0
0
0
3
2
9

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
2
9
0.
0
0
1
0
0

2
.
8
0
0.
0
0
0
0
0
1
2
7

0
.
0
0
0
0
3
4
2
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Ch
l
o
r
o
f
o
r
m
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
7
9

0
.
0
0
0
3
3
5

0
.
0
0
0
0
1
5
2

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
5
2
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
1
6
1
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Ch
l
o
r
o
m
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
5

0
.
0
0
1
0
5

0
.
0
0
0
0
4
7
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
4
7
6
0.
0
0
1
0
0

2
.
8
0
0.
0
0
0
0
0
1
2
7

0
.
0
0
0
0
4
8
8
15
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
1
7

0
.
0
0
0
8
1
9

0
.
0
0
0
0
3
7
1

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
7
1
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
3
8
0
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
0
1

0
.
0
0
0
6
0
8

0
.
0
0
0
0
2
7
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
7
6
0.
0
0
0
6
0
0

2
.
8
0
0.
0
0
0
0
0
0
7
6
2

0
.
0
0
0
0
2
8
3
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
3
7

0
.
0
0
0
3
0
6

0
.
0
0
0
0
1
3
9

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
3
9
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
1
4
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Di
b
r
o
m
o
m
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
2
7

0
.
0
0
0
6
3
4

0
.
0
0
0
0
2
8
7

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
8
7
0.
0
0
0
5
0
0

2
.
8
0
0.
0
0
0
0
0
0
6
3
5

0
.
0
0
0
0
2
9
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
1
4

0
.
0
0
0
4
5
5

0
.
0
0
0
0
2
0
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
0
6
0.
0
0
1
1
0

2
.
8
0
0.
0
0
0
0
0
1
4
0

0
.
0
0
0
0
2
2
0
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Et
h
y
l
b
e
n
z
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
1
9
3

0
.
0
0
0
2
5
1

0
.
0
0
0
0
1
1
4

0

-

0
0
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0
0

0
.
0
0
0
0
1
1
4
0.
0
0
1
3
0

2
.
8
0
0.
0
0
0
0
0
1
6
5

0
.
0
0
0
0
1
3
1
97
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
m,
p
-
X
y
l
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
4
8

0
.
0
0
1
5
0

0
.
0
0
0
0
6
7
8

0

-

0
0
0-
0
0

0
.
0
0
0
0
6
7
8
0.
0
0
2
0
0

2
.
8
0
0.
0
0
0
0
0
2
5
4

0
.
0
0
0
0
7
0
4
17
9
.
0

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
8
3
3

0
.
0
0
2
6
6

0
.
0
0
0
1
2
1

0

-

0
0
0-
0
0

0
.
0
0
0
1
2
1
0.
0
0
3
2
0

2
.
8
0
0.
0
0
0
0
0
4
0
6

0
.
0
0
0
1
2
5
5.
9

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e

o
-
X
y
l
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
7
4

0
.
0
0
2
0
9

0
.
0
0
0
0
9
4
7

0

-

0
0
0-
0
0

0
.
0
0
0
0
9
4
7
0.
0
0
2
7
0

2
.
8
0
0.
0
0
0
0
0
3
4
3

0
.
0
0
0
0
9
8
1
17
9
.
0

<
0
.
0
1

1
4
%
Pa
s
s
Co
y
o
t
e
Ph
e
n
o
l
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
0
9

7
.
4
5

0
.
3
3
8

0

-

0
0
0-
0
00
.
3
3
8
10
.
5

2
.
8
0
0.
0
1
3
3

0
.
3
5
1
17
.
1

0
.
0
2
1

0
%
Pa
s
s
Co
y
o
t
e

S
t
y
r
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
8
2
7

0
.
0
0
2
1
5

0
.
0
0
0
0
9
7
5

0

-

0
0
0-
0
0

0
.
0
0
0
0
9
7
5
0.
0
0
2
6
0

2
.
8
0
0.
0
0
0
0
0
3
3
0

0
.
0
0
0
1
0
1
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
4
4

0
.
0
0
1
0
1

0
.
0
0
0
0
4
5
7

0

-

0
0
0-
0
0

0
.
0
0
0
0
4
5
7
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
4
6
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
0
0

0
.
0
0
0
6
3
0

0
.
0
0
0
0
2
8
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
8
6
0.
0
0
0
9
0
0

2
.
8
0
0.
0
0
0
0
0
1
1
4

0
.
0
0
0
0
2
9
7
1.
4

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e

T
o
l
u
e
n
e

1
0
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
8
7
5

0
.
0
1
6
4

0
.
0
0
0
7
4
2

0

-

0
0
0-
0
0

0
.
0
0
0
7
4
2
0.
0
1
8
7

2
.
8
0
0.
0
0
0
0
2
3
7

0
.
0
0
0
7
6
6
52
.
0

<
0
.
0
1

2
3
%
Pa
s
s
Co
y
o
t
e
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
6
9
8

0
.
0
0
0
4
8
9

0
.
0
0
0
0
2
2
2

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
2
2
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
2
3
0
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
4
6
8

0
.
0
0
0
3
7
4

0
.
0
0
0
0
1
7
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
7
0
0.
0
0
0
8
0
0

2
.
8
0
0.
0
0
0
0
0
1
0
2

0
.
0
0
0
0
1
8
0
45
.
2

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
3
9

0
.
0
0
0
2
3
7

0
.
0
0
0
0
1
0
8

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
0
8
0.
0
0
0
7
0
0

2
.
8
0
0.
0
0
0
0
0
0
8
8
9

0
.
0
0
0
0
1
1
6
0.
7

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
3
1
1

0
.
0
0
0
3
4
2

0
.
0
0
0
0
1
5
5

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
5
5
0.
0
0
1
1
0

2
.
8
0
0.
0
0
0
0
0
1
4
0

0
.
0
0
0
0
1
6
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Vi
n
y
l

A
c
e
t
a
t
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

1
.
5
2

0
.
0
0
1
8
2

0
.
0
0
0
0
8
2
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
8
2
6
0.
0
0
1
2
0

2
.
8
0
0.
0
0
0
0
0
1
5
2

0
.
0
0
0
0
8
4
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Co
y
o
t
e
Vi
n
y
l

c
h
l
o
r
i
d
e
10
.
3
3
0

0
.
0
4
5

1

0
.
0
4
5

1
0
0

0
.
7
5
4

0
.
0
0
0
9
0
4

0
.
0
0
0
0
4
1
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
4
1
0
0.
0
0
1
2
0

2
.
8
0
0.
0
0
0
0
0
1
5
2

0
.
0
0
0
0
4
2
5
0.
2

<
0
.
0
1

5
%
Pa
s
s
Co
y
o
t
e
HI

-

V
O
C
s
0.
2
8
(d
e
t
s
)
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
.
7
8

0
.
5
0
2
0.
0
1
2
8

0
.
0
1
2
8
0.
1
0
5

2
.
0
0
0.
0
0
0
0
5
3
6

0
.
0
1
2
9
00
.
1
8
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
5

1
.
2
0
0.
0
3
0
6

0
.
0
3
0
6
0.
0
8
0
0

2
.
0
0
0.
0
0
0
0
4
0
8

0
.
0
3
0
7
0

0
.
0
7
3

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
.
2
3

6
.
3
4
0.
1
6
2

0
.
1
6
2
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
1
6
3
0
2.
3
0%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
4
0

1
2
0
3.
0
6

3
.
0
6
50

2
.
0
0
0.
0
2
5
5

3
.
0
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
6
0
7

1
.
2
1
0.
0
3
1
0

0
.
0
3
1
0
2.
0
0

2
.
0
0
0.
0
0
1
0
2

0
.
0
3
2
0
00
.
4
6
2
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
1

1
1
6
2.
9
5

2
.
9
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

2
.
9
5
0
42
0%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
.
7
2
0.
0
6
9
4

0
.
0
6
9
4
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
0
7
0
1
0
1.
0
0%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
0
.
7

5
3
6
13
.
7

1
3
.
7
50

2
.
0
0
0.
0
2
5
5

1
3
.
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
N
i
t
r
o
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
1
.
3

1
1
9
3.
0
4

3
.
0
4
10
.
5

2
.
0
0
0.
0
0
5
3
6

3
.
0
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
4
2
8

0
.
0
5
9
9
0.
0
0
1
5
3

0
.
0
0
1
5
3
0.
1
4
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
0
0
1
6
0
0

0
.
0
2
3

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
3-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
6
.
8

8
4
0
21
.
4

2
1
.
4
50

2
.
0
0
0.
0
2
5
5

2
1
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

6
.
1
2

0
.
9
1
9
0.
0
2
3
4

0
.
0
2
3
4
0.
1
5
0

2
.
0
0
0.
0
0
0
0
7
6
5

0
.
0
2
3
5
00
.
3
4
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
1
8
2

9
.
0
8
0.
2
3
2

0
.
2
3
2
50

2
.
0
0
0.
0
2
5
5

0
.
2
5
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
4-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
0
4

1
5
2
3.
8
8

3
.
8
8
50

2
.
0
0
0.
0
2
5
5

3
.
9
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
4-
N
i
t
r
o
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
9
9
2

4
9
.
6
1.
2
7

1
.
2
7
50

2
.
0
0
0.
0
2
5
5

1
.
2
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

6
.
6
6

1
.
2
7
0.
0
3
2
3

0
.
0
3
2
3
0.
1
9
0

2
.
0
0
0.
0
0
0
0
9
7
0

0
.
0
3
2
4
00
.
4
6
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

H
M
X

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
7
2.
2
4

2
.
2
4
25

2
.
0
0
0.
0
1
2
8

2
.
2
5
9

0
.
2
5

3
1
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Ni
t
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
1
3

1
1
.
9
0.
3
0
3

0
.
3
0
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
3
0
8
0
4.
4
0%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Ni
t
r
o
g
l
y
c
e
r
i
n
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
4
.
7

5
.
0
1
0.
1
2
8

0
.
1
2
8
0.
3
4
0

2
.
0
0
0.
0
0
0
1
7
3

0
.
1
2
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

N
i
t
r
o
g
u
a
n
i
d
i
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
3
9

4
1
.
6
1.
0
6

1
.
0
6
0.
3
0
0

2
.
0
0
0.
0
0
0
1
5
3

1
.
0
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
3

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Sa
g
e

S
p
a
r
r
o
w
PE
T
N
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

6
.
5
4

3
.
2
7
0.
0
8
3
4

0
.
0
8
3
4
0.
5
0
0

2
.
0
0
0.
0
0
0
2
5
5

0
.
0
8
3
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

P
i
c
r
i
c

a
c
i
d

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
7
.
4

8
.
7
2
0.
2
2
2

0
.
2
2
2
0.
5
0
0

2
.
0
0
0.
0
0
0
2
5
5

0
.
2
2
3
NS
V
--
7%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
RD
X
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
0.
9
6
0

0
.
9
6
0
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
9
6
1
0
14
0%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Te
t
r
y
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
7
8

0
.
4
0
8
0.
0
1
0
4

0
.
0
1
0
4
0.
2
3
0

2
.
0
0
0.
0
0
0
1
1
7

0
.
0
1
0
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
HI

-

E
n
e
r
g
e
t
i
c
s
0.
7
1
(d
e
t
s
)
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

A
l
u
m
i
n
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
4
0
0

2
1
6
5.
5
1

5
.
5
1
54
0
0
0

2
.
0
0
27
.
6

3
3
.
1
11
0

0
.
3
0

1
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

A
n
t
i
m
o
n
y

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
5
0
0

8
.
3
5
0.
2
1
3

0
.
2
1
3
16
7

2
.
0
0
0.
0
8
5
2

0
.
2
9
8
NS
V
--
79
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

A
r
s
e
n
i
c

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
1
1
0.
0
2
8
4

0
.
0
2
8
4
41
.
3

2
.
0
0
0.
0
2
1
1

0
.
0
4
9
5
9

<
0
.
0
1

5
8
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

B
a
r
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
1
0
0

6
4
1.
6
3

1
.
6
3
64
0

2
.
0
0
0.
3
2
7

1
.
9
6
21

0
.
0
9
4

1
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

B
e
r
y
l
l
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

0
.
0
0
7
2
0
0.
0
0
0
1
8
4

0
.
0
0
0
1
8
4
0.
7
2
0

2
.
0
0
0.
0
0
0
3
6
7

0
.
0
0
0
5
5
1
NS
V
--
48
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

C
a
d
m
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
.
1
2
0.
1
0
5

0
.
1
0
5
32

2
.
0
0
0.
0
1
6
3

0
.
1
2
1
0

0
.
7
6

4
4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

9
.
3
2

0
.
0
1
0
3
0.
0
0
0
2
6
2

0
.
0
0
0
2
6
2
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
5
6
1

0
.
0
0
0
2
6
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

C
h
r
o
m
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
4
0
0

2
.
2
1
0.
0
5
6
4

0
.
0
5
6
4
55
.
3

2
.
0
0
0.
0
2
8
2

0
.
0
8
4
7
1

0
.
0
8
5

1
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

C
o
b
a
l
t

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
5
4
0

0
.
2
6
5
0.
0
0
6
7
5

0
.
0
0
6
7
5
4.
9
0

2
.
0
0
0.
0
0
2
5
0

0
.
0
0
9
2
5
8

<
0
.
0
1

7
9
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

C
o
p
p
e
r

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

9
2
.
7
2.
3
7

2
.
3
7
18
0
0
0

2
.
0
0
9.
1
8

1
1
.
6
47

0
.
2
5

8
5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

I
r
o
n

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
0

1
5
0
3.
8
3

3
.
8
3
15
0
0
0

2
.
0
0
7.
6
5

1
1
.
5
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

L
e
a
d

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
1
2
2.
8
6

2
.
8
6
48
0
0
0

2
.
0
0
24
.
5

2
7
.
4
0
14
0
83
%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

M
a
g
n
e
s
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
0
6

5
0
1
0
0
12
8
0

1
2
8
0
24
3
0
0

2
.
0
0
12
.
4

1
2
9
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

M
a
n
g
a
n
e
s
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
6
8
0

3
5
3
9.
0
0

9
.
0
0
51
9

2
.
0
0
0.
2
6
5

9
.
2
7
97
7

<
0
.
0
1

1
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

M
e
r
c
u
r
y

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
0
8
6
9
0.
0
0
2
2
2

0
.
0
0
2
2
2
0.
0
7
0
0

2
.
0
0
0.
0
0
0
0
3
5
7

0
.
0
0
2
2
5
0

0
.
0
3
3

2
7
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

M
o
l
y
b
d
e
n
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

6
.
8
0
0.
1
7
3

0
.
1
7
3
17

2
.
0
0
0.
0
0
8
6
7

0
.
1
8
2
40
.
0
5
2
9
1
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

N
i
c
k
e
l

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
7
5
0.
0
4
4
6

0
.
0
4
4
6
41
.
3

2
.
0
0
0.
0
2
1
1

0
.
0
6
5
7
18

<
0
.
0
1

1
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

N
i
t
r
a
t
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
0
0

2
2
.
8
0.
5
8
2

0
.
5
8
2
22
.
8

2
.
0
0
0.
0
1
1
6

0
.
5
9
3
NS
V
--
92
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

P
e
r
c
h
l
o
r
a
t
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
8
2

1
2
7
0
32
.
4

3
2
.
4
4.
5
0

2
.
0
0
0.
0
0
2
3
0

3
2
.
4
3
9.
9
50
%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

P
h
o
s
p
h
o
r
u
s

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
0
0

9
9
0
25
.
3

2
5
.
3
99
0

2
.
0
0
0.
5
0
5

2
5
.
8
0
70
0
10
0
%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Se
l
e
n
i
u
m
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
0
7
6
6

0
.
0
7
6
6
5.
0
0

2
.
0
0
0.
0
0
2
5
5

0
.
0
7
9
1
00
.
2
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

S
i
l
v
e
r

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
0
0

4
.
0
0
0.
1
0
2

0
.
1
0
2
4.
0
0

2
.
0
0
0.
0
0
2
0
4

0
.
1
0
4
NS
V
--
8%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

S
t
r
o
n
t
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
1
0

5
3
2
13
.
6

1
3
.
6
48
4

2
.
0
0
0.
2
4
7

1
3
.
8
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

T
h
a
ll
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
4
0
0

0
.
0
0
2
2
0
0.
0
0
0
0
5
6
1

0
.
0
0
0
0
5
6
1
0.
5
5
0

2
.
0
0
0.
0
0
0
2
8
1

0
.
0
0
0
3
3
7
1

<
0
.
0
1

5
4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

V
a
n
a
d
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
5
0

0
.
1
4
1
0.
0
0
3
6
1

0
.
0
0
3
6
1
25
.
7

2
.
0
0
0.
0
1
3
1

0
.
0
1
6
7
11

<
0
.
0
1

1
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

Z
i
n
c

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
5
5
9.05
9.05
23
0
0

2
.
0
0
1.
1
7

1
0
.
2
15

0
.
7
0

1
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
HI

-

I
n
o
r
g
a
n
i
c
s
85
0
(d
e
t
s
)
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
8
7

3
1
8
8.
1
1

8
.
1
1
17
0

2
.
0
0
0.
0
8
6
7

8
.
2
0
27

0
.
3
0

1
4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

A
c
e
n
a
p
h
t
h
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
7
.
2
0.
4
4
0

0
.
4
4
0
0.
0
4
1
8

2
.
0
0
0.
0
0
0
0
2
1
4

0
.
4
4
0
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Ac
e
n
a
p
h
t
h
y
l
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
0
.
2
0.
5
1
4

0
.
5
1
4
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
5
2
0
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

A
n
t
h
r
a
c
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
1
9
0

0
.
1
9
0
3.
7
0

2
.
0
0
0.
0
0
1
8
9

0
.
1
9
2
32
5

<
0
.
0
1

7
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
2
0
9

0
.
2
0
9
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
2
1
5
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
.
5
0.
2
6
9

0
.
2
6
9
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
2
7
4
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
3
1
0

3
.
2
6
0.
0
8
3
0

0
.
0
8
3
0
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
8
8
4
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
1.
0
5

1
.
0
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

1
.
0
5
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
8
4
0.
2
2
5

0
.
2
2
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
2
3
1
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Ch
r
y
s
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
2
1
0.
2
0
9

0
.
2
0
9
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
2
1
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
1
3
0

1
.
3
6
0.
0
3
4
8

0
.
0
3
4
8
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
4
0
2
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
1
8
4

0
.
0
0
1
8
4
0.
1
4
4

2
.
0
0
0.
0
0
0
0
7
3
5

0
.
0
0
1
9
1
32
5

<
0
.
0
1

4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

F
l
u
o
r
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
1
9
0
13
2

1
3
2
33

2
.
0
0
0.
0
1
6
8

1
3
2
32
5

0
.
4
1

1
4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
1
1
0

1
.
1
6
0.
0
2
9
5

0
.
0
2
9
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
3
4
8
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

N
a
p
h
t
h
a
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
2
.
2

6
4
7
16
.
5

1
6
.
5
53

2
.
0
0
0.
0
2
7
0

1
6
.
5
27

0
.
6
1

2
5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
9
.
5
0.
4
9
8

0
.
4
9
8
92

2
.
0
0
0.
0
4
6
9

0
.
5
4
5
32
5

<
0
.
0
1

1
8
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Py
r
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
7
2
0

7
.
5
6
0.
1
9
3

0
.
1
9
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
1
9
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
HI

-

P
A
H
s
1.
3
(d
e
t
s
)
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
TP
H
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

-

0
00
47
0
0
0

2
.
0
0
24

2
4
50
0

0
.
0
4
8

1
0
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
HI

-

P
e
t
r
o
l
e
u
m
0.
0
4
8
(d
e
t
s
)
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
2
0
2

1
.
0
1
0.
0
2
5
8

0
.
0
2
5
8
50

2
.
0
0
0.
0
2
5
5

0
.
0
5
1
3
17

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
7

0
.
1
5
4
0.
0
0
3
9
3

0
.
0
0
3
9
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
0
9
2
8
17

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
1
1
8

1
.
2
4
0.
0
3
1
6

0
.
0
3
1
6
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
3
7
0
17

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
1
4
3

1
.
5
0
0.
0
3
8
3

0
.
0
3
8
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
4
3
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
.
1
1
6
0.
0
0
2
9
7

0
.
0
0
2
9
7
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
0
8
3
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
M
e
t
h
y
l
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

9
.
7
7

1
0
3
2.
6
2

2
.
6
2
10
.
5

2
.
0
0
0.
0
0
5
3
6

2
.
6
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
2
8

4
7
.
8
1.
2
2

1
.
2
2
21

2
.
0
0
0.
0
1
0
7

1
.
2
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
7
6
7

0
.
8
0
5
0.
0
2
0
5

0
.
0
2
0
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
2
5
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
4-
C
h
l
o
r
o
a
n
i
l
i
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
1
8

1
2
.
4
0.
3
1
6

0
.
3
1
6
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
3
2
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
4-
M
e
t
h
y
l
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
9
5
1

9
.
9
8
0.
2
5
5

0
.
2
5
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
2
6
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Be
n
z
o
i
c

a
c
i
d
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
0
8

5
4
.
1
1.
3
8

1
.
3
8
50

2
.
0
0
0.
0
2
5
5

1
.
4
1
32
5

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Be
n
z
y
l
a
l
c
o
h
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

5
.
6
7

5
9
.
5
1.
5
2

1
.
5
2
10
.
5

2
.
0
0
0.
0
0
5
3
6

1
.
5
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
6
6
0

0
.
0
9
9
0
0.
0
0
2
5
2

0
.
0
0
2
5
2
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
0
0
3
2
9
1

<
0
.
0
1

1
8
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
1
8
2

0
.
0
1
9
1
0.
0
0
0
4
8
7

0
.
0
0
0
4
8
7
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
0
5
8
4
0

0
.
0
5
3

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

D
i
b
e
n
z
o
f
u
r
a
n

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
8
9

2
2
.
6
0.
5
7
8

0
.
5
7
8
12

2
.
0
0
0.
0
0
6
1
2

0
.
5
8
4
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
3
0
4

3
.
2
0
0.
0
8
1
6

0
.
0
8
1
6
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
8
6
9
00
.
7
9
0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
1
1

2
2
.
1
0.
5
6
5

0
.
5
6
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
5
7
0
0
5.
2
0%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
2
9
8

0
.
0
3
1
3
0.
0
0
0
8
0
0

0
.
0
0
0
8
0
0
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
0
6
1
6
0

0
.
0
5
6

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
4
6
1

4
.
8
4
0.
1
2
3

0
.
1
2
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
1
2
9
0
1.
2
0%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
0
7
8
5

0
.
0
0
8
2
4
0.
0
0
0
2
1
0

0
.
0
0
0
2
1
0
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
0
5
5
7
1

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
2
0
7

#
#
#
#
#
#
#
#
#
0.
0
0
0
0
0
0
0
4
2
2

0
.
0
0
0
0
0
0
0
4
2
2
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
0
8

0
.
0
0
0
0
0
0
4
5
0
1

<
0
.
0
1

4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
1
1
1

0
.
1
1
6
0.
0
0
2
9
7

0
.
0
0
2
9
7
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
0
8
3
2
1

0
.
0
1
5

0
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
4

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Sa
g
e

S
p
a
r
r
o
w
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x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
3
0
5

0
.
0
3
2
0
0.
0
0
0
8
1
6

0
.
0
0
0
8
1
6
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
0
6
1
7
1

0
.
0
1
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Is
o
p
h
o
r
o
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
4
6
7

4
.
9
1
0.
1
2
5

0
.
1
2
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
1
3
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
n-
N
i
t
r
o
s
o
-
d
i
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n
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p
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p
y
l
a
m
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n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
4
5

2
5
.
7
0.
6
5
6

0
.
6
5
6
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
6
6
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
7
1
9

0
.
7
5
5
0.
0
1
9
3

0
.
0
1
9
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
2
4
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
1
2
9

0
.
0
6
4
4
0.
0
0
1
6
4

0
.
0
0
1
6
4
50

2
.
0
0
0.
0
2
5
5

0
.
0
2
7
2
17

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
HI

-

S
V
O
C
s
<0
.
0
1

(
d
e
t
s
)
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
2
1
4
0.
0
0
0
0
5
4
5

0
.
0
0
0
0
5
4
5
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
0
6

0
.
0
0
0
0
5
4
8
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
2
7
9

0
.
0
0
0
2
5
1
0.
0
0
0
0
0
6
4
1

0
.
0
0
0
0
0
6
4
1
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
5
9

0
.
0
0
0
0
0
6
8
7
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
3
5
4
0.
0
0
0
0
0
9
0
3

0
.
0
0
0
0
0
9
0
3
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
1
0

0
.
0
0
0
0
0
9
5
4
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
2
9
8

0
.
0
0
0
2
3
8
0.
0
0
0
0
0
6
0
8

0
.
0
0
0
0
0
6
0
8
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
0
8

0
.
0
0
0
0
0
6
4
8
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
8
9
9
0.
0
0
0
0
2
2
9

0
.
0
0
0
0
2
2
9
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
2
3
3
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
9
0
8
0.
0
0
0
2
3
2

0
.
0
0
0
2
3
2
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
5
6
1

0
.
0
0
0
2
3
2
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
3
7

0
.
0
0
3
8
5
0.
0
0
0
0
9
8
1

0
.
0
0
0
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9
8
1
0.
0
0
2
8
0

2
.
0
0
0.
0
0
0
0
0
1
4
3

0
.
0
0
0
0
9
9
6
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
5
2
6
0.
0
0
0
1
3
4

0
.
0
0
0
1
3
4
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
5
9

0
.
0
0
0
1
3
5
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
8
0

0
.
0
0
0
0
1
8
5
0.
0
0
0
0
0
0
4
7
3

0
.
0
0
0
0
0
0
4
7
3
0.
0
0
3
2
0

2
.
0
0
0.
0
0
0
0
0
1
6
3

0
.
0
0
0
0
0
2
1
1
17

<
0
.
0
1

4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
4
3
8

0
.
0
0
1
7
1
0.
0
0
0
0
4
3
6

0
.
0
0
0
0
4
3
6
0.
0
0
3
9
0

2
.
0
0
0.
0
0
0
0
0
1
9
9

0
.
0
0
0
0
4
5
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
5
7

0
.
0
0
3
6
0
0.
0
0
0
0
9
1
8

0
.
0
0
0
0
9
1
8
0.
0
0
1
4
0

2
.
0
0
0.
0
0
0
0
0
0
7
1
4

0
.
0
0
0
0
9
2
5
17

<
0
.
0
1

4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
2
0
0
0.
0
0
0
0
5
1
1

0
.
0
0
0
0
5
1
1
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
0
8

0
.
0
0
0
0
5
1
5
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
5
7
3
0.
0
0
0
0
1
4
6

0
.
0
0
0
0
1
4
6
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
1
5
0
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
1
.
7

0
.
0
1
0
5
0.
0
0
0
2
6
8

0
.
0
0
0
2
6
8
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
5
9

0
.
0
0
0
2
6
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
4
9
8
0.
0
0
0
0
0
1
2
7

0
.
0
0
0
0
0
1
2
7
0.
0
0
1
9
0

2
.
0
0
0.
0
0
0
0
0
0
9
7
0

0
.
0
0
0
0
0
2
2
4
17

<
0
.
0
1

4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
8
1
2
0.
0
0
0
0
0
2
0
7

0
.
0
0
0
0
0
2
0
7
0.
0
0
3
1
0

2
.
0
0
0.
0
0
0
0
0
1
5
8

0
.
0
0
0
0
0
3
6
5
17

<
0
.
0
1

4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

2
-
B
u
t
a
n
o
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
7
3
2
0.
0
1
8
7

0
.
0
1
8
7
0.
0
1
5
9

2
.
0
0
0.
0
0
0
0
0
8
1
1

0
.
0
1
8
7
39

<
0
.
0
1

1
8
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
0
.
2

0
.
1
2
0
0.
0
0
3
0
7

0
.
0
0
3
0
7
0.
0
0
5
9
5

2
.
0
0
0.
0
0
0
0
0
3
0
4

0
.
0
0
3
0
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
C
h
l
o
r
o
p
h
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
5
5
7

5
.
8
4
0.
1
4
9

0
.
1
4
9
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
1
5
4
17

<
0
.
0
1

0
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
2-
H
e
x
a
n
o
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
6
3
2
0.
0
0
1
6
1

0
.
0
0
1
6
1
0.
0
0
3
8
0

2
.
0
0
0.
0
0
0
0
0
1
9
4

0
.
0
0
1
6
2
39

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
5
6
6

5
.
9
4
0.
1
5
2

0
.
1
5
2
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
1
5
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
9
3
4

0
.
0
9
8
1
0.
0
0
2
5
0

0
.
0
0
2
5
0
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
0
0
7
8
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
8
5
4
0.
0
0
2
1
8

0
.
0
0
2
1
8
0.
0
0
4
3
0

2
.
0
0
0.
0
0
0
0
0
2
1
9

0
.
0
0
2
1
8
39

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

A
c
e
t
o
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

7
5
.
6

1
8
1
0
46
.
3

4
6
.
3
24

2
.
0
0
0.
0
1
2
2

4
6
.
3
39
1.
2
32
%
Re
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

B
e
n
z
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
3
3
9
0.
0
0
0
8
6
4

0
.
0
0
0
8
6
4
0.
0
0
4
1
0

2
.
0
0
0.
0
0
0
0
0
2
0
9

0
.
0
0
0
8
6
6
10

<
0
.
0
1

1
4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
7
.
9

1
.
3
3
0.
0
3
3
9

0
.
0
3
3
9
0.
0
7
4
0

2
.
0
0
0.
0
0
0
0
3
7
8

0
.
0
3
3
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
4
0

2
5
.
2
0.
6
4
3

0
.
6
4
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
6
4
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
6
5
9

6
.
9
2
0.
1
7
7

0
.
1
7
7
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
1
8
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

8
.
4
9

0
.
0
0
5
9
4
0.
0
0
0
1
5
2

0
.
0
0
0
1
5
2
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
1
5
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Br
o
m
o
f
o
r
m
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
3
4
6

0
.
0
0
0
1
7
3
0.
0
0
0
0
0
4
4
2

0
.
0
0
0
0
0
4
4
2
0.
0
0
0
5
0
0

2
.
0
0
0.
0
0
0
0
0
0
2
5
5

0
.
0
0
0
0
0
4
6
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Br
o
m
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
2
9
8
0.
0
0
0
7
6
0

0
.
0
0
0
7
6
0
0.
0
0
1
5
0

2
.
0
0
0.
0
0
0
0
0
0
7
6
5

0
.
0
0
0
7
6
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
.
2
9

0
.
0
0
3
8
6
0.
0
0
0
0
9
8
6

0
.
0
0
0
0
9
8
6
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
5
9

0
.
0
0
0
0
9
9
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
9
4
0
0.
0
0
0
0
0
2
4
0

0
.
0
0
0
0
0
2
4
0
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
0
2
7
5
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
7
9
0.
0
0
0
0
7
1
1

0
.
0
0
0
0
7
1
1
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
1
0

0
.
0
0
0
0
7
1
7
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
f
o
r
m
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
8
7
3

0
.
0
0
0
6
1
1
0.
0
0
0
0
1
5
6

0
.
0
0
0
0
1
5
6
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
1
5
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
2
0
0

0
.
0
0
0
2
0
0
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
1
0

0
.
0
0
0
2
0
0
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
7
4
4
0.
0
0
0
1
9
0

0
.
0
0
0
1
9
0
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
1
9
0
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
4
2
7
0.
0
0
0
1
0
9

0
.
0
0
0
1
0
9
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
0
6

0
.
0
0
0
1
0
9
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
6
7
4

0
.
0
0
0
4
7
2
0.
0
0
0
0
1
2
0

0
.
0
0
0
0
1
2
0
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
1
2
4
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Di
b
r
o
m
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
3
.
3

0
.
0
0
6
6
5
0.
0
0
0
1
7
0

0
.
0
0
0
1
7
0
0.
0
0
0
5
0
0

2
.
0
0
0.
0
0
0
0
0
0
2
5
5

0
.
0
0
0
1
7
0
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
5
8
0

0
.
0
0
0
6
3
8
0.
0
0
0
0
1
6
3

0
.
0
0
0
0
1
6
3
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
5
6
1

0
.
0
0
0
0
1
6
8
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Et
h
y
l
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
8
9
8
0.
0
0
0
0
0
2
2
9

0
.
0
0
0
0
0
2
2
9
0.
0
0
1
3
0

2
.
0
0
0.
0
0
0
0
0
0
6
6
3

0
.
0
0
0
0
0
2
9
5
10

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
m,
p
-
X
y
l
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
6
0
8
0.
0
0
0
1
5
5

0
.
0
0
0
1
5
5
0.
0
0
2
0
0

2
.
0
0
0.
0
0
0
0
0
1
0
2

0
.
0
0
0
1
5
6
10

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
.
1
0

0
.
0
1
3
1
0.
0
0
0
3
3
5

0
.
0
0
0
3
3
5
0.
0
0
3
2
0

2
.
0
0
0.
0
0
0
0
0
1
6
3

0
.
0
0
0
3
3
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

o
-
X
y
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
3
4

0
.
0
0
9
0
1
0.
0
0
0
2
3
0

0
.
0
0
0
2
3
0
0.
0
0
2
7
0

2
.
0
0
0.
0
0
0
0
0
1
3
8

0
.
0
0
0
2
3
1
10

<
0
.
0
1

1
4
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Ph
e
n
o
l
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
6
2

2
7
.
5
0.
7
0
1

0
.
7
0
1
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
7
0
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

S
t
y
r
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
.
0
2

0
.
0
1
0
5
0.
0
0
0
2
6
7

0
.
0
0
0
2
6
7
0.
0
0
2
6
0

2
.
0
0
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
2
6
8
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
9

0
.
0
1
3
3
0.
0
0
0
3
3
9

0
.
0
0
0
3
3
9
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
3
3
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
2
2
7
0.
0
0
0
0
5
7
9

0
.
0
0
0
0
5
7
9
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
5
9

0
.
0
0
0
0
5
8
4
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w

T
o
l
u
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
8
8
2
0.
0
0
2
2
5

0
.
0
0
2
2
5
0.
0
1
8
7

2
.
0
0
0.
0
0
0
0
0
9
5
4

0
.
0
0
2
2
6
10

<
0
.
0
1

2
3
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
0
4
4
7

0
.
0
0
0
0
4
4
7
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
4
5
1
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
6
5
4
0.
0
0
0
0
1
6
7

0
.
0
0
0
0
1
6
7
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
0
8

0
.
0
0
0
0
1
7
1
17

<
0
.
0
1

5
%
Pa
s
s
Sa
g
e

S
p
a
r
r
o
w
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
3
3
1

0
.
0
0
0
2
3
2
0.
0
0
0
0
0
5
9
2

0
.
0
0
0
0
0
5
9
2
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
0
6
2
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
2
6
1

0
.
0
0
0
2
8
8
0.
0
0
0
0
0
7
3
4

0
.
0
0
0
0
0
7
3
4
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
5
6
1

0
.
0
0
0
0
0
7
9
0
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Vi
n
y
l

A
c
e
t
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
2

0
.
0
2
6
4
0.
0
0
0
6
7
3

0
.
0
0
0
6
7
3
0.
0
0
1
2
0

2
.
0
0
0.
0
0
0
0
0
0
6
1
2

0
.
0
0
0
6
7
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
1
0

0
.
0
0
3
7
2
0.
0
0
0
0
9
5
0

0
.
0
0
0
0
9
5
0
0.
0
0
1
2
0

2
.
0
0
0.
0
0
0
0
0
0
6
1
2

0
.
0
0
0
0
9
5
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
HI

-

V
O
C
s
1.
2
(d
e
t
s
)
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
9

2
.
9
3
0.
0
6
5
4
0-
0
00
.
0
6
5
4
0.
1
0
5

0
00
.
0
6
5
4
00
.
9
3
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
6

2
.
1
3
0.
0
4
7
5
0-
0
00
.
0
4
7
5
0.
0
8
0
0

0
0

0
.
0
4
7
5
00
.
1
1
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
1
7
0

0
.
2
5
5
0.
0
0
5
6
9
0-
0
0

0
.
0
0
5
6
9
1.
5
0

0
0

0
.
0
0
5
6
9
0

0
.
0
8
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
7

1
4
4
0
32
0-
0
03
2
50

0
03
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

5
.
1
0

1
0
.
2
0.
2
2
8
0-
0
00
.
2
2
8
2.
0
0

0
00
.
2
2
8
0
3.
3
2%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
1
6

3
3
.
2
0.
7
4
0
0-
0
00
.
7
4
0
10
.
5

0
00
.
7
4
0
0
11
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
1
0.
1
5
0
0-
0
00
.
1
5
0
1.
5
0

0
00
.
1
5
0
0
2.
1
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7

1
3
5
0
30
.
1
0-
0
03
0
.
1
50

0
03
0
.
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
N
i
t
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
9

2
8
3
6.
3
1
0-
0
06
.
3
1
10
.
5

0
06
.
3
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
9

4
.
3
2
0.
0
9
6
5
0-
0
00
.
0
9
6
5
0.
1
4
0

0
00
.
0
9
6
5
0
1.
4
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
3-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
5

1
3
2
0
29
.
5
0-
0
02
9
.
5
50

0
02
9
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
5

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
6

4
.
1
4
0.
0
9
2
4
0-
0
00
.
0
9
2
4
0.
1
5
0

0
00
.
0
9
2
4
0
1.
3
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
2

1
6
0
0
35
.
7
0-
0
03
5
.
7
50

0
03
5
.
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
N
i
t
r
o
a
n
i
l
i
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
5

1
4
2
0
31
.
7
0-
0
03
1
.
7
50

0
03
1
.
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
N
i
t
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
8

1
4
9
0
33
.
3
0-
0
03
3
.
3
50

0
03
3
.
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
5

5
.
2
3
0.
1
1
7
0-
0
00
.
1
1
7
0.
1
9
0

0
00
.
1
1
7
0
1.
7
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

H
M
X

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
0
0

2
5
0.
5
5
8
0-
0
00
.
5
5
8
25

0
00
.
5
5
8
9

0
.
0
6
2

3
1
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ni
t
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
7

3
1
1
6.
9
5
0-
0
06
.
9
5
10
.
5

0
06
.
9
5
0
99
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ni
t
r
o
g
l
y
c
e
r
i
n
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
6

9
.
0
5
0.
2
0
2
0-
0
00
.
2
0
2
0.
3
4
0

0
00
.
2
0
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

N
i
t
r
o
g
u
a
n
i
d
i
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
4
.
2

7
.
2
7
0.
1
6
2
0-
0
00
.
1
6
2
0.
3
0
0

0
00
.
1
6
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
PE
T
N
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
6

1
3
.
8
0.
3
0
7
0-
0
00
.
3
0
7
0.
5
0
0

0
00
.
3
0
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

P
i
c
r
i
c

a
c
i
d

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
4

1
3
.
2
0.
2
9
5
0-
0
00
.
2
9
5
0.
5
0
0

0
00
.
2
9
5
NS
V
--
7%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
RD
X
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
3
1.
9
5
0-
0
01
.
9
5
1.
5
0

0
01
.
9
5
0
28
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Te
t
r
y
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
1

6
.
6
9
0.
1
4
9
0-
0
00
.
1
4
9
0.
2
3
0

0
00
.
1
4
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

E
n
e
r
g
e
t
i
c
s
3.
3
(d
e
t
s
)
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

A
l
u
m
i
n
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
3
4
0

1
8
4
0
0
41
0
0-
0
0

4
1
0
54
0
0
0

0
0

4
1
0
11
0
3.
7
10
0
%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

A
n
t
i
m
o
n
y

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
0
2
5
0

4
.
1
7
0.
0
9
3
1
0-
0
0

0
.
0
9
3
1
16
7

0
0

0
.
0
9
3
1
NS
V
--
79
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

A
r
s
e
n
i
c

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
3
4
0.
0
7
4
5
0-
0
0

0
.
0
7
4
5
41
.
3

0
00
.
0
7
4
5
9

<
0
.
0
1

5
8
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

B
a
r
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
3
6
0

2
3
0
5.
1
4
0-
0
05
.
1
4
64
0

0
05
.
1
4
21

0
.
2
5

1
0
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

B
e
r
y
ll
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
1
8

0
.
8
5
1
0.
0
1
9
0
0-
0
00
.
0
1
9
0
0.
7
2
0

0
00
.
0
1
9
0
NS
V
--
48
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

C
a
d
m
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
3
0
2.
9
0
0-
0
02
.
9
0
32

0
02
.
9
0
0
18
44
%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
1

0
.
0
2
9
9
0.
0
0
0
6
6
6
0-
0
0

0
.
0
0
0
6
6
6
0.
0
0
1
1
0

0
0

0
.
0
0
0
6
6
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

C
h
r
o
m
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
1
6

1
7
5
3.
9
0
0-
0
03
.
9
0
55
.
3

0
03
.
9
0
1
3.
9
10
0
%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

C
o
b
a
l
t

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
2
9
1

1
.
4
3
0.
0
3
1
8
0-
0
0

0
.
0
3
1
8
4.
9
0

0
00
.
0
3
1
8
8

<
0
.
0
1

7
9
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

C
o
p
p
e
r

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
0
.
9
1.
5
8
0-
0
01
.
5
8
18
0
0
0

0
01
.
5
8
47

0
.
0
3
4

8
5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

I
r
o
n

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
3
8
0

5
7
0
0
12
7
0-
0
0

1
2
7
15
0
0
0

0
0

1
2
7
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

L
e
a
d

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
8
2
0
10
8
0-
0
0

1
0
8
48
0
0
0

0
0

1
0
8
0
57
0
83
%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

M
a
g
n
e
s
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
4
2
5

1
0
3
0
0
23
0
0-
0
0

2
3
0
24
3
0
0

0
0

2
3
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

M
a
n
g
a
n
e
s
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
.
7
0.
7
0
6
0-
0
00
.
7
0
6
51
9

0
00
.
7
0
6
97
7

<
0
.
0
1

1
0
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

M
e
r
c
u
r
y

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
3
6
9
0.
0
0
8
2
2
0-
0
0

0
.
0
0
8
2
2
0.
0
7
0
0

0
0

0
.
0
0
8
2
2
0

0
.
1
2

2
7
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

M
o
l
y
b
d
e
n
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
0
9

3
5
.
5
0.
7
9
3
0-
0
00
.
7
9
3
17

0
00
.
7
9
3
4

0
.
2
3

9
1
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

N
i
c
k
e
l

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

4
.
7
3

1
9
5
4.
3
6
0-
0
04
.
3
6
41
.
3

0
04
.
3
6
18

0
.
2
5

1
0
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

N
i
t
r
a
t
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
0
0

2
2
.
8
0.
5
0
9
0-
0
00
.
5
0
9
22
.
8

0
00
.
5
0
9
NS
V
--
92
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

P
e
r
c
h
l
o
r
a
t
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
0
0

4
.
5
0
0.
1
0
0
0-
0
00
.
1
0
0
4.
5
0

0
00
.
1
0
0
3

0
.
0
3
1

5
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

P
h
o
s
p
h
o
r
u
s

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
0
0

9
9
0
22
.
1
0-
0
02
2
.
1
99
0

0
02
2
.
1
0
60
0
10
0
%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Se
l
e
n
i
u
m
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
2
0.
0
6
7
3
0-
0
00
.
0
6
7
3
5.
0
0

0
00
.
0
6
7
3
00
.
1
7
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

S
i
l
v
e
r

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
5
.
3

6
1
.
4
1.
3
7
0-
0
01
.
3
7
4.
0
0

0
01
.
3
7
NS
V
--
8%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

S
t
r
o
n
t
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
2
7
8

1
3
5
3.
0
0
0-
0
03
.
0
0
48
4

0
03
.
0
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

T
h
a
ll
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
2
5
6

0
.
1
4
1
0.
0
0
3
1
4
0-
0
0

0
.
0
0
3
1
4
0.
5
5
0

0
0

0
.
0
0
3
1
4
1

<
0
.
0
1

5
4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

V
a
n
a
d
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
0
8
8
0

2
.
2
6
0.
0
5
0
4
0-
0
0

0
.
0
5
0
4
25
.
7

0
00
.
0
5
0
4
11

<
0
.
0
1

1
0
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

Z
i
n
c

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
8
0
24
.2
0-
0
0
24
.2
23
0
0

0
02
4
.
2
15
1.
7
10
0
%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

I
n
o
r
g
a
n
i
c
s
12
0
0
(d
e
t
s
)
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9

4
9
4
0
11
0
0-
0
0

1
1
0
17
0

0
01
1
0
27
4.
1
14
%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

A
c
e
n
a
p
h
t
h
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
4
7

0
.
0
6
1
5
0.
0
0
1
3
7
0-
0
0

0
.
0
0
1
3
7
0.
0
4
1
8

0
0

0
.
0
0
1
3
7
32
5

<
0
.
0
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ac
e
n
a
p
h
t
h
y
l
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
2
.
9

2
4
0
5.
3
6
0-
0
05
.
3
6
10
.
5

0
05
.
3
6
32
5

0
.
0
1
6

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

A
n
t
h
r
a
c
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
4
2

8
.
9
5
0.
2
0
0
0-
0
00
.
2
0
0
3.
7
0

0
00
.
2
0
0
32
5

<
0
.
0
1

7
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
5
9

1
6
.
7
0.
3
7
2
0-
0
00
.
3
7
2
10
.
5

0
00
.
3
7
2
32
5

<
0
.
0
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
3
3

1
4
0.
3
1
1
0-
0
00
.
3
1
1
10
.
5

0
00
.
3
1
1
32
5

<
0
.
0
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
6
0

2
7
.
3
0.
6
0
9
0-
0
00
.
6
0
9
10
.
5

0
00
.
6
0
9
32
5

<
0
.
0
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
9
4

3
0
.
9
0.
6
8
9
0-
0
00
.
6
8
9
10
.
5

0
00
.
6
8
9
32
5

<
0
.
0
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
6
0

2
7
.
3
0.
6
0
9
0-
0
00
.
6
0
9
10
.
5

0
00
.
6
0
9
32
5

<
0
.
0
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ch
r
y
s
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
2
9

2
4
0.
5
3
6
0-
0
00
.
5
3
6
10
.
5

0
00
.
5
3
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
3
1

2
4
.
3
0.
5
4
1
0-
0
00
.
5
4
1
10
.
5

0
00
.
5
4
1
32
5

<
0
.
0
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
0
4

0
.
4
3
8
0.
0
0
9
7
6
0-
0
0

0
.
0
0
9
7
6
0.
1
4
4

0
0

0
.
0
0
9
7
6
32
5

<
0
.
0
1

4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

F
l
u
o
r
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

9
.
5
7

3
1
6
7.
0
4
0-
0
07
.
0
4
33

0
07
.
0
4
32
5

0
.
0
2
2

1
4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
8
6

3
0
0.
6
7
0
0-
0
00
.
6
7
0
10
.
5

0
00
.
6
7
0
32
5

<
0
.
0
1

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

N
a
p
h
t
h
a
l
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

4
.
4
0

2
3
3
5.
2
0
0-
0
05
.
2
0
53

0
05
.
2
0
27

0
.
1
9

2
5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
7
2

1
5
8
3.
5
3
0-
0
03
.
5
3
92

0
03
.
5
3
32
5

0
.
0
1
1

1
8
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Py
r
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
7
5

1
8
.
4
0.
4
1
0
0-
0
00
.
4
1
0
10
.
5

0
00
.
4
1
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

P
A
H
s
4.
3
(d
e
t
s
)
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
TP
H
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

-

0
0
0-
0
00
47
0
0
0

0
00
50
0

<
0
.
0
1

1
0
0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

P
e
t
r
o
l
e
u
m
<0
.
0
1

(
d
e
t
s
)
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
5
.
1

1
7
6
0
39
.
1
0-
0
03
9
.
1
50

0
03
9
.
1
17
2.
3
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
5
.
6

3
7
4
8.
3
3
0-
0
08
.
3
3
10
.
5

0
08
.
3
3
17

0
.
4
9

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
2
.
6

3
4
2
7.
6
4
0-
0
07
.
6
4
10
.
5

0
07
.
6
4
17

0
.
4
5

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
2
.
3

3
4
0
7.
5
7
0-
0
07
.
5
7
10
.
5

0
07
.
5
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
6

3
7
8
8.
4
3
0-
0
08
.
4
3
10
.
5

0
08
.
4
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
M
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
1

2
8
4
6.
3
5
0-
0
06
.
3
5
10
.
5

0
06
.
3
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
8

6
0
5
13
.
5
0-
0
01
3
.
5
21

0
01
3
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
3
.
2

3
4
9
7.
7
7
0-
0
07
.
7
7
10
.
5

0
07
.
7
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
C
h
l
o
r
o
a
n
i
l
i
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
6

3
1
1
6.
9
3
0-
0
06
.
9
3
10
.
5

0
06
.
9
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
M
e
t
h
y
l
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
9

3
1
4
7.
0
0
0-
0
07
.
0
0
10
.
5

0
07
.
0
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Be
n
z
o
i
c

a
c
i
d
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
7

1
4
9
0
33
.
1
0-
0
03
3
.
1
50

0
03
3
.
1
32
5

0
.
1
0

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Be
n
z
y
l
a
l
c
o
h
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
7

2
9
1
6.
4
9
0-
0
06
.
4
9
10
.
5

0
06
.
4
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
3
.
4

5
0
.
1
1.
1
2
0-
0
01
.
1
2
1.
5
0

0
01
.
1
2
1
1.
0
18
%
Re
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
6

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8
.
8

4
0
8
9.
0
9
0-
0
09
.
0
9
10
.
5

0
09
.
0
9
0
83
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

D
i
b
e
n
z
o
f
u
r
a
n

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9

3
4
8
7.
7
7
0-
0
07
.
7
7
12

0
07
.
7
7
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
3

3
2
9
7.
3
4
0-
0
07
.
3
4
10
.
5

0
07
.
3
4
0
67
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
9

3
0
3
6.
7
7
0-
0
06
.
7
7
10
.
5

0
06
.
7
7
0
62
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8

3
9
9
8.
9
1
0-
0
08
.
9
1
10
.
5

0
08
.
9
1
0
81
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
8

3
2
3
7.
2
1
0-
0
07
.
2
1
10
.
5

0
07
.
2
1
0
66
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

4
0
.
2

4
2
2
9.
4
2
0-
0
09
.
4
2
10
.
5

0
09
.
4
2
1
17
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8
.
6

0
.
0
3
0
9
0.
0
0
0
6
8
9
0-
0
0

0
.
0
0
0
6
8
9
0.
0
0
0
8
0
0

0
0

0
.
0
0
0
6
8
9
1

<
0
.
0
1

4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
6

3
7
8
8.
4
3
0-
0
08
.
4
3
10
.
5

0
08
.
4
3
1
15
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8

3
9
9
8.
9
0
0-
0
08
.
9
0
10
.
5

0
08
.
9
0
1
16
0%
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Is
o
p
h
o
r
o
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
8

3
2
3
7.
2
1
0-
0
07
.
2
1
10
.
5

0
07
.
2
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
7

3
0
1
6.
7
2
0-
0
06
.
7
2
10
.
5

0
06
.
7
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
3
.
3

3
4
9
7.
8
0
0-
0
07
.
8
0
10
.
5

0
07
.
8
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

5
.
9
3

2
9
7
6.
6
1
0-
0
06
.
6
1
50

0
06
.
6
1
17

0
.
3
9

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

S
V
O
C
s
1.
0
(d
e
t
s
)
Re
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
3

0
.
0
1
7
0
0.
0
0
0
3
7
8
0-
0
0

0
.
0
0
0
3
7
8
0.
0
0
0
6
0
0

0
0

0
.
0
0
0
3
7
8
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
4

0
.
0
2
8
3
0.
0
0
0
6
3
1
0-
0
0

0
.
0
0
0
6
3
1
0.
0
0
0
9
0
0

0
0

0
.
0
0
0
6
3
1
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
1

0
.
0
3
1
1
0.
0
0
0
6
9
4
0-
0
0

0
.
0
0
0
6
9
4
0.
0
0
1
0
0

0
0

0
.
0
0
0
6
9
4
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
4

0
.
0
2
5
1
0.
0
0
0
5
6
0
0-
0
0

0
.
0
0
0
5
6
0
0.
0
0
0
8
0
0

0
0

0
.
0
0
0
5
6
0
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
5

0
.
0
2
0
6
0.
0
0
0
4
6
1
0-
0
0

0
.
0
0
0
4
6
1
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
6
1
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
3

0
.
0
3
0
0
0.
0
0
0
6
6
9
0-
0
0

0
.
0
0
0
6
6
9
0.
0
0
1
1
0

0
0

0
.
0
0
0
6
6
9
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
4

0
.
0
8
2
4
0.
0
0
1
8
4
0-
0
0

0
.
0
0
1
8
4
0.
0
0
2
8
0

0
0

0
.
0
0
1
8
4
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
7

0
.
0
2
4
9
0.
0
0
0
5
5
6
0-
0
0

0
.
0
0
0
5
5
6
0.
0
0
0
9
0
0

0
0

0
.
0
0
0
5
5
6
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
7

0
.
1
1
8
0.
0
0
2
6
4
0-
0
0

0
.
0
0
2
6
4
0.
0
0
3
2
0

0
0

0
.
0
0
2
6
4
17

<
0
.
0
1

4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
9

0
.
1
2
0
0.
0
0
2
6
8
0-
0
0

0
.
0
0
2
6
8
0.
0
0
3
9
0

0
0

0
.
0
0
2
6
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
7

0
.
0
4
0
1
0.
0
0
0
8
9
5
0-
0
0

0
.
0
0
0
8
9
5
0.
0
0
1
4
0

0
0

0
.
0
0
0
8
9
5
17

<
0
.
0
1

4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
7

0
.
0
2
2
9
0.
0
0
0
5
1
2
0-
0
0

0
.
0
0
0
5
1
2
0.
0
0
0
8
0
0

0
0

0
.
0
0
0
5
1
2
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
1

0
.
0
2
1
0
0.
0
0
0
4
6
9
0-
0
0

0
.
0
0
0
4
6
9
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
6
9
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
9

0
.
0
2
4
2
0.
0
0
0
5
4
0
0-
0
0

0
.
0
0
0
5
4
0
0.
0
0
0
9
0
0

0
0

0
.
0
0
0
5
4
0
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
4
.
7

0
.
0
6
6
0
0.
0
0
1
4
7
0-
0
0

0
.
0
0
1
4
7
0.
0
0
1
9
0

0
0

0
.
0
0
1
4
7
17

<
0
.
0
1

4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
4
.
7

0
.
1
0
8
0.
0
0
2
4
0
0-
0
0

0
.
0
0
2
4
0
0.
0
0
3
1
0

0
0

0
.
0
0
2
4
0
17

<
0
.
0
1

4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

2
-
B
u
t
a
n
o
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
5
.
4

0
.
4
0
4
0.
0
0
9
0
0
0-
0
0

0
.
0
0
9
0
0
0.
0
1
5
9

0
0

0
.
0
0
9
0
0
39

<
0
.
0
1

1
8
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
3

0
.
1
5
6
0.
0
0
3
4
9
0-
0
0

0
.
0
0
3
4
9
0.
0
0
5
9
5

0
0

0
.
0
0
3
4
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
C
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
6

3
2
1
7.
1
5
0-
0
07
.
1
5
10
.
5

0
07
.
1
5
17

0
.
4
2

0
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
H
e
x
a
n
o
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
5

0
.
1
0
1
0.
0
0
2
2
5
0-
0
0

0
.
0
0
2
2
5
0.
0
0
3
8
0

0
0

0
.
0
0
2
2
5
39

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
5

3
2
1
7.
1
5
0-
0
07
.
1
5
10
.
5

0
07
.
1
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
6
.
3

3
8
1
8.
4
9
0-
0
08
.
4
9
10
.
5

0
08
.
4
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
3

0
.
1
1
3
0.
0
0
2
5
2
0-
0
0

0
.
0
0
2
5
2
0.
0
0
4
3
0

0
0

0
.
0
0
2
5
2
39

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

A
c
e
t
o
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
4
.
9

5
9
7
13
.
3
0-
0
01
3
.
3
24

0
0

1
3
.
3
39

0
.
3
4

3
2
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

B
e
n
z
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
3

0
.
1
1
2
0.
0
0
2
5
0
0-
0
0

0
.
0
0
2
5
0
0.
0
0
4
1
0

0
0

0
.
0
0
2
5
0
10

<
0
.
0
1

1
4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
4

1
.
9
5
0.
0
4
3
6
0-
0
00
.
0
4
3
6
0.
0
7
4
0

0
0

0
.
0
4
3
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
7

3
0
2
6.
7
3
0-
0
06
.
7
3
10
.
5

0
06
.
7
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
3

3
1
9
7.
1
0
0-
0
07
.
1
0
10
.
5

0
07
.
1
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
3

0
.
0
1
9
1
0.
0
0
0
4
2
6
0-
0
0

0
.
0
0
0
4
2
6
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
2
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Br
o
m
o
f
o
r
m
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
2

0
.
0
1
5
6
0.
0
0
0
3
4
8
0-
0
0

0
.
0
0
0
3
4
8
0.
0
0
0
5
0
0

0
0

0
.
0
0
0
3
4
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Br
o
m
o
m
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
3

0
.
0
3
9
4
0.
0
0
0
8
8
0
0-
0
0

0
.
0
0
0
8
8
0
0.
0
0
1
5
0

0
0

0
.
0
0
0
8
8
0
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8

0
.
0
2
5
2
0.
0
0
0
5
6
3
0-
0
0

0
.
0
0
0
5
6
3
0.
0
0
0
9
0
0

0
0

0
.
0
0
0
5
6
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
2
.
4

0
.
0
2
2
7
0.
0
0
0
5
0
6
0-
0
0

0
.
0
0
0
5
0
6
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
5
0
6
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
6

0
.
0
2
8
6
0.
0
0
0
6
3
7
0-
0
0

0
.
0
0
0
6
3
7
0.
0
0
1
0
0

0
0

0
.
0
0
0
6
3
7
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ch
l
o
r
o
f
o
r
m
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0

0
.
0
2
1
0
0.
0
0
0
4
6
8
0-
0
0

0
.
0
0
0
4
6
8
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
6
8
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
3

0
.
0
2
7
3
0.
0
0
0
6
1
0
0-
0
0

0
.
0
0
0
6
1
0
0.
0
0
1
0
0

0
0

0
.
0
0
0
6
1
0
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7

0
.
0
1
8
9
0.
0
0
0
4
2
2
0-
0
0

0
.
0
0
0
4
2
2
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
2
2
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
5

0
.
0
1
6
5
0.
0
0
0
3
6
7
0-
0
0

0
.
0
0
0
3
6
7
0.
0
0
0
6
0
0

0
0

0
.
0
0
0
3
6
7
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
3

0
.
0
2
1
2
0.
0
0
0
4
7
3
0-
0
0

0
.
0
0
0
4
7
3
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
7
3
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
b
r
o
m
o
m
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
7

0
.
0
1
3
4
0.
0
0
0
2
9
8
0-
0
0

0
.
0
0
0
2
9
8
0.
0
0
0
5
0
0

0
0

0
.
0
0
0
2
9
8
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
5

0
.
0
3
3
5
0.
0
0
0
7
4
8
0-
0
0

0
.
0
0
0
7
4
8
0.
0
0
1
1
0

0
0

0
.
0
0
0
7
4
8
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Et
h
y
l
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
3
.
3

0
.
0
4
3
3
0.
0
0
0
9
6
7
0-
0
0

0
.
0
0
0
9
6
7
0.
0
0
1
3
0

0
0

0
.
0
0
0
9
6
7
10

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
m,
p
-
X
y
l
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
5

0
.
0
5
6
9
0.
0
0
1
2
7
0-
0
0

0
.
0
0
1
2
7
0.
0
0
2
0
0

0
0

0
.
0
0
1
2
7
10

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
1

0
.
0
8
9
9
0.
0
0
2
0
1
0-
0
0

0
.
0
0
2
0
1
0.
0
0
3
2
0

0
0

0
.
0
0
2
0
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

o
-
X
y
l
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
3

0
.
0
7
6
5
0.
0
0
1
7
1
0-
0
0

0
.
0
0
1
7
1
0.
0
0
2
7
0

0
0

0
.
0
0
1
7
1
10

<
0
.
0
1

1
4
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ph
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
6

3
0
1
6.
7
1
0-
0
06
.
7
1
10
.
5

0
06
.
7
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

S
t
y
r
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
1

0
.
0
7
3
1
0.
0
0
1
6
3
0-
0
0

0
.
0
0
1
6
3
0.
0
0
2
6
0

0
0

0
.
0
0
1
6
3
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
4

0
.
0
1
8
4
0.
0
0
0
4
1
1
0-
0
0

0
.
0
0
0
4
1
1
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
1
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
7

0
.
0
2
5
8
0.
0
0
0
5
7
6
0-
0
0

0
.
0
0
0
5
7
6
0.
0
0
0
9
0
0

0
0

0
.
0
0
0
5
7
6
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

T
o
l
u
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
9

0
.
5
2
2
0.
0
1
1
7
0-
0
0

0
.
0
1
1
7
0.
0
1
8
7

0
00
.
0
1
1
7
10

<
0
.
0
1

2
3
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
7

0
.
0
2
0
1
0.
0
0
0
4
4
8
0-
0
0

0
.
0
0
0
4
4
8
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
4
8
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
1

0
.
0
2
4
0
0.
0
0
0
5
3
6
0-
0
0

0
.
0
0
0
5
3
6
0.
0
0
0
8
0
0

0
0

0
.
0
0
0
5
3
6
17

<
0
.
0
1

5
%
Pa
s
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
2

0
.
0
2
1
9
0.
0
0
0
4
8
7
0-
0
0

0
.
0
0
0
4
8
7
0.
0
0
0
7
0
0

0
0

0
.
0
0
0
4
8
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
5

0
.
0
3
4
7
0.
0
0
0
7
7
4
0-
0
0

0
.
0
0
0
7
7
4
0.
0
0
1
1
0

0
0

0
.
0
0
0
7
7
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Vi
n
y
l

A
c
e
t
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
6
.
2

0
.
0
3
1
4
0.
0
0
0
7
0
1
0-
0
0

0
.
0
0
0
7
0
1
0.
0
0
1
2
0

0
0

0
.
0
0
0
7
0
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
4

0
.
0
3
4
1
0.
0
0
0
7
6
1
0-
0
0

0
.
0
0
0
7
6
1
0.
0
0
1
2
0

0
0

0
.
0
0
0
7
6
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

V
O
C
s
0.
7
7
(d
e
t
s
)
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
9

2
.
9
3
0.
0
5
8
1
0-
0
00
.
0
5
8
1
0.
1
0
5

2
.
0
0
0.
0
0
0
0
4
1
7

0
.
0
5
8
2
00
.
8
3
0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
6
.
6

2
.
1
3
0.
0
4
2
2
0-
0
00
.
0
4
2
2
0.
0
8
0
0

2
.
0
0
0.
0
0
0
0
3
1
7

0
.
0
4
2
3
00
.
1
0
0
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
7

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
1
7
0

0
.
2
5
5
0.
0
0
5
0
6
0-
0
0

0
.
0
0
5
0
6
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

0
.
0
0
5
6
5
0

0
.
0
8
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
8
.
7

1
4
4
0
28
.
5
0-
0
02
8
.
5
50

2
.
0
0
0.
0
1
9
8

2
8
.
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

5
.
1
0

1
0
.
2
0.
2
0
2
0-
0
00
.
2
0
2
2.
0
0

2
.
0
0
0.
0
0
0
7
9
3

0
.
2
0
3
0
2.
9
2%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
1
6

3
3
.
2
0.
6
5
8
0-
0
00
.
6
5
8
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
6
6
2
0
9.
5
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
1
0.
1
3
3
0-
0
00
.
1
3
3
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

0
.
1
3
4
0
1.
9
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
N
i
t
r
o
a
n
i
l
i
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7

1
3
5
0
26
.
8
0-
0
02
6
.
8
50

2
.
0
0
0.
0
1
9
8

2
6
.
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
N
i
t
r
o
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
6
.
9

2
8
3
5.
6
1
0-
0
05
.
6
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

5
.
6
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
0
.
9

4
.
3
2
0.
0
8
5
8
0-
0
00
.
0
8
5
8
0.
1
4
0

2
.
0
0
0.
0
0
0
0
5
5
5

0
.
0
8
5
8
0
1.
2
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
3-
N
i
t
r
o
a
n
i
l
i
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
6
.
5

1
3
2
0
26
.
3
0-
0
02
6
.
3
50

2
.
0
0
0.
0
1
9
8

2
6
.
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
6

4
.
1
4
0.
0
8
2
2
0-
0
00
.
0
8
2
2
0.
1
5
0

2
.
0
0
0.
0
0
0
0
5
9
5

0
.
0
8
2
3
0
1.
2
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
2

1
6
0
0
31
.
8
0-
0
03
1
.
8
50

2
.
0
0
0.
0
1
9
8

3
1
.
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
4-
N
i
t
r
o
a
n
i
l
i
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
8
.
5

1
4
2
0
28
.
2
0-
0
02
8
.
2
50

2
.
0
0
0.
0
1
9
8

2
8
.
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
4-
N
i
t
r
o
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9
.
8

1
4
9
0
29
.
6
0-
0
02
9
.
6
50

2
.
0
0
0.
0
1
9
8

2
9
.
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
5

5
.
2
3
0.
1
0
4
0-
0
00
.
1
0
4
0.
1
9
0

2
.
0
0
0.
0
0
0
0
7
5
4

0
.
1
0
4
0
1.
5
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

H
M
X

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
0
0

2
5
0.
4
9
6
0-
0
00
.
4
9
6
25

2
.
0
0
0.
0
0
9
9
2

0
.
5
0
6
90
.
0
5
6
3
1
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Ni
t
r
o
b
e
n
z
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9
.
7

3
1
1
6.
1
8
0-
0
06
.
1
8
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
1
8
0
88
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Ni
t
r
o
g
l
y
c
e
r
i
n
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
6
.
6

9
.
0
5
0.
1
8
0
0-
0
00
.
1
8
0
0.
3
4
0

2
.
0
0
0.
0
0
0
1
3
5

0
.
1
8
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

N
i
t
r
o
g
u
a
n
i
d
i
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
4
.
2

7
.
2
7
0.
1
4
4
0-
0
00
.
1
4
4
0.
3
0
0

2
.
0
0
0.
0
0
0
1
1
9

0
.
1
4
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
PE
T
N
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
6

1
3
.
8
0.
2
7
3
0-
0
00
.
2
7
3
0.
5
0
0

2
.
0
0
0.
0
0
0
1
9
8

0
.
2
7
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

P
i
c
r
i
c

a
c
i
d

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
6
.
4

1
3
.
2
0.
2
6
2
0-
0
00
.
2
6
2
0.
5
0
0

2
.
0
0
0.
0
0
0
1
9
8

0
.
2
6
2
NS
V
--
7%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
RD
X
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
3
1.
7
3
0-
0
01
.
7
3
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

1
.
7
3
0
25
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Te
t
r
y
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9
.
1

6
.
6
9
0.
1
3
3
0-
0
00
.
1
3
3
0.
2
3
0

2
.
0
0
0.
0
0
0
0
9
1
3

0
.
1
3
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

E
n
e
r
g
e
t
i
c
s
3.
0
(d
e
t
s
)
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

A
l
u
m
i
n
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
3
4
0

1
8
4
0
0
36
4
0-
0
0

3
6
4
54
0
0
0

2
.
0
0
21
.
4

3
8
6
11
0
3.
5
10
0
%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

A
n
t
i
m
o
n
y

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
0
2
5
0

4
.
1
7
0.
0
8
2
8
0-
0
0

0
.
0
8
2
8
16
7

2
.
0
0
0.
0
6
6
2

0
.
1
4
9
NS
V
--
79
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

A
r
s
e
n
i
c

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
3
4
0.
0
6
6
3
0-
0
0

0
.
0
6
6
3
41
.
3

2
.
0
0
0.
0
1
6
4

0
.
0
8
2
6
9

<
0
.
0
1

5
8
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

B
a
r
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
3
6
0

2
3
0
4.
5
7
0-
0
04
.
5
7
64
0

2
.
0
0
0.
2
5
4

4
.
8
2
21

0
.
2
3

1
0
0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

B
e
r
y
l
l
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
1
8

0
.
8
5
1
0.
0
1
6
9
0-
0
00
.
0
1
6
9
0.
7
2
0

2
.
0
0
0.
0
0
0
2
8
6

0
.
0
1
7
2
NS
V
--
48
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

C
a
d
m
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
3
0
2.
5
8
0-
0
02
.
5
8
32

2
.
0
0
0.
0
1
2
7

2
.
6
0
0
16
44
%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
1

0
.
0
2
9
9
0.
0
0
0
5
9
2
0-
0
0

0
.
0
0
0
5
9
2
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
4
3
6

0
.
0
0
0
5
9
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

C
h
r
o
m
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
1
6

1
7
5
3.
4
7
0-
0
03
.
4
7
55
.
3

2
.
0
0
0.
0
2
1
9

3
.
4
9
1
3.
5
10
0
%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

C
o
b
a
l
t

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
2
9
1

1
.
4
3
0.
0
2
8
3
0-
0
0

0
.
0
2
8
3
4.
9
0

2
.
0
0
0.
0
0
1
9
4

0
.
0
3
0
2
8

<
0
.
0
1

7
9
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

C
o
p
p
e
r

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
0
.
9
1.
4
1
0-
0
01
.
4
1
18
0
0
0

2
.
0
0
7.
1
4

8
.
5
5
47

0
.
1
8

8
5
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

I
r
o
n

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
3
8
0

5
7
0
0
11
3
0-
0
0

1
1
3
15
0
0
0

2
.
0
0
5.
9
5

1
1
9
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

L
e
a
d

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
8
2
0
95
.
6
0-
0
09
5
.
6
48
0
0
0

2
.
0
0
19

1
1
5
0
60
0
83
%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

M
a
g
n
e
s
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
4
2
5

1
0
3
0
0
20
5
0-
0
0

2
0
5
24
3
0
0

2
.
0
0
9.
6
4

2
1
5
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

M
a
n
g
a
n
e
s
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
.
7
0.
6
2
8
0-
0
00
.
6
2
8
51
9

2
.
0
0
0.
2
0
6

0
.
8
3
4
97
7

<
0
.
0
1

1
0
0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

M
e
r
c
u
r
y

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
3
6
9
0.
0
0
7
3
1
0-
0
0

0
.
0
0
7
3
1
0.
0
7
0
0

2
.
0
0
0.
0
0
0
0
2
7
8

0
.
0
0
7
3
4
0

0
.
1
1

2
7
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

M
o
l
y
b
d
e
n
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
0
9

3
5
.
5
0.
7
0
5
0-
0
00
.
7
0
5
17

2
.
0
0
0.
0
0
6
7
4

0
.
7
1
2
4

0
.
2
0

9
1
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

N
i
c
k
e
l

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

4
.
7
3

1
9
5
3.
8
8
0-
0
03
.
8
8
41
.
3

2
.
0
0
0.
0
1
6
4

3
.
8
9
18

0
.
2
2

1
0
0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

N
i
t
r
a
t
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
0
0

2
2
.
8
0.
4
5
2
0-
0
00
.
4
5
2
22
.
8

2
.
0
0
0.
0
0
9
0
5

0
.
4
6
1
NS
V
--
92
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

P
e
r
c
h
l
o
r
a
t
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
0
0

4
.
5
0
0.
0
8
9
3
0-
0
0

0
.
0
8
9
3
4.
5
0

2
.
0
0
0.
0
0
1
7
9

0
.
0
9
1
1
3

0
.
0
2
8

5
0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

P
h
o
s
p
h
o
r
u
s

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
0
0

9
9
0
19
.
6
0-
0
01
9
.
6
99
0

2
.
0
0
0.
3
9
3

2
0
0
54
0
10
0
%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Se
l
e
n
i
u
m
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
2
0.
0
5
9
9
0-
0
00
.
0
5
9
9
5.
0
0

2
.
0
0
0.
0
0
1
9
8

0
.
0
6
1
9
00
.
1
5
0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

S
i
l
v
e
r

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
5
.
3

6
1
.
4
1.
2
2
0-
0
01
.
2
2
4.
0
0

2
.
0
0
0.
0
0
1
5
9

1
.
2
2
NS
V
--
8%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

S
t
r
o
n
t
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
2
7
8

1
3
5
2.
6
7
0-
0
02
.
6
7
48
4

2
.
0
0
0.
1
9
2

2
.
8
6
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

T
h
a
ll
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
2
5
6

0
.
1
4
1
0.
0
0
2
7
9
0-
0
0

0
.
0
0
2
7
9
0.
5
5
0

2
.
0
0
0.
0
0
0
2
1
8

0
.
0
0
3
0
1
1

<
0
.
0
1

5
4
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

V
a
n
a
d
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
0
8
8
0

2
.
2
6
0.
0
4
4
9
0-
0
0

0
.
0
4
4
9
25
.
7

2
.
0
0
0.
0
1
0
2

0
.
0
5
5
1
11

<
0
.
0
1

1
0
0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Zi
n
c

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
8
0
21
.5
0-
0
0
21
.5
23
0
0

2
.
0
0
0.
9
1
3

2
2
.
4
15
1.
5
10
0
%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

I
n
o
r
g
a
n
i
c
s
12
0
0
(d
e
t
s
)
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9

4
9
4
0
97
.
9
0-
0
09
7
.
9
17
0

2
.
0
0
0.
0
6
7
4

9
8
27
3.
6
14
%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

A
c
e
n
a
p
h
t
h
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
4
7

0
.
0
6
1
5
0.
0
0
1
2
2
0-
0
0

0
.
0
0
1
2
2
0.
0
4
1
8

2
.
0
0
0.
0
0
0
0
1
6
6

0
.
0
0
1
2
4
32
5

<
0
.
0
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Ac
e
n
a
p
h
t
h
y
l
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
2
.
9

2
4
0
4.
7
7
0-
0
04
.
7
7
10
.
5

2
.
0
0
0.
0
0
4
1
7

4
.
7
7
32
5

0
.
0
1
5

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

A
n
t
h
r
a
c
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
4
2

8
.
9
5
0.
1
7
8
0-
0
00
.
1
7
8
3.
7
0

2
.
0
0
0.
0
0
1
4
7

0
.
1
7
9
32
5

<
0
.
0
1

7
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
5
9

1
6
.
7
0.
3
3
1
0-
0
00
.
3
3
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
3
3
5
32
5

<
0
.
0
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
3
3

1
4
0.
2
7
7
0-
0
00
.
2
7
7
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
2
8
1
32
5

<
0
.
0
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
6
0

2
7
.
3
0.
5
4
2
0-
0
00
.
5
4
2
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
5
4
6
32
5

<
0
.
0
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
9
4

3
0
.
9
0.
6
1
2
0-
0
00
.
6
1
2
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
6
1
7
32
5

<
0
.
0
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
6
0

2
7
.
3
0.
5
4
2
0-
0
00
.
5
4
2
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
5
4
6
32
5

<
0
.
0
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Ch
r
y
s
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
2
9

2
4
0.
4
7
7
0-
0
00
.
4
7
7
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
4
8
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
3
1

2
4
.
3
0.
4
8
1
0-
0
00
.
4
8
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
4
8
5
32
5

<
0
.
0
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

F
l
u
o
r
a
n
t
h
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
0
4

0
.
4
3
8
0.
0
0
8
6
8
0-
0
0

0
.
0
0
8
6
8
0.
1
4
4

2
.
0
0
0.
0
0
0
0
5
7
1

0
.
0
0
8
7
4
32
5

<
0
.
0
1

4
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

F
l
u
o
r
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

9
.
5
7

3
1
6
6.
2
6
0-
0
06
.
2
6
33

2
.
0
0
0.
0
1
3
1

6
.
2
8
32
5

0
.
0
1
9

1
4
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
8
6

3
0
0.
5
9
6
0-
0
00
.
5
9
6
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
6
0
0
32
5

<
0
.
0
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

N
a
p
h
t
h
a
l
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

4
.
4
0

2
3
3
4.
6
3
0-
0
04
.
6
3
53

2
.
0
0
0.
0
2
1
0

4
.
6
5
27

0
.
1
7

2
5
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

P
h
e
n
a
n
t
h
r
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
7
2

1
5
8
3.
1
4
0-
0
03
.
1
4
92

2
.
0
0
0.
0
3
6
5

3
.
1
8
32
5

<
0
.
0
1

1
8
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Py
r
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
7
5

1
8
.
4
0.
3
6
5
0-
0
00
.
3
6
5
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
3
6
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

P
A
H
s
3.
8
(d
e
t
s
)
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
TP
H
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

-

0
0
0-
0
00
47
0
0
0

2
.
0
0
18
.
6

1
8
.
6
50
0

0
.
0
3
7

1
0
0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

P
e
t
r
o
l
e
u
m
0.
0
3
7
(d
e
t
s
)
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
5
.
1

1
7
6
0
34
.
8
0-
0
03
4
.
8
50

2
.
0
0
0.
0
1
9
8

3
4
.
8
17
2.
1
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
5
.
6

3
7
4
7.
4
1
0-
0
07
.
4
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

7
.
4
2
17

0
.
4
4

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
2
.
6

3
4
2
6.
7
9
0-
0
06
.
7
9
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
7
9
17

0
.
4
0

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
2
.
3

3
4
0
6.
7
4
0-
0
06
.
7
4
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
7
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
8

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
C
h
l
o
r
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1
0
3

0
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0
2
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1

0
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0
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0

-

0

0

1
0
0

3
6

3
7
8
7.
5
0
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0
07
.
5
0
10
.
5

2
.
0
0
0.
0
0
4
1
7

7
.
5
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
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n

M
e
a
d
o
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l
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k
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M
e
t
h
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0.
1
0
3

0
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0
2
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1

0
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0
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0

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0

0

1
0
0

2
7
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1

2
8
4
5.
6
4
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0
05
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6
4
10
.
5

2
.
0
0
0.
0
0
4
1
7

5
.
6
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
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n

M
e
a
d
o
w
l
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k
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3
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D
i
c
h
l
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o
b
e
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z
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d
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n
e
0.
1
0
3

0
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0
2
0

1

0
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0
2
0

0

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0

0

1
0
0

2
8
.
8

6
0
5
12
0-
0
01
2
21

2
.
0
0
0.
0
0
8
3
3

1
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
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k
4-
C
h
l
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3
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m
e
t
h
y
l
p
h
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l
0.
1
0
3

0
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0
2
0

1

0
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0
2
0

0

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0

0

1
0
0

3
3
.
2

3
4
9
6.
9
1
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0
06
.
9
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
9
2
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
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n

M
e
a
d
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w
l
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k
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C
h
l
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n
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l
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0.
1
0
3

0
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0
2
0

1

0
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0
2
0

0

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0

0

1
0
0

2
9
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6

3
1
1
6.
1
7
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0
06
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1
7
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
1
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
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k
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M
e
t
h
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l
p
h
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0.
1
0
3

0
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0
2
0

1

0
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0
2
0

0

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0

0

1
0
0

2
9
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9

3
1
4
6.
2
2
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0
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2
2
10
.
5

2
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0
0
0.
0
0
4
1
7

6
.
2
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
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n

M
e
a
d
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w
l
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k
Be
n
z
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a
c
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0.
1
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3

0
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0
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1

0
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0

0

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0

0

1
0
0

2
9
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7

1
4
9
0
29
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5
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0
02
9
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5
50

2
.
0
0
0.
0
1
9
8

2
9
.
5
32
5

0
.
0
9
1

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
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l
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k
Be
n
z
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l
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l
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1
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3

0
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0
2
0

1

0
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0
2
0

0

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0

0

1
0
0

2
7
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7

2
9
1
5.
7
7
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0
05
.
7
7
10
.
5

2
.
0
0
0.
0
0
4
1
7

5
.
7
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k

b
i
s
(
2
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E
t
h
y
l
h
e
x
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l
)
p
h
t
h
a
l
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0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
3
.
4

5
0
.
1
0.
9
9
4
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0
00
.
9
9
4
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

0
.
9
9
5
1

0
.
9
0

1
8
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
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e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8
.
8

4
0
8
8.
0
9
0-
0
08
.
0
9
10
.
5

2
.
0
0
0.
0
0
4
1
7

8
.
0
9
0
74
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

D
i
b
e
n
z
o
f
u
r
a
n

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9

3
4
8
6.
9
1
0-
0
06
.
9
1
12

2
.
0
0
0.
0
0
4
7
6

6
.
9
1
NS
V
--
14
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
1
.
3

3
2
9
6.
5
3
0-
0
06
.
5
3
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
5
3
0
59
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
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e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
8
.
9

3
0
3
6.
0
2
0-
0
06
.
0
2
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
0
2
0
55
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
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e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8

3
9
9
7.
9
2
0-
0
07
.
9
2
10
.
5

2
.
0
0
0.
0
0
4
1
7

7
.
9
3
0
72
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
Di
-
n
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o
c
t
y
l
p
h
t
h
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l
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e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

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0

0

1
0
0

3
0
.
8

3
2
3
6.
4
1
0-
0
06
.
4
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
4
2
0
58
0%
Re
t
a
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n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
He
x
a
c
h
l
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b
e
n
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0.
1
0
3

0
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0
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0

1

0
.
0
2
0

0

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0

0

1
0
0

4
0
.
2

4
2
2
8.
3
8
0-
0
08
.
3
8
10
.
5

2
.
0
0
0.
0
0
4
1
7

8
.
3
8
1
15
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
He
x
a
c
h
l
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b
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t
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d
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e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8
.
6

0
.
0
3
0
9
0.
0
0
0
6
1
3
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0
0

0
.
0
0
0
6
1
3
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
1
7

0
.
0
0
0
6
1
3
1

<
0
.
0
1

4
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
He
x
a
c
h
l
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c
y
c
l
o
p
e
n
t
a
d
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e
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e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
6

3
7
8
7.
5
0
0-
0
07
.
5
0
10
.
5

2
.
0
0
0.
0
0
4
1
7

7
.
5
0
1
13
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
He
x
a
c
h
l
o
r
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e
t
h
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n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8

3
9
9
7.
9
1
0-
0
07
.
9
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

7
.
9
2
1
14
0%
Re
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
Is
o
p
h
o
r
o
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

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0

0

1
0
0

3
0
.
8

3
2
3
6.
4
1
0-
0
06
.
4
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
4
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
n-
N
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t
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s
o
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d
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n
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p
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p
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l
a
m
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n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

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0

0

1
0
0

2
8
.
7

3
0
1
5.
9
8
0-
0
05
.
9
8
10
.
5

2
.
0
0
0.
0
0
4
1
7

5
.
9
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
n-
N
i
t
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s
o
d
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p
h
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y
l
a
m
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n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
3
.
3

3
4
9
6.
9
3
0-
0
06
.
9
3
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
9
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
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k
Pe
n
t
a
c
h
l
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r
o
p
h
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l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

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0

0

1
0
0

5
.
9
3

2
9
7
5.
8
8
0-
0
05
.
8
8
50

2
.
0
0
0.
0
1
9
8

5
.
9
0
17

0
.
3
5

0
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

S
V
O
C
s
0.
9
1
(d
e
t
s
)
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
1,
1
,
1
,
2
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T
e
t
r
a
c
h
l
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r
o
e
t
h
a
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
8
.
3

0
.
0
1
7
0
0.
0
0
0
3
3
6
0-
0
0

0
.
0
0
0
3
3
6
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
2
3
8

0
.
0
0
0
3
3
7
17

<
0
.
0
1

5
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
1,
1
,
1
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T
r
i
c
h
l
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r
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e
t
h
a
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
1
.
4

0
.
0
2
8
3
0.
0
0
0
5
6
1
0-
0
0

0
.
0
0
0
5
6
1
0.
0
0
0
9
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
5
6
2
17

<
0
.
0
1

5
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
1
.
1

0
.
0
3
1
1
0.
0
0
0
6
1
8
0-
0
0

0
.
0
0
0
6
1
8
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
9
7

0
.
0
0
0
6
1
8
17

<
0
.
0
1

5
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
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M
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17

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5
%
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M
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2
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6
17

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5
%
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M
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0
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6
3
17

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5
%
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M
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2
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7

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0
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2
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0
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17

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5
%
Pa
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s
We
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n

M
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2
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4
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1
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0
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3
7

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0
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0
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5
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0
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2
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0
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7

0
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0
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3
5
17

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0
1

4
%
Pa
s
s
We
s
t
e
r
n

M
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a
d
o
w
l
a
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1,
2
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D
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b
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3
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1
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3
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9

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9
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9
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2
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0
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0.
0
0
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5
5

0
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0
0
2
3
9
NS
V
--
5%
Un
c
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a
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n
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n

M
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1
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0
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2
8
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7

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0
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0
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2
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0
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5
5

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0
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9
6
17

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4
%
Pa
s
s
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s
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n

M
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2
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1
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2
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7

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0
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5
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0
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8
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2
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7

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0
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5
6
17

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5
%
Pa
s
s
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s
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r
n

M
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1,
2
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1
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0
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3
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2
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7
8

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8
17

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0
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5
%
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s
s
We
s
t
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n

M
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2
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t
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1
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0
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2
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9

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2
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0
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5
7

0
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0
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0
4
8
0
NS
V
--
5%
Un
c
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t
a
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n
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n

M
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3
4
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7

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2
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0
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4

0
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0
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17

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4
%
Pa
s
s
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s
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r
n

M
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1,
4
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1
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3
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7

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2
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17

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4
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Pa
s
s
We
s
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n

M
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a
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2
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0
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0
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0
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4

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4
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2
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1

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0
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8
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1
39

<
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1
8
%
Pa
s
s
We
s
t
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r
n

M
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a
d
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l
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1
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2
6
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3

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5
6
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9
5

2
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0
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3
6

0
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0
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0
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V
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t
a
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n
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n

M
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1
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1

0
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3
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6

3
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1
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3
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06
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3
6
10
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5

2
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0
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0
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4
1
7

6
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3
7
17

0
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3
8

0
%
Pa
s
s
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s
t
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r
n

M
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a
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1
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0
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1

0
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2
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1

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0
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39

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5
%
Pa
s
s
We
s
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n

M
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a
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1
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3
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3
6
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5

2
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0
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7

6
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3
6
NS
V
--
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t
a
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n

M
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3
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3

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.
5
5
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5

2
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0
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7
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5
6
NS
V
--
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t
a
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n
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n

M
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1
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2
6
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3

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0
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2
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39

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5
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n

M
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A
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0
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2
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9

5
9
7
11
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8
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1
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8
24

2
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1
1
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8
39

0
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3
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3
2
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s
s
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s
t
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n

M
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B
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0
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2
2
10

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1
4
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Pa
s
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n

M
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a
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Bi
s
(
2
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h
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)
m
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1
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0
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4
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2
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0
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4

0
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0
3
8
8
NS
V
--
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c
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t
a
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n

M
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a
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2
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5
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9
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M
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2
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2
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6
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3
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M
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3
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17

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17

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17

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17

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17

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17

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2
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10

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5
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M
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2
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9
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10

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5
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M
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2
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7

0
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0
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7
8
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5%
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0
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1
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2
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2
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2
10

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1
4
%
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M
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Ph
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0.
1
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3

0
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2
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6

3
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9
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9
6
10
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5

2
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0
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7

5
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9
7
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--
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n

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0
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1
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1

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2
8
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1

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0
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0
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2
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0
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3

0
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0
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1
4
5
NS
V
--
14
%
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c
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t
a
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n
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n

M
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1
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2
6
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4

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0
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6
6
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2
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7
8

0
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6
6
NS
V
--
5%
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t
a
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n
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n

M
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1
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0
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0

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2
8
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7

0
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0
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0
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1
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0
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9
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2
.
0
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0
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3
5
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0
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2
17

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0
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0
1

5
%
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n

M
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w
l
a
r
k

T
o
l
u
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
9

0
.
5
2
2
0.
0
1
0
4
0-
0
0

0
.
0
1
0
4
0.
0
1
8
7

2
.
0
0
0.
0
0
0
0
0
7
4
2

0
.
0
1
0
4
10

<
0
.
0
1

2
3
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

1
9

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
2
0
1
0.
0
0
0
3
9
8
0-
0
0

0
.
0
0
0
3
9
8
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
2
7
8

0
.
0
0
0
3
9
9
17

<
0
.
0
1

5
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
0
.
1

0
.
0
2
4
0
0.
0
0
0
4
7
7
0-
0
0

0
.
0
0
0
4
7
7
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
1
7

0
.
0
0
0
4
7
7
17

<
0
.
0
1

5
%
Pa
s
s
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
1
.
2

0
.
0
2
1
9
0.
0
0
0
4
3
4
0-
0
0

0
.
0
0
0
4
3
4
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
2
7
8

0
.
0
0
0
4
3
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
1
.
5

0
.
0
3
4
7
0.
0
0
0
6
8
8
0-
0
0

0
.
0
0
0
6
8
8
0.
0
0
1
1
0

2
.
0
0
0.
0
0
0
0
0
0
4
3
6

0
.
0
0
0
6
8
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Vi
n
y
l

A
c
e
t
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
6
.
2

0
.
0
3
1
4
0.
0
0
0
6
2
3
0-
0
0

0
.
0
0
0
6
2
3
0.
0
0
1
2
0

2
.
0
0
0.
0
0
0
0
0
0
4
7
6

0
.
0
0
0
6
2
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
8
.
4

0
.
0
3
4
1
0.
0
0
0
6
7
7
0-
0
0

0
.
0
0
0
6
7
7
0.
0
0
1
2
0

2
.
0
0
0.
0
0
0
0
0
0
4
7
6

0
.
0
0
0
6
7
7
NS
V
--
5%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

V
O
C
s
0.
6
8
(d
e
t
s
)
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
8
8
0

0
.
0
9
2
4

0
.
0
1
0
3

0

-

0
0
0-
0
0

0
.
0
1
0
3
0.
1
0
5

5
.
0
0
0.
0
0
0
5
8
3

0
.
0
1
0
8
00
.
1
5
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
3
2

0
.
1
0
6

0
.
0
1
1
8

0

-

0
0
0-
0
0

0
.
0
1
1
8
0.
0
8
0
0

5
.
0
0
0.
0
0
0
4
4
4

0
.
0
1
2
2
0

0
.
0
2
9

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
1.
5
0

5
.
0
0
0.
0
0
8
3
3

0
.
0
0
8
3
3
00
.
1
2
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
8
8

3
4
.
4

3
.
8
2

0

-

0
0
0-
0
03
.
8
2
50

5
.
0
0
0.
2
7
8

4
.
1
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
5

2
.
1
1

0
.
2
3
4

0

-

0
0
0-
0
00
.
2
3
4
2.
0
0

5
.
0
0
0.
0
1
1
1

0
.
2
4
5
0
3.
5
2%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
0

1
1
.
5

1
.
2
8

0

-

0
0
0-
0
01
.
2
8
10
.
5

5
.
0
0
0.
0
5
8
3

1
.
3
4
0
19
0%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
8

1
.
7
7

0
.
1
9
6

0

-

0
0
0-
0
00
.
1
9
6
1.
5
0

5
.
0
0
0.
0
0
8
3
3

0
.
2
0
5
0
2.
9
0%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2-
N
i
t
r
o
a
n
i
l
i
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
7

5
8
.
7

6
.
5
2

0

-

0
0
0-
0
06
.
5
2
50

5
.
0
0
0.
2
7
8

6
.
8
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2-
N
i
t
r
o
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
2
0

1
2
.
6

1
.
4
0

0

-

0
0
0-
0
01
.
4
0
10
.
5

5
.
0
0
0.
0
5
8
3

1
.
4
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
7
1

0
.
0
5
2
0

0
.
0
0
5
7
7

0

-

0
0
0-
0
0

0
.
0
0
5
7
7
0.
1
4
0

5
.
0
0
0.
0
0
0
7
7
7

0
.
0
0
6
5
5
0

0
.
0
9
4

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
3-
N
i
t
r
o
a
n
i
l
i
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
3
8

6
8
.
9

7
.
6
5

0

-

0
0
0-
0
07
.
6
5
50

5
.
0
0
0.
2
7
8

7
.
9
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
9
6
1

0
.
1
4
4

0
.
0
1
6
0

0

-

0
0
0-
0
0

0
.
0
1
6
0
0.
1
5
0

5
.
0
0
0.
0
0
0
8
3
3

0
.
0
1
6
8
00
.
2
4
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
2
7
3

1
3
.
7

1
.
5
2

0

-

0
0
0-
0
01
.
5
2
50

5
.
0
0
0.
2
7
8

1
.
8
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
4-
N
i
t
r
o
a
n
i
l
i
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
7
4
9

3
7
.
4

4
.
1
6

0

-

0
0
0-
0
04
.
1
6
50

5
.
0
0
0.
2
7
8

4
.
4
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
4-
N
i
t
r
o
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
0
1

2
5
.
1

2
.
7
8

0

-

0
0
0-
0
02
.
7
8
50

5
.
0
0
0.
2
7
8

3
.
0
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
9
9
0

0
.
1
8
8

0
.
0
2
0
9

0

-

0
0
0-
0
0

0
.
0
2
0
9
0.
1
9
0

5
.
0
0
0.
0
0
1
0
6

0
.
0
2
2
0
00
.
3
1
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

H
M
X

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

2
.
1
3

5
3
.
4

5
.
9
3

0

-

0
0
0-
0
05
.
9
3
25

5
.
0
0
0.
1
3
9

6
.
0
7
9

0
.
6
7

3
1
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Ni
t
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
2
5

5
.
5
1

0
.
6
1
2

0

-

0
0
0-
0
00
.
6
1
2
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
6
7
1
0
9.
6
0%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Ni
t
r
o
g
l
y
c
e
r
i
n
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
3
2

0
.
4
4
7

0
.
0
4
9
7

0

-

0
0
0-
0
0

0
.
0
4
9
7
0.
3
4
0

5
.
0
0
0.
0
0
1
8
9

0
.
0
5
1
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

N
i
t
r
o
g
u
a
n
i
d
i
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

2
.
9
3

0
.
8
7
9

0
.
0
9
7
7

0

-

0
0
0-
0
0

0
.
0
9
7
7
0.
3
0
0

5
.
0
0
0.
0
0
1
6
7

0
.
0
9
9
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
PE
T
N
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
9
8
4

0
.
4
9
2

0
.
0
5
4
6

0

-

0
0
0-
0
0

0
.
0
5
4
6
0.
5
0
0

5
.
0
0
0.
0
0
2
7
8

0
.
0
5
7
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

P
i
c
r
i
c

a
c
i
d

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
4
0

0
.
6
9
8

0
.
0
7
7
6

0

-

0
0
0-
0
0

0
.
0
7
7
6
0.
5
0
0

5
.
0
0
0.
0
0
2
7
8

0
.
0
8
0
3
NS
V
--
7%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
RD
X
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
1.
5
0

5
.
0
0
0.
0
0
8
3
3

0
.
0
0
8
3
3
00
.
1
2
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Te
t
r
y
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
1
7

0
.
1
4
2

0
.
0
1
5
8

0

-

0
0
0-
0
0

0
.
0
1
5
8
0.
2
3
0

5
.
0
0
0.
0
0
1
2
8

0
.
0
1
7
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

E
n
e
r
g
e
t
i
c
s
4.
2
(d
e
t
s
)
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

A
l
u
m
i
n
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
7
3
2

3
9
5
0

4
3
9

0

-

0
0
0-
0
0

4
3
9
54
0
0
0

5
.
0
0
30
0

7
3
9
11
0
6.
7
10
0
%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

A
n
t
i
m
o
n
y

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
0

1
6
7

1
8
.
5

0

-

0
0
0-
0
01
8
.
5
16
7

5
.
0
0
0.
9
2
7

1
9
.
5
NS
V
--
79
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

A
r
s
e
n
i
c

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
1
6
5

0
.
0
1
8
4

0

-

0
0
0-
0
0

0
.
0
1
8
4
41
.
3

5
.
0
0
0.
2
2
9

0
.
2
4
8
9

0
.
0
2
7

5
8
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

B
a
r
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
1
2

7
1
.
7

7
.
9
7

0

-

0
0
0-
0
07
.
9
7
64
0

5
.
0
0
3.
5
5

1
1
.
5
21

0
.
5
5

1
0
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

B
e
r
y
l
l
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
1
0

0
.
2
9
5

0
.
0
3
2
8

0

-

0
0
0-
0
0

0
.
0
3
2
8
0.
7
2
0

5
.
0
0
0.
0
0
4
0
0

0
.
0
3
6
8
NS
V
--
48
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

C
a
d
m
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
6
1

0
.
4
0
0

0

-

0
0
0-
0
00
.
4
0
0
32

5
.
0
0
0.
1
7
8

0
.
5
7
8
0
3.
6
44
%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
2

0
.
0
0
1
2
3

0
.
0
0
0
1
3
6

0

-

0
0
0-
0
0

0
.
0
0
0
1
3
6
0.
0
0
1
1
0

5
.
0
0
0.
0
0
0
0
0
6
1
1

0
.
0
0
0
1
4
3
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

C
h
r
o
m
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
3
3

1
8
.
4

2
.
0
5

0

-

0
0
0-
0
02
.
0
5
55
.
3

5
.
0
0
0.
3
0
7

2
.
3
5
1
2.
4
10
0
%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

C
o
b
a
l
t

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
0
9
1
7

0
.
0
1
0
2

0

-

0
0
0-
0
0

0
.
0
1
0
2
4.
9
0

5
.
0
0
0.
0
2
7
2

0
.
0
3
7
4
8

<
0
.
0
1

7
9
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

C
o
p
p
e
r

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
.
7

3
.
5
2

0

-

0
0
0-
0
03
.
5
2
18
0
0
0

5
.
0
0
10
0

1
0
3
47
2.
2
85
%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

I
r
o
n

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
3
3

2
5
.
9

0

-

0
0
0-
0
02
5
.
9
15
0
0
0

5
.
0
0
83
.
3

1
0
9
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

L
e
a
d

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
7

1
4
.
1

0

-

0
0
0-
0
01
4
.
1
48
0
0
0

5
.
0
0
26
7

2
8
1
0
15
0
0
83
%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

M
a
g
n
e
s
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
9
9
2

2
4
1
0
0

2
6
8
0

0

-

0
0
0-
0
0

2
6
8
0
24
3
0
0

5
.
0
0
13
5

2
8
1
0
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

M
a
n
g
a
n
e
s
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
7
9
0

4
1

4
.
5
5

0

-

0
0
0-
0
04
.
5
5
51
9

5
.
0
0
2.
8
8

7
.
4
4
97
7

<
0
.
0
1

1
0
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

M
e
r
c
u
r
y

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
9
2

0
.
0
1
3
4

0
.
0
0
1
4
9

0

-

0
0
0-
0
0

0
.
0
0
1
4
9
0.
0
7
0
0

5
.
0
0
0.
0
0
0
3
8
9

0
.
0
0
1
8
8
0

0
.
0
2
8

2
7
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

M
o
l
y
b
d
e
n
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
0

1
7

1
.
8
9

0

-

0
0
0-
0
01
.
8
9
17

5
.
0
0
0.
0
9
4
4

1
.
9
8
40
.
5
7
9
1
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

N
i
c
k
e
l

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
8
9

2
4
.
3

2
.
7
0

0

-

0
0
0-
0
02
.
7
0
41
.
3

5
.
0
0
0.
2
2
9

2
.
9
3
18

0
.
1
7

1
0
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

N
i
t
r
a
t
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
0

2
2
.
8

2
.
5
3

0

-

0
0
0-
0
02
.
5
3
22
.
8

5
.
0
0
0.
1
2
7

2
.
6
6
NS
V
--
92
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

P
e
r
c
h
l
o
r
a
t
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
0
0

0
.
4
5
0

0
.
0
5
0
0

0

-

0
0
0-
0
0

0
.
0
5
0
0
4.
5
0

5
.
0
0
0.
0
2
5
0

0
.
0
7
5
0
3

0
.
0
2
3

5
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

P
h
o
s
p
h
o
r
u
s

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
0

9
9
0

1
1
0

0

-

0
0
0-
0
0

1
1
0
99
0

5
.
0
0
5.
5
0

1
1
5
0
31
0
0
10
0
%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Se
l
e
n
i
u
m
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
2
1

0
.
1
3
4

0

-

0
0
0-
0
00
.
1
3
4
5.
0
0

5
.
0
0
0.
0
2
7
8

0
.
1
6
2
00
.
4
1
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

S
i
l
v
e
r

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
8
1
0

3
.
2
4

0
.
3
6
0

0

-

0
0
0-
0
00
.
3
6
0
4.
0
0

5
.
0
0
0.
0
2
2
2

0
.
3
8
2
NS
V
--
8%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

S
t
r
o
n
t
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
0

4
8
4

5
3
.
8

0

-

0
0
0-
0
05
3
.
8
48
4

5
.
0
0
2.
6
9

5
6
.
4
NS
V
--
10
0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

T
h
a
l
l
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
2
3

0
.
0
6
7
5

0
.
0
0
7
4
9

0

-

0
0
0-
0
0

0
.
0
0
7
4
9
0.
5
5
0

5
.
0
0
0.
0
0
3
0
5

0
.
0
1
0
5
1

0
.
0
1
8

5
4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

V
a
n
a
d
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
1
9
5

0
.
5
0
0

0
.
0
5
5
6

0

-

0
0
0-
0
0

0
.
0
5
5
6
25
.
7

5
.
0
0
0.
1
4
3

0
.
1
9
8
11

0
.
0
1
7

1
0
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

Z
i
n
c

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
5
5

1
7
.
2

0

-

0
0
0-
0
0
17
.2
23
0
0

5
.
0
0
12
.
8

3
0
15
2.
1
10
0
%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

I
n
o
r
g
a
n
i
c
s
46
0
0
(d
e
t
s
)
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
2
9

1
0
7

1
1
.
9

0

-

0
0
0-
0
01
1
.
9
17
0

5
.
0
0
0.
9
4
4

1
2
.
8
27

0
.
4
8

1
4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

A
c
e
n
a
p
h
t
h
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
0.
0
4
1
8

5
.
0
0
0.
0
0
0
2
3
2

0
.
0
0
0
2
3
2
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Ac
e
n
a
p
h
t
h
y
l
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

A
n
t
h
r
a
c
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
3.
7
0

5
.
0
0
0.
0
2
0
5

0
.
0
2
0
5
32
5

<
0
.
0
1

7
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Ch
r
y
s
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

F
l
u
o
r
a
n
t
h
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
0.
1
4
4

5
.
0
0
0.
0
0
0
8
0
0

0
.
0
0
0
8
0
0
32
5

<
0
.
0
1

4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

F
l
u
o
r
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
33

5
.
0
0
0.
1
8
3

0
.
1
8
3
32
5

<
0
.
0
1

1
4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

N
a
p
h
t
h
a
l
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
53

5
.
0
0
0.
2
9
4

0
.
2
9
4
27

0
.
0
1
1

2
5
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

2
0

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Bu
r
r
o
w
i
n
g

O
w
l

P
h
e
n
a
n
t
h
r
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
92

5
.
0
0
0.
5
1
1

0
.
5
1
1
32
5

<
0
.
0
1

1
8
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Py
r
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0

0

0

0

-

0
0
0-
0
00
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
0
5
8
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

P
A
H
s
0.
4
9
(d
e
t
s
)
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
TP
H
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

-

0

0

0

-

0
0
0-
0
00
47
0
0
0

5
.
0
0
26
1

2
6
1
50
0

0
.
5
2

1
0
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

P
e
t
r
o
l
e
u
m
0.
5
2
(d
e
t
s
)
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
2
5

6
.
2
4

0
.
6
9
3

0

-

0
0
0-
0
00
.
6
9
3
50

5
.
0
0
0.
2
7
8

0
.
9
7
0
17

0
.
0
5
7

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
1
1

1
.
1
7

0
.
1
3
0

0

-

0
0
0-
0
00
.
1
3
0
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
8
8
17

0
.
0
1
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
2
3
4

2
.
4
6

0
.
2
7
3

0

-

0
0
0-
0
00
.
2
7
3
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
3
3
2
17

0
.
0
2
0

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
2
5
1

2
.
6
4

0
.
2
9
3

0

-

0
0
0-
0
00
.
2
9
3
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
3
5
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
0
1

1
.
0
6

0
.
1
1
7

0

-

0
0
0-
0
00
.
1
1
7
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
7
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2-
M
e
t
h
y
l
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
4

1
1
.
9

1
.
3
2

0

-

0
0
0-
0
01
.
3
2
10
.
5

5
.
0
0
0.
0
5
8
3

1
.
3
8
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
7
5

1
4
.
2

1
.
5
7

0

-

0
0
0-
0
01
.
5
7
21

5
.
0
0
0.
1
1
7

1
.
6
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
2
0
1

2
.
1
1

0
.
2
3
4

0

-

0
0
0-
0
00
.
2
3
4
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
2
9
3
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
4-
C
h
l
o
r
o
a
n
i
l
i
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
3
3

5
.
6
0

0
.
6
2
2

0

-

0
0
0-
0
00
.
6
2
2
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
6
8
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
4-
M
e
t
h
y
l
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
9
4

5
.
1
9

0
.
5
7
6

0

-

0
0
0-
0
00
.
5
7
6
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
6
3
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Be
n
z
o
i
c

a
c
i
d
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
1
7

2
5
.
9

2
.
8
7

0

-

0
0
0-
0
02
.
8
7
50

5
.
0
0
0.
2
7
8

3
.
1
5
32
5

<
0
.
0
1

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Be
n
z
y
l
a
l
c
o
h
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
9
3
5

9
.
8
2

1
.
0
9

0

-

0
0
0-
0
01
.
0
9
10
.
5

5
.
0
0
0.
0
5
8
3

1
.
1
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
9
0

0
.
2
8
5

0
.
0
3
1
7

0

-

0
0
0-
0
0

0
.
0
3
1
7
1.
5
0

5
.
0
0
0.
0
0
8
3
3

0
.
0
4
0
0
1

0
.
0
3
6

1
8
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
5
2
7

0
.
5
5
4

0
.
0
6
1
5

0

-

0
0
0-
0
0

0
.
0
6
1
5
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
2
0
0
1.
1
0%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

D
i
b
e
n
z
o
f
u
r
a
n

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
3
1

7
.
5
7

0
.
8
4
1

0

-

0
0
0-
0
00
.
8
4
1
12

5
.
0
0
0.
0
6
6
6

0
.
9
0
8
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
2
9

3
.
4
5

0
.
3
8
3

0

-

0
0
0-
0
00
.
3
8
3
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
4
4
2
0
4.
0
0%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
5
6

6
.
8
9

0
.
7
6
5

0

-

0
0
0-
0
00
.
7
6
5
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
8
2
4
0
7.
5
0%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
6
2
9

0
.
6
6
1

0
.
0
7
3
4

0

-

0
0
0-
0
0

0
.
0
7
3
4
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
3
2
0
1.
2
0%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
8
1

4
.
0
0

0
.
4
4
4

0

-

0
0
0-
0
00
.
4
4
4
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
5
0
3
0
4.
6
0%
Re
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
3
9
1

0
.
4
1
0

0
.
0
4
5
5

0

-

0
0
0-
0
0

0
.
0
4
5
5
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
0
4
10
.
1
9
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
5
5
2

0
.
0
0
0
0
4
4
2

0
.
0
0
0
0
0
4
9
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
0
4
9
0
0.
0
0
0
8
0
0

5
.
0
0
0.
0
0
0
0
0
4
4
4

0
.
0
0
0
0
0
9
3
5
1

<
0
.
0
1

4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
0
1

1
.
0
6

0
.
1
1
7

0

-

0
0
0-
0
00
.
1
1
7
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
7
6
10
.
3
1
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
6
3
4

0
.
6
6
6

0
.
0
7
4
0

0

-

0
0
0-
0
0

0
.
0
7
4
0
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
3
2
10
.
2
4
0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Is
o
p
h
o
r
o
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
8
3

4
.
0
2

0
.
4
4
7

0

-

0
0
0-
0
00
.
4
4
7
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
5
0
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
9
3

7
.
2
7

0
.
8
0
8

0

-

0
0
0-
0
00
.
8
0
8
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
8
6
6
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
9
6

2
.
0
6

0
.
2
2
9

0

-

0
0
0-
0
00
.
2
2
9
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
2
8
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
4
6
6

2
.
3
3

0
.
2
5
9

0

-

0
0
0-
0
00
.
2
5
9
50

5
.
0
0
0.
2
7
8

0
.
5
3
7
17

0
.
0
3
2

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

S
V
O
C
s
0.
0
3
6
(d
e
t
s
)
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
7
9
2

0
.
0
0
0
4
7
5

0
.
0
0
0
0
5
2
8

0

-

0
0
0-
0
0

0
.
0
0
0
0
5
2
8
0.
0
0
0
6
0
0

5
.
0
0
0.
0
0
0
0
0
3
3
3

0
.
0
0
0
0
5
6
1
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
1
9

0
.
0
0
0
2
8
7

0
.
0
0
0
0
3
1
9

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
1
9
0.
0
0
0
9
0
0

5
.
0
0
0.
0
0
0
0
0
5
0
0

0
.
0
0
0
0
3
6
9
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
4
7

0
.
0
0
0
3
4
7

0
.
0
0
0
0
3
8
5

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
8
5
0.
0
0
1
0
0

5
.
0
0
0.
0
0
0
0
0
5
5
5

0
.
0
0
0
0
4
4
1
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
2
6

0
.
0
0
0
2
6
1

0
.
0
0
0
0
2
9
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
9
0
0.
0
0
0
8
0
0

5
.
0
0
0.
0
0
0
0
0
4
4
4

0
.
0
0
0
0
3
3
4
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
5
0

0
.
0
0
0
3
8
5

0
.
0
0
0
0
4
2
7

0

-

0
0
0-
0
0

0
.
0
0
0
0
4
2
7
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
4
6
6
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
7

0
.
0
0
1
1
8

0
.
0
0
0
1
3
1

0

-

0
0
0-
0
0

0
.
0
0
0
1
3
1
0.
0
0
1
1
0

5
.
0
0
0.
0
0
0
0
0
6
1
1

0
.
0
0
0
1
3
7
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
6
3

0
.
0
0
1
5
8

0
.
0
0
0
1
7
5

0

-

0
0
0-
0
0

0
.
0
0
0
1
7
5
0.
0
0
2
8
0

5
.
0
0
0.
0
0
0
0
1
5
5

0
.
0
0
0
1
9
1
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
9
4
5

0
.
0
0
0
8
5
1

0
.
0
0
0
0
9
4
5

0

-

0
0
0-
0
0

0
.
0
0
0
0
9
4
5
0.
0
0
0
9
0
0

5
.
0
0
0.
0
0
0
0
0
5
0
0

0
.
0
0
0
0
9
9
5
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
7
9
8

0
.
0
0
0
2
5
5

0
.
0
0
0
0
2
8
4

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
8
4
0.
0
0
3
2
0

5
.
0
0
0.
0
0
0
0
1
7
8

0
.
0
0
0
0
4
6
1
17

<
0
.
0
1

4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
2
-
D
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
7
4

0
.
0
0
1
4
6

0
.
0
0
0
1
6
2

0

-

0
0
0-
0
0

0
.
0
0
0
1
6
2
0.
0
0
3
9
0

5
.
0
0
0.
0
0
0
0
2
1
7

0
.
0
0
0
1
8
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
7
0
5

0
.
0
0
0
9
8
6

0
.
0
0
0
1
1
0

0

-

0
0
0-
0
0

0
.
0
0
0
1
1
0
0.
0
0
1
4
0

5
.
0
0
0.
0
0
0
0
0
7
7
7

0
.
0
0
0
1
1
7
17

<
0
.
0
1

4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
9
8

0
.
0
0
0
5
5
8

0
.
0
0
0
0
6
2
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
6
2
0
0.
0
0
0
8
0
0

5
.
0
0
0.
0
0
0
0
0
4
4
4

0
.
0
0
0
0
6
6
5
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
6
8

0
.
0
0
0
3
2
8

0
.
0
0
0
0
3
6
4

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
6
4
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
4
0
3
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
2
-
E
t
h
y
l
e
n
e

D
i
b
r
o
m
i
d
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
2
1

0
.
0
0
1
0
9

0
.
0
0
0
1
2
1

0

-

0
0
0-
0
0

0
.
0
0
0
1
2
1
0.
0
0
0
9
0
0

5
.
0
0
0.
0
0
0
0
0
5
0
0

0
.
0
0
0
1
2
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
3
7

0
.
0
0
0
2
6
0

0
.
0
0
0
0
2
8
9

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
8
9
0.
0
0
1
9
0

5
.
0
0
0.
0
0
0
0
1
0
6

0
.
0
0
0
0
3
9
4
17

<
0
.
0
1

4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
3
7

0
.
0
0
0
4
2
4

0
.
0
0
0
0
4
7
1

0

-

0
0
0-
0
0

0
.
0
0
0
0
4
7
1
0.
0
0
3
1
0

5
.
0
0
0.
0
0
0
0
1
7
2

0
.
0
0
0
0
6
4
3
17

<
0
.
0
1

4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

2
-
B
u
t
a
n
o
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
9
8

0
.
0
3
1
4

0
.
0
0
3
4
9

0

-

0
0
0-
0
0

0
.
0
0
3
4
9
0.
0
1
5
9

5
.
0
0
0.
0
0
0
0
8
8
3

0
.
0
0
3
5
8
39

<
0
.
0
1

1
8
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
2-
C
h
l
o
r
o
e
t
h
y
l
V
i
n
y
l
E
t
h
e
r
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
4
7

0
.
0
0
8
7
7

0
.
0
0
0
9
7
4

0

-

0
0
0-
0
0

0
.
0
0
0
9
7
4
0.
0
0
5
9
5

5
.
0
0
0.
0
0
0
0
3
3
0

0
.
0
0
1
0
1
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2-
C
h
l
o
r
o
p
h
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
0
8

4
.
2
8

0
.
4
7
6

0

-

0
0
0-
0
00
.
4
7
6
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
5
3
4
17

0
.
0
3
2

0
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
2-
H
e
x
a
n
o
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
3
7

0
.
0
0
5
2
2

0
.
0
0
0
5
8
0

0

-

0
0
0-
0
0

0
.
0
0
0
5
8
0
0.
0
0
3
8
0

5
.
0
0
0.
0
0
0
0
2
1
1

0
.
0
0
0
6
0
1
39

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
4-
B
r
o
m
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
1
0

4
.
3
1

0
.
4
7
8

0

-

0
0
0-
0
00
.
4
7
8
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
5
3
7
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
4-
C
h
l
o
r
o
p
h
e
n
y
l
p
h
e
n
y
l
e
t
h
e
r
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
9
4
6

0
.
9
9
4

0
.
1
1
0

0

-

0
0
0-
0
00
.
1
1
0
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
6
9
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
4
6

0
.
0
0
6
2
9

0
.
0
0
0
6
9
9

0

-

0
0
0-
0
0

0
.
0
0
0
6
9
9
0.
0
0
4
3
0

5
.
0
0
0.
0
0
0
0
2
3
9

0
.
0
0
0
7
2
3
39

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

A
c
e
t
o
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

2
.
3
6

5
6
.
6

6
.
2
9

0

-

0
0
0-
0
06
.
2
9
24

5
.
0
0
0.
1
3
3

6
.
4
2
39

0
.
1
6

3
2
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

B
e
n
z
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
7

0
.
0
0
4
3
8

0
.
0
0
0
4
8
7

0

-

0
0
0-
0
0

0
.
0
0
0
4
8
7
0.
0
0
4
1
0

5
.
0
0
0.
0
0
0
0
2
2
8

0
.
0
0
0
5
1
0
10

<
0
.
0
1

1
4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Bi
s
(
2
-
c
h
l
o
r
o
e
t
h
o
x
y
)
m
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
4
1

0
.
1
0
4

0
.
0
1
1
6

0

-

0
0
0-
0
0

0
.
0
1
1
6
0.
0
7
4
0

5
.
0
0
0.
0
0
0
4
1
1

0
.
0
1
2
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
bi
s
(
2
-
c
h
l
o
r
o
e
t
h
y
l
)
e
t
h
e
r
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
8
8

7
.
2
2

0
.
8
0
2

0

-

0
0
0-
0
00
.
8
0
2
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
8
6
0
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
bi
s
(
2
-
c
h
l
o
r
o
i
s
o
p
r
o
p
y
l
)
e
t
h
e
r
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
3
3

4
.
5
5

0
.
5
0
5

0

-

0
0
0-
0
00
.
5
0
5
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
5
6
4
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Br
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
8

0
.
0
0
0
7
5
6

0
.
0
0
0
0
8
4
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
8
4
0
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
8
7
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Br
o
m
o
f
o
r
m
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
4
4

0
.
0
0
0
1
7
2

0
.
0
0
0
0
1
9
1

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
9
1
0.
0
0
0
5
0
0

5
.
0
0
0.
0
0
0
0
0
2
7
8

0
.
0
0
0
0
2
1
9
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Br
o
m
o
m
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
4
6

0
.
0
0
2
2
0

0
.
0
0
0
2
4
4

0

-

0
0
0-
0
0

0
.
0
0
0
2
4
4
0.
0
0
1
5
0

5
.
0
0
0.
0
0
0
0
0
8
3
3

0
.
0
0
0
2
5
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
8
4
7

0
.
0
0
0
7
6
2

0
.
0
0
0
0
8
4
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
8
4
6
0.
0
0
0
9
0
0

5
.
0
0
0.
0
0
0
0
0
5
0
0

0
.
0
0
0
0
8
9
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
2
4
5

0
.
0
0
0
1
7
2

0
.
0
0
0
0
1
9
1

0

-

0
0
0-
0
0

0
.
0
0
0
0
1
9
1
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
2
3
0
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Ch
l
o
r
o
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
7
2
6

0
.
0
0
0
7
2
6

0
.
0
0
0
0
8
0
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
8
0
6
0.
0
0
1
0
0

5
.
0
0
0.
0
0
0
0
0
5
5
5

0
.
0
0
0
0
8
6
1
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Ch
l
o
r
o
f
o
r
m
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
7
9

0
.
0
0
0
3
3
5

0
.
0
0
0
0
3
7
2

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
7
2
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
4
1
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
5

0
.
0
0
1
0
5

0
.
0
0
0
1
1
7

0

-

0
0
0-
0
0

0
.
0
0
0
1
1
7
0.
0
0
1
0
0

5
.
0
0
0.
0
0
0
0
0
5
5
5

0
.
0
0
0
1
2
2
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
7

0
.
0
0
0
8
1
9

0
.
0
0
0
0
9
1
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
9
1
0
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
9
4
9
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
1

0
.
0
0
0
6
0
8

0
.
0
0
0
0
6
7
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
6
7
6
0.
0
0
0
6
0
0

5
.
0
0
0.
0
0
0
0
0
3
3
3

0
.
0
0
0
0
7
0
9
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
3
7

0
.
0
0
0
3
0
6

0
.
0
0
0
0
3
4
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
4
0
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
3
7
8
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Di
b
r
o
m
o
m
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
2
7

0
.
0
0
0
6
3
4

0
.
0
0
0
0
7
0
4

0

-

0
0
0-
0
0

0
.
0
0
0
0
7
0
4
0.
0
0
0
5
0
0

5
.
0
0
0.
0
0
0
0
0
2
7
8

0
.
0
0
0
0
7
3
2
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
1
4

0
.
0
0
0
4
5
5

0
.
0
0
0
0
5
0
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
5
0
6
0.
0
0
1
1
0

5
.
0
0
0.
0
0
0
0
0
6
1
1

0
.
0
0
0
0
5
6
7
17

<
0
.
0
1

5
%
Pa
s
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
1
6
Pa
g
e

2
1

o
f

2
2
Ta
b
l
e

1
6
In
i
t
i
a
l

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
d
So
i
l

E
P
C

(m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)
Sc
r
e
e
n
i
n
g

R
i
s
k

Co
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Bu
r
r
o
w
i
n
g

O
w
l
Et
h
y
l
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
9
3

0
.
0
0
0
2
5
1

0
.
0
0
0
0
2
7
9

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
7
9
0.
0
0
1
3
0

5
.
0
0
0.
0
0
0
0
0
7
2
2

0
.
0
0
0
0
3
5
1
10

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
m,
p
-
X
y
l
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
7
4
8

0
.
0
0
1
5
0

0
.
0
0
0
1
6
6

0

-

0
0
0-
0
0

0
.
0
0
0
1
6
6
0.
0
0
2
0
0

5
.
0
0
0.
0
0
0
0
1
1
1

0
.
0
0
0
1
7
7
10

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
8
3
3

0
.
0
0
2
6
6

0
.
0
0
0
2
9
6

0

-

0
0
0-
0
0

0
.
0
0
0
2
9
6
0.
0
0
3
2
0

5
.
0
0
0.
0
0
0
0
1
7
8

0
.
0
0
0
3
1
4
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

o
-
X
y
l
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
7
7
4

0
.
0
0
2
0
9

0
.
0
0
0
2
3
2

0

-

0
0
0-
0
0

0
.
0
0
0
2
3
2
0.
0
0
2
7
0

5
.
0
0
0.
0
0
0
0
1
5
0

0
.
0
0
0
2
4
7
10

<
0
.
0
1

1
4
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Ph
e
n
o
l
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
7
0
9

7
.
4
5

0
.
8
2
7

0

-

0
0
0-
0
00
.
8
2
7
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
8
8
5
NS
V
--
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

S
t
y
r
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
8
2
7

0
.
0
0
2
1
5

0
.
0
0
0
2
3
9

0

-

0
0
0-
0
0

0
.
0
0
0
2
3
9
0.
0
0
2
6
0

5
.
0
0
0.
0
0
0
0
1
4
4

0
.
0
0
0
2
5
3
NS
V
--
14
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
te
r
t
-
B
u
t
y
l
M
e
t
h
y
l
E
t
h
e
r
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
4
4

0
.
0
0
1
0
1

0
.
0
0
0
1
1
2

0

-

0
0
0-
0
0

0
.
0
0
0
1
1
2
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
1
1
6
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
7
0
0

0
.
0
0
0
6
3
0

0
.
0
0
0
0
7
0
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
7
0
0
0.
0
0
0
9
0
0

5
.
0
0
0.
0
0
0
0
0
5
0
0

0
.
0
0
0
0
7
4
9
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l

T
o
l
u
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
8
7
5

0
.
0
1
6
4

0
.
0
0
1
8
2

0

-

0
0
0-
0
0

0
.
0
0
1
8
2
0.
0
1
8
7

5
.
0
0
0.
0
0
0
1
0
4

0
.
0
0
1
9
2
10

<
0
.
0
1

2
3
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
9
8

0
.
0
0
0
4
8
9

0
.
0
0
0
0
5
4
3

0

-

0
0
0-
0
0

0
.
0
0
0
0
5
4
3
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
5
8
2
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
4
6
8

0
.
0
0
0
3
7
4

0
.
0
0
0
0
4
1
6

0

-

0
0
0-
0
0

0
.
0
0
0
0
4
1
6
0.
0
0
0
8
0
0

5
.
0
0
0.
0
0
0
0
0
4
4
4

0
.
0
0
0
0
4
6
0
17

<
0
.
0
1

5
%
Pa
s
s
Bu
r
r
o
w
i
n
g

O
w
l
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
3
9

0
.
0
0
0
2
3
7

0
.
0
0
0
0
2
6
3

0

-

0
0
0-
0
0

0
.
0
0
0
0
2
6
3
0.
0
0
0
7
0
0

5
.
0
0
0.
0
0
0
0
0
3
8
9

0
.
0
0
0
0
3
0
2
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Tr
i
c
h
l
o
r
o
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
1
1

0
.
0
0
0
3
4
2

0
.
0
0
0
0
3
8
0

0

-

0
0
0-
0
0

0
.
0
0
0
0
3
8
0
0.
0
0
1
1
0

5
.
0
0
0.
0
0
0
0
0
6
1
1

0
.
0
0
0
0
4
4
1
NS
V
--
5%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Vi
n
y
l

A
c
e
t
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
5
2

0
.
0
0
1
8
2

0
.
0
0
0
2
0
2

0

-

0
0
0-
0
0

0
.
0
0
0
2
0
2
0.
0
0
1
2
0

5
.
0
0
0.
0
0
0
0
0
6
6
6

0
.
0
0
0
2
0
9
NS
V
--
5%
Un
c
e
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Table 18
Sample Designations for Surface Soil Collected from the TTU at the UTTR
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Sample
Location
Within
TTU? Background Location Description Site # Sample Designation
Sampling
Year
Number of
Analytes
NR-226 NO NO Range land - habitat zone 2002 151
NR-227 NO NO Range land - habitat zone 2002 150
NR-228 YES NO Onsite - hazardous waste site - OB/OD operational area 2002 151
NR-229 YES NO Onsite - range land - habitat zone 2002 151
NR-230 YES NO Onsite - range land - habitat zone 2002 151
NR-231 YES NO Onsite - pad 2 2 OB/OD operational area 2002 151
NR-232 YES NO Onsite - range land - habitat zone 2002 151
NR-233 YES NO Onsite - range land - habitat zone 2002 151
NR-234 YES NO Onsite - range land - habitat zone 2002 151
NR-235 YES NO Onsite - range land - habitat zone 2002 151
NR-236 YES NO Onsite - range land - habitat zone 2002 151
NR-237 YES NO Onsite - range land - habitat zone 2002 151
NR-238 NO YES Background - background 2002 151
NR-239 NO YES Background - background 2002 151
NR-526 YES NO Onsite - range land - habitat zone 2004 151
NR-527 YES NO Onsite - range land - habitat zone 2004 151
NR-528 YES NO Onsite - range land - habitat zone 2004 151
NR-529 YES NO Onsite - range land - habitat zone 2004 151
NR-530 YES NO Onsite - range land - habitat zone 2004 151
NR-531 YES NO Onsite - burn pad 1 OB/OD operational area 2004 151
NR-532 YES NO Onsite - burn pad 1 OB/OD operational area 2004 151
NR-533 YES NO Onsite - main pad 2 OB/OD operational area 2004 151
NR-534 YES NO Onsite - main pad 2 OB/OD operational area 2004 151
NR-535 YES NO Onsite - main pad 2 OB/OD operational area 2004 151
NR-536 NO YES Background - background 2004 25
NR-537 NO YES Background - background 2004 25
SS1 YES NO Onsite - burn pad 1 OB/OD operational area 1991 36
SS2 YES NO Onsite - burn pad 1 OB/OD operational area 1991 36
SS3 YES NO Onsite - burn pad 1 OB/OD operational area 1991 36
SS4 YES NO Onsite - burn pad 1 OB/OD operational area 1991 36
SS5 YES NO Onsite - burn pan 3 OB/OD operational area 1991 36
SS6 YES NO Onsite - burn pan 3 OB/OD operational area 1991 36
SS7 YES NO Onsite - burn pan 3 OB/OD operational area 1991 36
SS8 YES NO Onsite - burn pan 3 OB/OD operational area 1991 36
SS9 YES NO Onsite - burn pan 3 OB/OD operational area 1991 36
SS10 YES NO Onsite - pad 1 2 OB/OD operational area 1991 36
SS11 YES NO Onsite - pad 1 2 OB/OD operational area 1991 36
SS12 YES NO Onsite - pad 2 2 OB/OD operational area 1991 36
SS13 YES NO Onsite - pad 2 2 OB/OD operational area 1991 36
SS14 YES NO Onsite - pad 3 2 OB/OD operational area 1991 36
SS15 YES NO Onsite - pad 3 2 OB/OD operational area 1991 36
SS16 YES NO Onsite - range land -habitat zone 1991 36
SS17 YES NO Onsite - range land -habitat zone 1991 36
SS18 YES NO Onsite - range land -habitat zone 1991 36
SS19 YES NO Onsite - range land -habitat zone 1991 36
SS20 YES NO Onsite - range land -habitat zone 1991 36
TTU-SS01S YES NO Onsite - burn pan 3 OB/OD operational area 1989 84
TTU-SS02S YES NO Onsite - burn pan 3 OB/OD operational area 1989 84
TTU-SS03S YES NO Onsite - burn pan 3 OB/OD operational area 1989 84
TTU-SS04S(D)YES NO Onsite - burn pan 3 OB/OD operational area 1989 84
TTU-SS05S YES NO Onsite - burn pan 3 OB/OD operational area 1989 84
TTU-SS06S(BG)YES NO Onsite - 150-200 yards SE of burn pan - habitat zone 1989 84
Notes:
Eco - Sample collected in ecological habitat
OB/OD - Sample collected in open burn/open detonation area where limited habitat represents an incomplete exposure pathway for eclogical receptors.
Background - Sample collected outside of the UTTR Boundary
Samples NR-226 and NR-227 were not considered background samples due to their proximity to Site 2, Site 3, and an active firing range
Sample TTU-SS04S(D) was included as a site sample as a conservative measure
Sample TTU-SS06S(BG) was considered background when sample collected, but is currently considered a site samples that is located within the TTU boundary near Site 3.
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/18 Page 1 of 1
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5
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5
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5
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5
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5
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4
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D
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0
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3
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6
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5
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6
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5
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m
g
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2
1

2
1
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%
53
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7
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3
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0
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D
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e

N
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c

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15
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0

U
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m
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1
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1
6
88
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7
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3
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3
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8
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6
6

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4
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8
0

M
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x

D
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t
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s
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c

m
g
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1
6

2
1
76
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9
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4
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3

7
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3
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7
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9
4

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4
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4
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c

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14
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4

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5
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5

2
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5
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c

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25
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0

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y
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m
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6

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3
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7
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6
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6
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5

U
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d
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m
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1
3

2
1
62
%
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1
2
0

1
.
0
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0
.
3
4
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3
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6
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6
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m

m
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2
0

2
0
10
0
%
15
4
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1
5
6
0
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0
0

2
3
1
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0

4
2
9
0
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-
-

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t

a

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d
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0
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5
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l
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m
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1
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80
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4

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1
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6
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6
8
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-
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t

a

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l

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12
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1
5

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6
94
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6
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4
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6
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9
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9

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3
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1

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l

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0
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4
1

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L
Co
p
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m
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2
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2
1
95
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14
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1

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4
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1

9
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4
0

6
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1
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1

1
2

2
3
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6
0

D
a
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o
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l

(
0
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)
23
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6

U
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Ir
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n

m
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2
0

2
0
10
0
%
54
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0

1
4
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2
4
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3
1
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0
0

D
a
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e

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0
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13
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.
0

U
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Le
a
d

m
g
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2
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2
1
95
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16
.
1

1
6
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1

4
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5
0

3
6

1
6
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2

9
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3
1

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9
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0
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D
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l

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0
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19
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0

U
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s
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m
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2
0

2
0
10
0
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11
5
0
0

2
4
3
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1
8
3
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3
9
9
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2
2
7
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0
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D
a
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0
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22
7
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0

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n
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m
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1

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0
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3
7
6

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4
7
7
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0
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D
a
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0
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47
7
.
0

U
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Me
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m
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7

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1
33
%
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0
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1
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6
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0
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8
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2
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4

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U
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m
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1
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1
5
87
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3
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3
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6
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3
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8
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0
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9

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4
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12
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5
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0
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8

7
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6
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r
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5

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7

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s
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m
g
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5

5
10
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82
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9
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8
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4

3
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5

1
3
2
0

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a
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c

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89
0

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a
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t
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t
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s
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m
g
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2
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2
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0
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20
9
0

6
8
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4
5
8
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1
1
9
0

-
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-

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N
o
t

a

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l
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m

m
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.
7
7

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8
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5
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3
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7

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18
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m
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2
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2
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29
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7

6
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4
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7

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9
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6
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8
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c

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60
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5
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m
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5
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m
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6
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6
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5
*
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m
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0

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6
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6
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5
*
M
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Be
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(
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e

m
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0

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6
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6
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0
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7

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1
8
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5
*
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(
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e

m
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6
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0
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3
6
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5
*
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(
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)
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m
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0

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1
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3
6
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0
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0
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7

-
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5
*
M
a
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Be
n
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o
(
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,
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,
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)
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m
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6
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3
6
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0
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0
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0

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0
.
1
8
0
0.
5
*
M
a
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Be
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(
k
)
f
l
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m
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0

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6
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0
9
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3
6
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7

0
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0
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5
*
M
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r
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e

m
g
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6
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0.
0
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3
6
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0
6
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0
.
0
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5
1

-
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-
-

0
.
1
8
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5
*
M
a
x
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Di
b
e
n
z
o
(
a
,
h
)
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m
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0

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6
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0
7
6
5

0
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3
6
0

0
.
0
6
5
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0
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6

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0
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1
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5
*
M
a
x
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Fl
u
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r
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e

m
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1

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6
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3
6
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0
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1
4
4

0
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1
4
4

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0
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0
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0
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0
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1
0
7

D
a
t
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e

N
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c

(
0
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0
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)
0.
1
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7

U
C
L
Fl
u
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e

m
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g

0

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6
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0.
0
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6
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3
6
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4

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0
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5
*
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In
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o
(
1
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2
,
3
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d
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e

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0

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0
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6
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5
*
M
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l
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e

m
g
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K
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0

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6
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0
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3
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0
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0
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0
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5
*
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a
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n
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e

m
g
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0

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6
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5
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6
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7

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5
*
M
a
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e

m
g
/
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g

0

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6
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0
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3
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5
*
M
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m
g
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1

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0
%
20

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-
20
.
0

M
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e
t
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4
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0
7
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8
0

0
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5
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4
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3
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5
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6
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5
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5
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5
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7
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5
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5
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5
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5
*
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a
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s
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4
Table 20
Refined Chemical Biotransfer Factors for Inorganics and Selected Organics
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte
Refined Plant
BTF
Source for Plant
BTFs
Refined Terrestrial
Invertebrates BTF
Source for
Terrestrial
Invertebrate BTFs
Refinded Small
Mammal BTF
Source for
Mammal BTFs
Aluminum 0.00287 A 0.043 C 0.073 E
Antimony 0.0102 A 0.0162 D 1.0 F
Arsenic
Barium 0.10 B 0.09 C 0.057 E
Beryllium 0.010 B 0.045 C 0.41 E
Cadmium
Chromium 0.040 B 0.306 C 0.085 G
Cobalt 0.00745 A 0.122 C
Copper
Iron 0.00425 A 0.04 C
Lead
Magnesium 0.810 A 0.169 C 0.993 E
Manganese 0.0792 A 0.079 E
Mercury 0.054 E
Molybdenum 0.400 B 0.953 C 1.0 F
Nickel 1.059 C 0.249 G
Selenium
Silver 0.014 A 2.045 C 0.81 E
Strontium 1.1 B 0.087 C 1.0 F
Thallium 0.0040 B 0.0606 D 0.1124 E
Vanadium 0.00485 A 0.088 C 0.019 E
Zinc
2,4,6-Trinitrotoluene (TNT)1.710 H 0.058 H 0.000 I
2,4-Dinitrotoluene 0.376 H 3.710 H 1.050 J
2,6-Dinitrotoluene 3.140 H 3.160 H 1.100 J
HMX 0.313 H 2.130 J
Notes:
BTF = biotransfer factor
A Median soil-to-plant transfer factors for inorganics are from soil-to-dry plant uptake factors presented by ORNL (2000)
B Bechtel Jacobs, 1998 - median uptake factors
C Sample et al., 1998a - median soil-to-earthworm uptake factors
D Median uptake factors from ARAMS (Army Risk Assessment Modeling System; US Army, 2004)
Naphthalene data substituted for 2-methylnaphthalene.
E Sample et al., 1998b - median soil-to-mammal uptake factors
F Bioaccumulation data were not available. A default value of 1 was assumed.
G Sample et al, 1998 - Soil to small mammal bioaccumulation regression model presented in Table 9
H Median BAFs caclulated for the Army Risk Assessment Modelling System (2005)
I USEPA 2005
J USEPA 2000
regrsssion based
regrsssion based
regression based
regression based regression based regression based
regression based
regression based regression based regression based
regression based regression based
regrsssion based
regrsssion based regrsssion based regrsssion based
BTFs for COPECs not listed in this table are the same as those used in the screening analysis (Table 8)
regrsssion based regrsssion based
regrsssion based regrsssion based regrsssion based
regrsssion based regrsssion based regrsssion based
regression based
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/20 Page 1 of 1
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m

2
8

2
8

1
0
0
%

9
.
9

2
5
.
7

1
6
.
7

3
.
4
2

5
4

5
4

1
0
0
%

8
.
2
8

3
5
.
5

2
0
.
8

4
.
8
9

B
S

<
0
.
0
0
0
1
Zi
n
c

4
8

4
8

1
0
0
%

2
9
.
7

2
3
0
0

1
2
5

3
3
6

5
4

5
4

1
0
0
%

6
.
3
7

7
8

3
8
.
3

1
3
.
4

S
S
<0
.
0
0
0
1
No
t
e
s
:
1 S
u
m
m
a
r
y

s
t
a
t
i
s
t
i
c
s

i
n
c
l
u
d
e

1
/
2

d
e
t
e
c
t
i
o
n

l
i
m
i
t

a
s

a

p
r
o
x
y

v
a
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e

f
o
r

n
o
n
-
d
e
t
e
c
t
s
.
DF

=

d
e
t
e
c
t
i
o
n

f
r
e
q
u
e
n
c
y
Bo
l
d

a
n
d

h
i
g
h
l
i
g
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t
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d

t
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x
t

a
r
e

t
h
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C
O
P
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C
s

w
i
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h

s
i
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n
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f
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a
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l
y

g
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s
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c
o
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n
t
r
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s

c
o
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p
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d

t
o

b
a
c
k
g
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d
.

T
h
e
s
e

C
O
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C
s

we
r
e

r
e
t
a
i
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e
d

f
o
r

f
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r

c
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r
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i
n

t
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r
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f
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d

s
c
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e
n
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v
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l
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t
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n
.

BS

=

s
i
g
n
i
f
i
c
a
n
t

d
i
f
f
e
r
e
n
c
e

b
e
t
w
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n

b
a
c
k
g
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u
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d

a
n
d

s
i
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e

d
a
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a

w
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b
a
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k
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d

c
o
n
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n
t
r
a
t
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n
s

b
e
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g

g
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e
a
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r
NS

=

n
o

s
i
g
n
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f
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c
a
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t

d
i
f
f
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b
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b
a
c
k
g
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d

a
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d

s
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a
SS

=

s
i
g
n
i
f
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c
a
n
t

d
i
f
f
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r
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n
c
e

b
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t
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n

b
a
c
k
g
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u
n
d

a
n
d

s
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e

d
a
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a

w
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s
i
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e

c
o
n
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n
t
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b
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g
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p
-

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f

s
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e

(
0
.
0
5
)

b
a
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e
d

o
n

t
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e

t
w
o

t
a
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t
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d
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Ba
c
k
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d

S
o
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l

S
t
a
t
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s
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s
Si
t
e

S
a
m
p
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e

S
o
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l

S
t
a
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c
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
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0
S
L
C
/
H
i
l
l
A
F
B
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6
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t
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A
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n
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f

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Ta
b
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e

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2
Su
m
m
a
r
y

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f

t
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e

R
e
f
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d

S
c
r
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e
n
i
n
g

E
v
a
l
u
a
t
i
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n

f
o
r

P
l
a
n
t
s
At
t
a
c
h
m
e
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t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l

t
e
Cl
a
s
s
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

n

U
n
c
e
r
t
a
i
n

N
o

R
i
s
k

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

2
8

0

2
4
13
0
0
0
%
N
o
n
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

e
n
e
r
g
e
t
i
c

0
%

4
8

0

4
5
30
0
0
0
%
N
o
n
e
2-
N
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

2
8

0

2
4
40
0
0
0
%
N
o
n
e
4-
N
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

2
8

0

2
4
13
0
0
0
%
N
o
n
e
Ni
t
r
o
b
e
n
z
e
n
e

e
n
e
r
g
e
t
i
c

0
%

4
8

0

4
5
30
0
0
0
%
N
o
n
e
An
t
i
m
o
n
y

i
n
o
r
g
a
n
i
c

7
9
%

2
8

0

8

6

0

1
1

3

1
1
%

P
o
s
s
i
b
l
e
Cadmium

i
n
o
r
g
a
n
i
c
4
4
%
4
8
0
4
7
0
0
1
0
0
%
N
o
n
e
Co
p
p
e
r

i
n
o
r
g
a
n
i
c

8
5
%

4
8

0

7

4

0

3
3

4

8
%

P
o
s
s
i
b
l
e
Le
a
d

i
n
o
r
g
a
n
i
c

8
3
%

4
8

0

4
3
01
1
3
6
%
N
o
n
e
Mo
l
y
b
d
e
n
u
m

i
n
o
r
g
a
n
i
c

9
1
%

2
2

0

2

0

0

1
8

2

9
%

P
o
s
s
i
b
l
e
Perchlorate

i
n
o
r
g
a
n
i
c
5
0
%
2
2
0
2
2
0
0
0
0
0
%
N
o
n
e
Se
l
e
n
i
u
m

i
n
o
r
g
a
n
i
c

0
%

4
8

0

1

1
6

3
1

0

0

0
%

U
n
c
e
r
t
a
i
n

P
r
o
b

r
i
s
k

b
y

N
D
Si
l
v
e
r

i
n
o
r
g
a
n
i
c

8
%

4
8

0

2
1

2
5

0

1

1

2
%

U
n
c
e
r
t
a
i
n

P
o
s
s

r
i
s
k

b
y

N
D
Zi
n
c

i
n
o
r
g
a
n
i
c

1
0
0
%

4
8

0

0

0

0

1
6

3
2
67
%
Pr
o
b
a
b
l
e
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

P
A
H

1
4
%

2
8

0

2
4
00
0
4
1
4
%
N
o
n
e
Ac
e
n
a
p
h
t
h
y
l
e
n
e

P
A
H

0
%

2
8

0

2
4
04
0
0
0
%
N
o
n
e
Anthracene

P
A
H
7
%
2
8
0
2
4
0
2
0
2
7
%
N
o
n
e
Benzo(a)anthrace
n
e

P
A
H
0
%
2
8
0
2
4
0
4
0
0
0
%
N
o
n
e
Benzo(a)pyrene

P
A
H
0
%
2
8
0
2
4
0
4
0
0
0
%
N
o
n
e
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e

P
A
H

0
%

2
8

0

2
4
04
0
0
0
%
N
o
n
e
Benzo(g,h,i)peryle
n
e

P
A
H
0
%
2
8
0
2
4
0
4
0
0
0
%
N
o
n
e
Benzo(k)fluoranth
e
n
e
P
A
H
0
%
2
8
0
2
4
0
4
0
0
0
%
N
o
n
e
Chrysene

P
A
H
0
%
2
8
0
2
4
0
4
0
0
0
%
N
o
n
e
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e

P
A
H

0
%

2
8

0

2
4
04
0
0
0
%
N
o
n
e
Fl
u
o
r
a
n
t
h
e
n
e

P
A
H

4
%

2
8

0

2
4
04
0
0
0
%
N
o
n
e
Fluorene

P
A
H
1
4
%
2
8
0
2
4
0
0
1
3
1
1
%
N
o
n
e
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e

P
A
H

0
%

2
8

0

2
4
04
0
0
0
%
N
o
n
e
Naphthalene

P
A
H
2
5
%
2
8
0
2
3
0
0
1
4
1
4
%
N
o
n
e
Phenanthrene

P
A
H
1
8
%
2
8
0
2
4
0
0
0
4
1
4
%
N
o
n
e
Pyrene

P
A
H
0
%
2
8
0
2
4
0
4
0
0
0
%
N
o
n
e
TP
H

p
e
t
r
o
l
e
u
m

1
0
0
%

6

0

3
00
0
3
50
%
Pr
o
b
a
b
l
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

2
8

0

2
4
13
0
0
0
%
N
o
n
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

2
8

0

2
4
40
0
0
0
%
N
o
n
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

2
8

0

2
4
40
0
0
0
%
N
o
n
e
4-
C
h
l
o
r
o
a
n
i
l
i
n
e

S
V
O
C

0
%

2
8

0

2
4
40
0
0
0
%
N
o
n
e
Butyl b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
S
V
O
C
0
%
2
8
0
2
5
3
0
0
0
0
%
N
o
n
e
Diethylphthalate

S
V
O
C
0
%
2
8
0
2
5
3
0
0
0
0
%
N
o
n
e
Dimethylphthalate

S
V
O
C
0
%
2
8
0
2
5
3
0
0
0
0
%
N
o
n
e
Co
m
m
e
n
t
s
ND

-

E
x
c
e
e
d
a
n
c
e
s

D
e
t
e
c
t
e
d

-

E
x
c
e
e
d
a
n
c
e
s
Re
f
i
n
e
d

R
i
s
k

Co
n
c
l
u
s
i
o
n
LO
E
C

Ex
c
e
e
d
a
n
c
e

Fr
e
q
u
e
n
c
y
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
il
l
A
F
B
_
T
T
U
_0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
2
Pa
g
e

1

o
f

2
Ta
b
l
e

2
2
Su
m
m
a
r
y

o
f

t
h
e

R
e
f
i
n
e
d

S
c
r
e
e
n
i
n
g

E
v
a
l
u
a
t
i
o
n

f
o
r

P
l
a
n
t
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l

t
e
Cl
a
s
s
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

n

U
n
c
e
r
t
a
i
n

N
o

R
i
s
k

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e
Co
m
m
e
n
t
s
ND

-

E
x
c
e
e
d
a
n
c
e
s

D
e
t
e
c
t
e
d

-

E
x
c
e
e
d
a
n
c
e
s
Re
f
i
n
e
d

R
i
s
k

Co
n
c
l
u
s
i
o
n
LO
E
C

Ex
c
e
e
d
a
n
c
e

Fr
e
q
u
e
n
c
y
Di-n-octylphthalate

S
V
O
C
0
%
2
8
0
2
5
3
0
0
0
0
%
N
o
n
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e

S
V
O
C

0
%

2
8

0

2
4
13
0
0
0
%
N
o
n
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e

S
V
O
C

0
%

2
8

0

2
4
13
0
0
0
%
N
o
n
e
Pentachloropheno
l

S
V
O
C
0
%
2
8
0
2
4
4
0
0
0
0
%
N
o
n
e
2-Chlorophenol

V
O
C
0
%
2
8
0
2
4
1
3
0
0
0
%
N
o
n
e
Ph
e
n
o
l

V
O
C

0
%

2
8

0

2
5
30
0
0
0
%
N
o
n
e
No
t
e
s
:
Un
c
e
r
t
a
i
n
t
i
e
s

a
r
e

n
o
t

s
h
o
w
n

i
n

t
h
i
s

t
a
b
l
e
ND

-

n
o
t

d
e
t
e
c
t
e
d
NO
E
C

-

n
o

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
LO
E
C

-

l
o
w
e
s
t

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
Un
c
e
r
t
a
i
n

-

r
e
t
a
i
n
e
d

a
s

a
n

u
n
c
e
r
t
a
i
n
t
y
No
n
e

-

e
x
p
o
s
u
r
e

c
o
n
c
e
n
t
r
a
t
i
o
n

d
o
e
s

n
o
t

e
x
c
e
e
d

t
h
e

e
i
t
h
e
r

t
o
x
i
c
i
t
y

v
a
l
u
e
Po
s
s
i
b
l
e

-

E
x
p
o
s
u
r
e

e
x
c
e
e
d
s

t
h
e

N
O
E
C

v
a
l
u
e

b
u
t

n
o
t

t
h
e

L
O
E
C

v
a
l
u
e
Pr
o
b
a
b
l
e

-

E
x
p
o
s
u
r
e

e
x
c
e
e
d
s

t
h
e

L
O
E
C

v
a
l
u
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
il
l
A
F
B
_
T
T
U
_0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
2
Pa
g
e

2

o
f

2
Ta
b
l
e

2
3
Su
m
m
a
r
y

o
f

t
h
e

R
e
f
i
n
e
d

S
c
r
e
e
n
i
n
g

E
v
a
l
u
a
t
i
o
n

f
o
r

P
l
a
n
t
s

w
i
t
h
i
n

E
c
o
l
o
g
i
c
a
l

H
a
b
i
t
a
t
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e
Cl
a
s
s
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c
y

n
Un
c
e
r
t
a
i
n

N
o

R
i
s
k

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

e
n
e
r
g
e
t
i
c

0
%

2
1

0

2
1

0

0

0

0

0
%

N
o
n
e
2-
N
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
4-
N
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Ni
t
r
o
b
e
n
z
e
n
e

e
n
e
r
g
e
t
i
c

0
%

2
1

0

2
1

0

0

0

0

0
%

N
o
n
e
An
t
i
m
o
n
y

i
n
o
r
g
a
n
i
c

8
8
%

1
6

0

5

2

0

9

0

0
%

P
o
s
s
i
b
l
e
Ca
d
m
i
u
m

i
n
o
r
g
a
n
i
c

6
2
%

2
1

0

2
1

0

0

0

0

0
%

N
o
n
e
Co
p
p
e
r

i
n
o
r
g
a
n
i
c

9
5
%

2
1

0

3

0

0

1
8

0

0
%

P
o
s
s
i
b
l
e
Le
a
d

i
n
o
r
g
a
n
i
c

9
5
%

2
1

0

2
1

0

0

0

0

0
%

N
o
n
e
Mo
l
y
b
d
e
n
u
m

i
n
o
r
g
a
n
i
c

8
7
%

1
5

0

2

0

0

1
3

0

0
%

P
o
s
s
i
b
l
e
Pe
r
c
h
l
o
r
a
t
e

i
n
o
r
g
a
n
i
c

3
3
%

1
5

0

1
5

0

0

0

0

0
%

N
o
n
e
Se
l
e
n
i
u
m

i
n
o
r
g
a
n
i
c

0
%

2
1

0

0

7

1
4

0

0

0
%

U
n
c
e
r
t
a
i
n

P
r
o
b

r
i
s
k

b
y

N
D
Si
l
v
e
r

i
n
o
r
g
a
n
i
c

5
%

2
1

0

1
5

6

0

0

0

0
%

N
o
n
e

P
o
s
s

r
i
s
k

b
y

N
D
Zi
n
c

i
n
o
r
g
a
n
i
c

1
0
0
%

2
1

0

0

0

0

9

1
2
57
%
Pr
o
b
a
b
l
e
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Ac
e
n
a
p
h
t
h
y
l
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
An
t
h
r
a
c
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Be
n
z
o
(
a
)
p
y
r
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Ch
r
y
s
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Fl
u
o
r
a
n
t
h
e
n
e

P
A
H

6
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Fl
u
o
r
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Na
p
h
t
h
a
l
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Ph
e
n
a
n
t
h
r
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Py
r
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
TP
H

p
e
t
r
o
l
e
u
m

1
0
0
%

1

0

1

0

0

0

0

0
%

N
o
n
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
4-
C
h
l
o
r
o
a
n
i
l
i
n
e

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Co
m
m
e
n
t
s
ND

-

E
x
c
e
e
d
a
n
c
e
s

D
e
t
e
c
t
e
d

-

E
x
c
e
e
d
a
n
c
e
s
LO
E
C

Ex
c
e
e
d
a
n
c
e

Fr
e
q
u
e
n
c
y
Re
f
i
n
e
d

R
i
s
k

Co
n
c
l
u
s
i
o
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
3
Pa
g
e

1

o
f

2
Ta
b
l
e

2
3
Su
m
m
a
r
y

o
f

t
h
e

R
e
f
i
n
e
d

S
c
r
e
e
n
i
n
g

E
v
a
l
u
a
t
i
o
n

f
o
r

P
l
a
n
t
s

w
i
t
h
i
n

E
c
o
l
o
g
i
c
a
l

H
a
b
i
t
a
t
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
An
a
l
y
t
e
Cl
a
s
s
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c
y

n
Un
c
e
r
t
a
i
n

N
o

R
i
s
k

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e
Co
m
m
e
n
t
s
ND

-

E
x
c
e
e
d
a
n
c
e
s

D
e
t
e
c
t
e
d

-

E
x
c
e
e
d
a
n
c
e
s
LO
E
C

Ex
c
e
e
d
a
n
c
e

Fr
e
q
u
e
n
c
y
Re
f
i
n
e
d

R
i
s
k

Co
n
c
l
u
s
i
o
n
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
2-
C
h
l
o
r
o
p
h
e
n
o
l

V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Ph
e
n
o
l

V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
No
t
e
s
:
Un
c
e
r
t
a
i
n
t
i
e
s

a
r
e

n
o
t

s
h
o
w
n

i
n

t
h
i
s

t
a
b
l
e
ND

-

n
o
t

d
e
t
e
c
t
e
d
NO
E
C

-

n
o

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
LO
E
C

-

l
o
w
e
s
t

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
Un
c
e
r
t
a
i
n

-

r
e
t
a
i
n
e
d

a
s

a
n

u
n
c
e
r
t
a
i
n
t
y
No
n
e

-

e
x
p
o
s
u
r
e

c
o
n
c
e
n
t
r
a
t
i
o
n

d
o
e
s

n
o
t

e
x
c
e
e
d

t
h
e

e
i
t
h
e
r

t
o
x
i
c
i
t
y

v
a
l
u
e
Po
s
s
i
b
l
e

-

E
x
p
o
s
u
r
e

e
x
c
e
e
d
s

t
h
e

N
O
E
C

v
a
l
u
e

b
u
t

n
o
t

t
h
e

L
O
E
C

v
a
l
u
e
Pr
o
b
a
b
l
e

-

E
x
p
o
s
u
r
e

e
x
c
e
e
d
s

t
h
e

L
O
E
C

v
a
l
u
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
3
Pa
g
e

2

o
f

2
Ta
b
l
e

2
4
Su
m
m
a
r
y

o
f

t
h
e

R
e
f
i
n
e
d

S
c
r
e
e
n
i
n
g

E
v
a
l
u
a
t
i
o
n

f
o
r

S
o
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Aa
n
a
l
y
t
e

C
l
a
s
s
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c
y

n
Un
c
e
r
t
a
i
n

N
o
n
e

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e
2,
4
-
D
i
n
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

2
8

0

2
2

2

4

0

0

0
%

N
o
n
e
2,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

e
n
e
r
g
e
t
i
c

2
%

4
8

0

4
8

0

0

0

0

0
%

N
o
n
e
2-
N
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

2
8

0

2
4

1

3

0

0

0
%

N
o
n
e
4-
N
i
t
r
o
p
h
e
n
o
l

e
n
e
r
g
e
t
i
c

0
%

2
8

0

2
2

2

4

0

0

0
%

N
o
n
e
HM
X

e
n
e
r
g
e
t
i
c

3
1
%

4
2

0

3
5

0

0

6

1

2
%

N
o
n
e
Ni
t
r
o
b
e
n
z
e
n
e

e
n
e
r
g
e
t
i
c

0
%

4
8

0

4
5

3

0

0

0

0
%

N
o
n
e
An
t
i
m
o
n
y

i
n
o
r
g
a
n
i
c

7
9
%

2
8

0

2
7

0

0

1

0

0
%

N
o
n
e
Ca
d
m
i
u
m

i
n
o
r
g
a
n
i
c

4
4
%

4
8

0

4
8

0

0

0

0

0
%

N
o
n
e
Co
p
p
e
r

i
n
o
r
g
a
n
i
c

8
5
%

4
8

0

1

6

0

3
2

9

1
9
%

P
o
s
s
i
b
l
e
Le
a
d

i
n
o
r
g
a
n
i
c

8
3
%

4
8

0

4
7

0

0

0

1

2
%

N
o
n
e
Pe
r
c
h
l
o
r
a
t
e

i
n
o
r
g
a
n
i
c

5
0
%

2
2

0

2
1

0

0

1

0

0
%

N
o
n
e
Zi
n
c

i
n
o
r
g
a
n
i
c

1
0
0
%

4
8

0

0

0

0

4
4

4

8
%

P
o
s
s
i
b
l
e
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

P
A
H

1
4
%

2
8

0

2
4

0

0

1

3

1
1
%

N
o
n
e
Ac
e
n
a
p
h
t
h
y
l
e
n
e

P
A
H

0
%

2
8

0

2
4

4

0

0

0

0
%

N
o
n
e
An
t
h
r
a
c
e
n
e

P
A
H

7
%

2
8

0

2
4

1

1

2

0

0
%

N
o
n
e
Fl
u
o
r
a
n
t
h
e
n
e

P
A
H

4
%

2
8

0

2
5

0

3

0

0

0
%

N
o
n
e
Fl
u
o
r
e
n
e

P
A
H

1
4
%

2
8

0

2
4

0

0

1

3

1
1
%

N
o
n
e
Na
p
h
t
h
a
l
e
n
e

P
A
H

2
5
%

2
8

0

2
4

0

0

1

3

1
1
%

N
o
n
e
Ph
e
n
a
n
t
h
r
e
n
e

P
A
H

1
8
%

2
8

0

2
4

0

0

0

4

1
4
%

N
o
n
e
Py
r
e
n
e

P
A
H

0
%

2
8

0

2
4

0

4

0

0

0
%

N
o
n
e
TP
H

p
e
t
r
o
l
e
u
m

1
0
0
%

6

0

2

0

0

0

4
67
%
Pr
o
b
a
b
l
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

2
8

0

2
3

1

4

0

0

0
%

N
o
n
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

2
8

0

2
4

1

3

0

0

0
%

N
o
n
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

2
8

0

2
4

1

3

0

0

0
%

N
o
n
e
4-
C
h
l
o
r
o
a
n
i
l
i
n
e

S
V
O
C

0
%

2
8

0

2
4

4

0

0

0

0
%

N
o
n
e
bi
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

S
V
O
C

1
8
%

2
8

2
8

0

0

0

0

0

0
%

N
o
n
e
Di
b
e
n
z
o
f
u
r
a
n

S
V
O
C

1
4
%

2
8

0

2
5

0

0

0

3

1
1
%

N
o
n
e
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
op
y
l
a
m
i
n
e

S
V
O
C

0
%

2
8

0

2
4

4

0

0

0

0
%

N
o
n
e
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e

S
V
O
C

0
%

2
8

0

2
4

4

0

0

0

0
%

N
o
n
e
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

2
8

0

2
5

3

0

0

0

0
%

N
o
n
e
2-
C
h
l
o
r
o
p
h
e
n
o
l

V
O
C

0
%

2
8

0

2
4

1

3

0

0

0
%

N
o
n
e
Ph
e
n
o
l

V
O
C

0
%

2
8

0

2
4

4

0

0

0

0
%

N
o
n
e
No
t
e
s
:
ND

-

n
o
t

d
e
t
e
c
t
e
d
NO
E
C

-

n
o

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
LO
E
C

-

l
o
w
e
s
t

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
Un
c
e
r
t
a
i
n

-

r
e
t
a
i
n
e
d

a
s

a
n

u
n
c
e
r
t
a
i
n
t
y
No
n
e

-

e
x
p
o
s
u
r
e

c
o
n
c
e
n
t
r
a
t
i
o
n

d
o
e
s

n
o
t

e
x
c
e
e
d

t
h
e

e
i
t
h
e
r

t
o
x
i
c
i
t
y

v
a
l
u
e
Po
s
s
i
b
l
e

-

E
x
p
o
s
u
r
e

e
x
c
e
e
d
s

t
h
e

N
O
E
C

v
a
l
u
e

b
u
t

n
o
t

t
h
e

L
O
E
C

v
a
l
u
e
Pr
o
b
a
b
l
e

-

E
x
p
o
s
u
r
e

e
x
c
e
e
d
s

t
h
e

L
O
E
C

v
a
l
u
e
Co
m
m
e
n
t
s
ND

-

E
x
c
e
e
d
a
n
c
e
s

D
e
t
e
c
t
e
d

-

E
x
c
e
e
d
a
n
c
e
s
LO
E
C

Ex
c
e
e
d
a
n
c
e

Fr
e
q
u
e
n
c
y
Re
f
i
n
e
d

R
i
s
k

Co
n
c
l
u
s
i
o
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
4
Pa
g
e

1

o
f

1
Ta
b
l
e

2
5
Su
m
m
a
r
y

o
f

t
h
e

R
e
f
i
n
e
d

S
c
r
e
e
n
i
n
g

E
v
a
l
u
a
t
i
o
n

f
o
r
S
o
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s

w
i
t
h
i
n

E
c
o
l
o
g
i
c
a
l

H
a
b
i
t
a
t
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Aa
n
a
l
y
t
e

C
l
a
s
s
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c
y

n
Un
c
e
r
t
a
i
n

N
o
n
e

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e

P
o
s
s
i
b
l
e

P
r
o
b
a
b
l
e
2,4-Dinitrophenol
e
n
e
r
g
e
t
i
c
0
%
1
6
0
1
5
1
0
0
0
0
%
N
o
n
e
2,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

e
n
e
r
g
e
t
i
c

0
%

2
1

0

2
1
00
0
0
0
%
N
o
n
e
2-Nitrophenol

e
n
e
r
g
e
t
i
c
0
%
1
6
0
1
6
0
0
0
0
0
%
N
o
n
e
4-Nitrophenol

e
n
e
r
g
e
t
i
c
0
%
1
6
0
1
5
1
0
0
0
0
%
N
o
n
e
HM
X

e
n
e
r
g
e
t
i
c

2
0
%

2
0

0

1
8
00
2
0
0
%
N
o
n
e
Nitrobenzene

e
n
e
r
g
e
t
i
c
0
%
2
1
0
2
1
0
0
0
0
0
%
N
o
n
e
An
t
i
m
o
n
y

i
n
o
r
g
a
n
i
c

8
8
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
Ca
d
m
i
u
m

i
n
o
r
g
a
n
i
c

6
2
%

2
1

0

2
1
00
0
0
0
%
N
o
n
e
Co
p
p
e
r

i
n
o
r
g
a
n
i
c

9
5
%

2
1

0

0

1

0

1
9

1

5
%

P
o
s
s
i
b
l
e
Le
a
d

i
n
o
r
g
a
n
i
c

9
5
%

2
1

0

2
1
00
0
0
0
%
N
o
n
e
Pe
r
c
h
l
o
r
a
t
e

i
n
o
r
g
a
n
i
c

3
3
%

1
5

0

1
5
00
0
0
0
%
N
o
n
e
Zi
n
c

i
n
o
r
g
a
n
i
c

1
0
0
%

2
1

0

0

0

0

2
1

0

0
%

P
o
s
s
i
b
l
e
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

P
A
H

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
Ac
e
n
a
p
h
t
h
y
l
e
n
e

P
A
H

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
An
t
h
r
a
c
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
Fluoranthene

P
A
H
6
%
1
6
0
1
6
0
0
0
0
0
%
N
o
n
e
Fluorene

P
A
H
0
%
1
6
0
1
6
0
0
0
0
0
%
N
o
n
e
Na
p
h
t
h
a
l
e
n
e

P
A
H

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
Phenanthrene

P
A
H
0
%
1
6
0
1
6
0
0
0
0
0
%
N
o
n
e
Py
r
e
n
e

P
A
H

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
TP
H

p
e
t
r
o
l
e
u
m

1
0
0
%

1

0

1
00
0
0
0
%
N
o
n
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

1
6

0

1
5
10
0
0
0
%
N
o
n
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
4-
C
h
l
o
r
o
a
n
i
l
i
n
e

S
V
O
C

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
bi
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

S
V
O
C

0
%

1
6

1
6

0

0

0

0

0

0
%

N
o
n
e
Dibenzofuran

S
V
O
C
0
%
1
6
0
1
6
0
0
0
0
0
%
N
o
n
e
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e

S
V
O
C

0
%

1
6

0

1
6

0

0

0

0

0
%

N
o
n
e
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e

S
V
O
C

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

S
V
O
C

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
2-
C
h
l
o
r
o
p
h
e
n
o
l

V
O
C

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
Ph
e
n
o
l

V
O
C

0
%

1
6

0

1
6
00
0
0
0
%
N
o
n
e
No
t
e
s
:
ND

-

n
o
t

d
e
t
e
c
t
e
d
NO
E
C

-

n
o

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
LO
E
C

-

l
o
w
e
s
t

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
Un
c
e
r
t
a
i
n

-

r
e
t
a
i
n
e
d

a
s

a
n

u
n
c
e
r
t
a
i
n
t
y
No
n
e

-

e
x
p
o
s
u
r
e

c
o
n
c
e
n
t
r
a
t
i
o
n

d
o
e
s

n
o
t

e
x
c
e
e
d

t
h
e

e
i
t
h
e
r

t
o
x
i
c
i
t
y

v
a
l
u
e
Po
s
s
i
b
l
e

-

E
x
p
o
s
u
r
e

e
x
c
e
e
d
s

t
h
e

N
O
E
C

v
a
l
u
e

b
u
t

n
o
t

t
h
e

L
O
E
C

v
a
l
u
e
Pr
o
b
a
b
l
e

-

E
x
p
o
s
u
r
e

e
x
c
e
e
d
s

t
h
e

L
O
E
C

v
a
l
u
e
Co
m
m
e
n
t
s
ND

-

E
x
c
e
e
d
a
n
c
e
s

D
e
t
e
c
t
e
d

-

E
x
c
e
e
d
a
n
c
e
s
LO
E
C

Ex
c
e
e
d
a
n
c
e

Fr
e
q
u
e
n
c
y
Ri
s
k
Co
n
c
l
u
s
i
o
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
5
Pa
g
e

1

o
f

1
Ta
b
l
e

2
6
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d
y

W
e
i
g
h
t

(k
g
)
Da
i
l
y

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
bw
/
d
a
y
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l
y

F
o
o
d

In
g
e
s
t
i
o
n
fr
o
m

S
i
t
e

(k
g
/
k
g
-
bw
/
d
a
y
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r
Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b
w
/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r

F
a
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b
w
/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b
w
/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b
w
/
d
)
d
Re
f
i
n
e
d

S
o
i
l

EP
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
bw
/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a
y
)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b
w
/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b
w
/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n
Fr
e
q
u
e
n
c
y

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
5

1
.
2
0
0.
1
3
3

0
.
1
3
3
0.
0
8
0
0

2
.
0
0
0.
0
0
0
1
7
8

0
.
1
3
4
0.
0
4

0
.
2
3.
3
0.
6
7

0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
7
6

0
.
7
5
2
0.
0
8
3
5

0
.
0
8
3
5
2.
0
0

2
.
0
0
0.
0
0
4
4
4

0
.
0
8
8
0
2

8

0
.
0
4
4

0
.
0
1
1

2
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
1
4

3
3
3.
6
6

3
.
6
6
10
.
5

2
.
0
0
0.
0
2
3
3

3
.
6
8
28
1.
8
0.
4
6

0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

H
M
X

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
8
.
3
5.
3
7

5
.
3
7
8.
1
2

2
.
0
0
0.
0
1
8
0

5
.
3
8
15
5.
4
1.
1
31
%
Pr
o
b
a
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
RD
X
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
4.
1
8

4
.
1
8
1.
5
0

2
.
0
0
0.
0
0
3
3
3

4
.
1
8
22
0
2.
1
0.
2
1

0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

E
n
e
r
g
e
t
i
c
s
5.
4

1
.
1
(d
e
t
s
)
Pr
o
b
a
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
n
t
i
m
o
n
y

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
2

0
.
6
8
4
0.
0
7
5
9

0
.
0
7
5
9
67

2
.
0
0
0.
1
4
9

0
.
2
2
5
0.
0
5
9

0
.
6
4
3.
8
0.
3
5

7
9
%
Po
s
s
i
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

C
a
d
m
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
9
1
0.
2
1
2

0
.
2
1
2
7.
8
0

2
.
0
0
0.
0
1
7
3

0
.
2
2
9
0.
7
7

1
.
4
2

0
.
3
0

0
.
1
6

4
4
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

C
o
p
p
e
r

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
2
5.
7
8

5
.
7
8
41
5
0

2
.
0
0
9.
2
3

1
5
11
.
7

1
5
.
1
4
1.
3
0.
9
9

8
5
%
Po
s
s
i
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

L
e
a
d

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
9
.
1
5.
4
5

5
.
4
5
11
0
0
0

2
.
0
0
24
.
5

2
9
.
9
0.
9
2

4
.
7
33
6.
4
83
%
Pr
o
b
a
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

M
o
l
y
b
d
e
n
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

1
.
9
7
0.
2
1
9

0
.
2
1
9
4.
9
3

2
.
0
0
0.
0
1
1
0

0
.
2
3
0
0.
2
6

2
.
6

0
.
8
8

0
.
0
8
8

9
1
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

N
i
t
r
a
t
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
0
0

1
2
.
8
1.
4
2

1
.
4
2
12
.
8

2
.
0
0
0.
0
2
8
4

1
.
4
5
50
7

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
2
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

P
e
r
c
h
l
o
r
a
t
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
8
2

7
6
9
85
.
4

8
5
.
4
2.
7
3

2
.
0
0
0.
0
0
6
0
6

8
5
.
4
2.
5
9

2
5
.
9
33
3.
3
50
%
Pr
o
b
a
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Se
l
e
n
i
u
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
3
3
3

0
.
3
3
3
5.
0
0

2
.
0
0
0.
0
1
1
1

0
.
3
4
4
0.
2

0
.
3
3
1.
7
1.
0
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

S
i
l
v
e
r

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
0

0
.
0
1
4
2
0.
0
0
1
5
7

0
.
0
0
1
5
7
1.
0
1

2
.
0
0
0.
0
0
2
2
5

0
.
0
0
3
8
2
2.
3
8

2
3
.
8

<
0
.
0
1

<
0
.
0
1

8
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

Z
i
n
c

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
2
13
.
6

1
3
.
6
33
7

2
.
0
0
0.
7
4
9

1
4
.
3
16
0

3
2
0

0
.
0
9
0

0
.
0
4
5

1
0
0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

I
n
o
r
g
a
n
i
c
s
72

1
1
(d
e
t
s
)
Pr
o
b
a
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
8
7

1
8
1
20
.
1

2
0
.
1
97

2
.
0
0
0.
2
1
5

2
0
.
4
5.
0
3

5
0
.
3
4.
0
0.
4
0

1
4
%
Po
s
s
i
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
n
t
h
r
a
c
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
8
2
6

0
.
8
2
6
3.
7
0

2
.
0
0
0.
0
0
8
2
2

0
.
8
3
5
10
0
0

N
S
V

<
0
.
0
1
--
7%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
0
.
5
1.
1
7

1
.
1
7
10
.
5

2
.
0
0
0.
0
2
3
3

1
.
1
9
11
0
1.
2
0.
1
2

0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
4.
5
5

4
.
5
5
10
.
5

2
.
0
0
0.
0
2
3
3

4
.
5
7
11
0
4.
6
0.
4
6

0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
8
4
0.
9
8
1

0
.
9
8
1
10
.
5

2
.
0
0
0.
0
2
3
3

1
.
0
0
11
0
1.
0
0.
1
0

0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
8
0
0

0
.
0
0
8
0
0
0.
1
4
4

2
.
0
0
0.
0
0
0
3
2
0

0
.
0
0
8
3
2
12
5

2
5
0

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

F
l
u
o
r
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
6
0
35
1

3
5
1
18
.
5

2
.
0
0
0.
0
4
1
0

3
5
1
12
5

2
5
0
2.
8
1.
4
14
%
Pr
o
b
a
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

N
a
p
h
t
h
a
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
2
.
2

1
2
1
13
.
5

1
3
.
5
9.
9
5

2
.
0
0
0.
0
2
2
1

1
3
.
5
50

1
5
0

0
.
2
7

0
.
0
9
0

2
5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
3
.
2
1.
4
7

1
.
4
7
49
.
1

2
.
0
0
0.
1
0
9

1
.
5
8
17
5

3
5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

P
A
H
s
7.
1

1
.
9
(d
e
t
s
)
Pr
o
b
a
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
1
6
9
0.
0
0
0
1
8
8

0
.
0
0
0
1
8
8
0.
0
0
0
4
7
5

2
.
0
0
0.
0
0
0
0
0
1
0
5

0
.
0
0
0
1
8
9
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
2
7
9

0
.
0
0
0
1
7
2
0.
0
0
0
0
1
9
1

0
.
0
0
0
0
1
9
1
0.
0
0
0
6
1
6

2
.
0
0
0.
0
0
0
0
0
1
3
7

0
.
0
0
0
0
2
0
5
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
2
4
5
0.
0
0
0
0
2
7
2

0
.
0
0
0
0
2
7
2
0.
0
0
0
6
9
2

2
.
0
0
0.
0
0
0
0
0
1
5
4

0
.
0
0
0
0
2
8
8
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
2
9
8

0
.
0
0
0
1
7
8
0.
0
0
0
0
1
9
7

0
.
0
0
0
0
1
9
7
0.
0
0
0
5
9
7

2
.
0
0
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
0
2
1
1
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
6
1
6
0.
0
0
0
0
6
8
4

0
.
0
0
0
0
6
8
4
0.
0
0
0
4
7
9

2
.
0
0
0.
0
0
0
0
0
1
0
6

0
.
0
0
0
0
6
9
4
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
7
4
1
0.
0
0
0
8
2
3

0
.
0
0
0
8
2
3
0.
0
0
0
8
9
7

2
.
0
0
0.
0
0
0
0
0
1
9
9

0
.
0
0
0
8
2
5
2.
5

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
3
7
3
0.
0
0
0
4
1
4

0
.
0
0
0
4
1
4
0.
0
0
0
6
3
8

2
.
0
0
0.
0
0
0
0
0
1
4
2

0
.
0
0
0
4
1
6
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
4
6
0.
0
0
0
1
6
3

0
.
0
0
0
1
6
3
0.
0
0
0
5
8
5

2
.
0
0
0.
0
0
0
0
0
1
3
0

0
.
0
0
0
1
6
4
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
1
0.
0
0
0
0
4
6
7

0
.
0
0
0
0
4
6
7
0.
0
0
0
5
1
5

2
.
0
0
0.
0
0
0
0
0
1
1
4

0
.
0
0
0
0
4
7
9
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

2
-
B
u
t
a
n
o
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
3
4
9
0.
0
3
8
8

0
.
0
3
8
8
0.
0
0
7
5
8

2
.
0
0
0.
0
0
0
0
1
6
8

0
.
0
3
8
8
10

5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2-
H
e
x
a
n
o
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
4
6
8
0.
0
0
5
1
9

0
.
0
0
5
1
9
0.
0
0
2
8
1

2
.
0
0
0.
0
0
0
0
0
6
2
4

0
.
0
0
5
2
0
10

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
6
4
7
0.
0
0
7
1
9

0
.
0
0
7
1
9
0.
0
0
3
2
6

2
.
0
0
0.
0
0
0
0
0
7
2
4

0
.
0
0
7
2
0
25

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
c
e
t
o
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

7
5
.
6

8
6
8
96
.
4

9
6
.
4
11
.
5

2
.
0
0
0.
0
2
5
5

9
6
.
4
10

5
0
9.
6
1.
9
32
%
Pr
o
b
a
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

B
e
n
z
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
1
2
8
0.
0
0
1
4
2

0
.
0
0
1
4
2
0.
0
0
1
5
4

2
.
0
0
0.
0
0
0
0
0
3
4
3

0
.
0
0
1
4
2
0.
7

7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Br
o
m
o
f
o
r
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
4
6

0
.
0
0
0
1
5
0
0.
0
0
0
0
1
6
6

0
.
0
0
0
0
1
6
6
0.
0
0
0
4
3
2

2
.
0
0
0.
0
0
0
0
0
0
9
5
9

0
.
0
0
0
0
1
7
6
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Br
o
m
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
1
8
2
0.
0
0
2
0
2

0
.
0
0
2
0
2
0.
0
0
0
9
1
7

2
.
0
0
0.
0
0
0
0
0
2
0
4

0
.
0
0
2
0
3
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
.
2
9

0
.
0
0
2
6
1
0.
0
0
0
2
9
0

0
.
0
0
0
2
9
0
0.
0
0
0
6
0
7

2
.
0
0
0.
0
0
0
0
0
1
3
5

0
.
0
0
0
2
9
1
16

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
7
5
2
0.
0
0
0
0
0
8
3
5

0
.
0
0
0
0
0
8
3
5
0.
0
0
0
5
6
0

2
.
0
0
0.
0
0
0
0
0
1
2
4

0
.
0
0
0
0
0
9
5
9
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
0
9
0.
0
0
0
2
3
2

0
.
0
0
0
2
3
2
0.
0
0
0
7
4
8

2
.
0
0
0.
0
0
0
0
0
1
6
6

0
.
0
0
0
2
3
3
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
f
o
r
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
8
7
3

0
.
0
0
0
3
9
9
0.
0
0
0
0
4
4
3

0
.
0
0
0
0
4
4
3
0.
0
0
0
4
5
7

2
.
0
0
0.
0
0
0
0
0
1
0
1

0
.
0
0
0
0
4
5
3
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
5
7
8
0.
0
0
0
6
4
2

0
.
0
0
0
6
4
2
0.
0
0
0
7
3
8

2
.
0
0
0.
0
0
0
0
0
1
6
4

0
.
0
0
0
6
4
3
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
5
2
8
0.
0
0
0
5
8
6

0
.
0
0
0
5
8
6
0.
0
0
0
4
9
7

2
.
0
0
0.
0
0
0
0
0
1
1
0

0
.
0
0
0
5
8
7
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
3
8
0
0.
0
0
0
4
2
2

0
.
0
0
0
4
2
2
0.
0
0
0
5
3
5

2
.
0
0
0.
0
0
0
0
0
1
1
9

0
.
0
0
0
4
2
4
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Et
h
y
l
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
3
8
9
0.
0
0
0
0
0
4
3
1

0
.
0
0
0
0
0
4
3
1
0.
0
0
0
5
6
3

2
.
0
0
0.
0
0
0
0
0
1
2
5

0
.
0
0
0
0
0
5
5
6
97

2
9
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
m,
p
-
X
y
l
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
2
9
3
0.
0
0
0
3
2
6

0
.
0
0
0
3
2
6
0.
0
0
0
9
6
5

2
.
0
0
0.
0
0
0
0
0
2
1
4

0
.
0
0
0
3
2
8
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
.
1
0

0
.
0
0
6
0
1
0.
0
0
0
6
6
7

0
.
0
0
0
6
6
7
0.
0
0
1
4
6

2
.
0
0
0.
0
0
0
0
0
3
2
5

0
.
0
0
0
6
7
0
5.
8
5

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

o
-
X
y
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
3
4

0
.
0
0
3
9
3
0.
0
0
0
4
3
6

0
.
0
0
0
4
3
6
0.
0
0
1
1
8

2
.
0
0
0.
0
0
0
0
0
2
6
1

0
.
0
0
0
4
3
9
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
1
6
5
0.
0
0
0
1
8
4

0
.
0
0
0
1
8
4
0.
0
0
0
6
5
6

2
.
0
0
0.
0
0
0
0
0
1
4
6

0
.
0
0
0
1
8
5
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

T
o
l
u
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
6
7
0
0.
0
0
7
4
4

0
.
0
0
7
4
4
0.
0
1
4
2

2
.
0
0
0.
0
0
0
0
3
1
6

0
.
0
0
7
4
7
52

5
2
0

<
0
.
0
1

<
0
.
0
1

2
3
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
3
8
0.
0
0
0
1
5
4

0
.
0
0
0
1
5
4
0.
0
0
0
5
5
2

2
.
0
0
0.
0
0
0
0
0
1
2
3

0
.
0
0
0
1
5
5
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
4
0.
0
0
0
0
4
7
1

0
.
0
0
0
0
4
7
1
0.
0
0
0
5
1
9

2
.
0
0
0.
0
0
0
0
0
1
1
5

0
.
0
0
0
0
4
8
3
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

0
.
3
3
1

0
.
0
0
0
1
6
9
0.
0
0
0
0
1
8
7

0
.
0
0
0
0
1
8
7
0.
0
0
0
5
0
9

2
.
0
0
0.
0
0
0
0
0
1
1
3

0
.
0
0
0
0
1
9
9
0.
7

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0
0
10
0

3
.
1
0

0
.
0
0
2
2
9
0.
0
0
0
2
5
4

0
.
0
0
0
2
5
4
0.
0
0
0
7
3
8

2
.
0
0
0.
0
0
0
0
0
1
6
4

0
.
0
0
0
2
5
6
0.
1
7

1
.
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

V
O
C
s
9.
6

1
.
9
(d
e
t
s
)
Pr
o
b
a
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
5

1
.
2
0
0.
0
6
0
0

0
.
0
6
0
0
0.
0
8
0
0

2
.
0
0
0.
0
0
0
0
7
9
9

0
.
0
6
0
1
0.
0
4

0
.
2
1.
5
0.
3
0

0
%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
3
7
6

0
.
7
5
2
0.
0
3
7
6

0
.
0
3
7
6
2.
0
0

2
.
0
0
0.
0
0
2
0
0

0
.
0
3
9
6
2

8

0
.
0
2
0

<
0
.
0
1

2
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

3
.
1
4

3
3
1.
6
5

1
.
6
5
10
.
5

2
.
0
0
0.
0
1
0
5

1
.
6
6
2

8

0
.
8
3

0
.
2
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

H
M
X

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
8
.
3
2.
4
1

2
.
4
1
8.
1
2

2
.
0
0
0.
0
0
8
1
1

2
.
4
2
15
2.
4
0.
4
8

3
1
%
Po
s
s
i
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

E
n
e
r
g
e
t
i
c
s
2.
4
0.
4
9
(d
e
t
s
)
Po
s
s
i
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

A
n
t
i
m
o
n
y

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
2

0
.
6
8
4
0.
0
3
4
1

0
.
0
3
4
1
67

2
.
0
0
0.
0
6
7
0

0
.
1
0
1
0.
0
5
9

0
.
6
4
1.
7
0.
1
6

7
9
%
Po
s
s
i
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

C
a
d
m
i
u
m

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
9
1
0.
0
9
5
2

0
.
0
9
5
2
7.
8
0

2
.
0
0
0.
0
0
7
7
9

0
.
1
0
3
0.
7
7

1
.
4
2

0
.
1
3

0
.
0
7
3

4
4
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

C
o
p
p
e
r

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
2
2.
6
0

2
.
6
0
41
5
0

2
.
0
0
4.
1
5

6
.
7
5
11
.
7

1
5
.
1
4

0
.
5
8

0
.
4
5

8
5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

L
e
a
d

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
9
.
1
2.
4
5

2
.
4
5
11
0
0
0

2
.
0
0
11

1
3
.
4
0.
9
2

4
.
7
15
2.
9
83
%
Pr
o
b
a
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

M
o
l
y
b
d
e
n
u
m

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

1
.
9
7
0.
0
9
8
6

0
.
0
9
8
6
4.
9
3

2
.
0
0
0.
0
0
4
9
3

0
.
1
0
4
0.
2
6

2
.
6

0
.
4
0

0
.
0
4
0

9
1
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

N
i
t
r
a
t
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
.
0
0

1
2
.
8
0.
6
3
8

0
.
6
3
8
12
.
8

2
.
0
0
0.
0
1
2
8

0
.
6
5
1
50
7

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
2
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

P
e
r
c
h
l
o
r
a
t
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

2
8
2

7
6
9
38
.
4

3
8
.
4
2.
7
3

2
.
0
0
0.
0
0
2
7
2

3
8
.
4
2.
5
9

2
5
.
9
15
1.
5
50
%
Pr
o
b
a
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

S
i
l
v
e
r

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
0

0
.
0
1
4
2
0.
0
0
0
7
0
8

0
.
0
0
0
7
0
8
1.
0
1

2
.
0
0
0.
0
0
1
0
1

0
.
0
0
1
7
2
2.
3
8

2
3
.
8

<
0
.
0
1

<
0
.
0
1

8
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

Z
i
n
c

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
2
6.
1
0

6
.
1
0
33
7

2
.
0
0
0.
3
3
7

6
.
4
4
16
0

3
2
0

0
.
0
4
0

0
.
0
2
0

1
0
0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

I
n
o
r
g
a
n
i
c
s
32

5
.
1
(d
e
t
s
)
Pr
o
b
a
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
.
8
7

1
8
1
9.
0
6

9
.
0
6
97

2
.
0
0
0.
0
9
6
9

9
.
1
5
5.
0
3

5
0
.
3
1.
8
0.
1
8

1
4
%
Po
s
s
i
b
l
e
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
6
Pa
g
e

1

o
f

7
Ta
b
l
e

2
6
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b

/
d
a

)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n
fr
o
m

S
i
t
e

(k
g
/
k
g
-
b

/
d
a

)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r
Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r

F
a
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

S
o
i
l

EP
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b

/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n
Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

A
n
t
h
r
a
c
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
3
7
2

0
.
3
7
2
3.
7
0

2
.
0
0
0.
0
0
3
7
0

0
.
3
7
5
10
0
0

N
S
V

<
0
.
0
1
--
7%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
2.
0
5

2
.
0
5
10
.
5

2
.
0
0
0.
0
1
0
5

2
.
0
6
11
0
2.
1
0.
2
1

0
%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

F
l
u
o
r
a
n
t
h
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
3
6
0

0
.
0
0
3
6
0
0.
1
4
4

2
.
0
0
0.
0
0
0
1
4
4

0
.
0
0
3
7
4
12
5

2
5
0

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

F
l
u
o
r
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
6
0
15
8

1
5
8
18
.
5

2
.
0
0
0.
0
1
8
5

1
5
8
12
5

2
5
0
1.
3
0.
6
3

1
4
%
Po
s
s
i
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

N
a
p
h
t
h
a
l
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
2
.
2

1
2
1
6.
0
6

6
.
0
6
9.
9
5

2
.
0
0
0.
0
0
9
9
4

6
.
0
7
50

1
5
0

0
.
1
2

0
.
0
4
0

2
5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

P
h
e
n
a
n
t
h
r
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
3
.
2
0.
6
6
0

0
.
6
6
0
49
.
1

2
.
0
0
0.
0
4
9
0

0
.
7
0
9
17
5

3
5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

P
A
H
s
3.
2
0.
8
6
(d
e
t
s
)
Po
s
s
i
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
1
6
9
0.
0
0
0
0
8
4
5

0
.
0
0
0
0
8
4
5
0.
0
0
0
4
7
5

2
.
0
0
0.
0
0
0
0
0
0
4
7
4

0
.
0
0
0
0
8
4
9
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
2
7
9

0
.
0
0
0
1
7
2
0.
0
0
0
0
0
8
5
9

0
.
0
0
0
0
0
8
5
9
0.
0
0
0
6
1
6

2
.
0
0
0.
0
0
0
0
0
0
6
1
5

0
.
0
0
0
0
0
9
2
0
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
2
4
5
0.
0
0
0
0
1
2
2

0
.
0
0
0
0
1
2
2
0.
0
0
0
6
9
2

2
.
0
0
0.
0
0
0
0
0
0
6
9
2

0
.
0
0
0
0
1
2
9
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
2
9
8

0
.
0
0
0
1
7
8
0.
0
0
0
0
0
8
8
8

0
.
0
0
0
0
0
8
8
8
0.
0
0
0
5
9
7

2
.
0
0
0.
0
0
0
0
0
0
5
9
7

0
.
0
0
0
0
0
9
4
8
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
6
1
6
0.
0
0
0
0
3
0
8

0
.
0
0
0
0
3
0
8
0.
0
0
0
4
7
9

2
.
0
0
0.
0
0
0
0
0
0
4
7
9

0
.
0
0
0
0
3
1
2
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
7
4
1
0.
0
0
0
3
7
0

0
.
0
0
0
3
7
0
0.
0
0
0
8
9
7

2
.
0
0
0.
0
0
0
0
0
0
8
9
6

0
.
0
0
0
3
7
1
2.
5

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
3
7
3
0.
0
0
0
1
8
6

0
.
0
0
0
1
8
6
0.
0
0
0
6
3
8

2
.
0
0
0.
0
0
0
0
0
0
6
3
8

0
.
0
0
0
1
8
7
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
4
6
0.
0
0
0
0
7
3
1

0
.
0
0
0
0
7
3
1
0.
0
0
0
5
8
5

2
.
0
0
0.
0
0
0
0
0
0
5
8
4

0
.
0
0
0
0
7
3
7
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
1
0.
0
0
0
0
2
1
0

0
.
0
0
0
0
2
1
0
0.
0
0
0
5
1
5

2
.
0
0
0.
0
0
0
0
0
0
5
1
4

0
.
0
0
0
0
2
1
5
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

2
-
B
u
t
a
n
o
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
3
4
9
0.
0
1
7
4

0
.
0
1
7
4
0.
0
0
7
5
8

2
.
0
0
0.
0
0
0
0
0
7
5
7

0
.
0
1
7
4
10

5
0

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0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
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H
e
x
a
n
o
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
4
6
8
0.
0
0
2
3
4

0
.
0
0
2
3
4
0.
0
0
2
8
1

2
.
0
0
0.
0
0
0
0
0
2
8
1

0
.
0
0
2
3
4
10

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
6
4
7
0.
0
0
3
2
3

0
.
0
0
3
2
3
0.
0
0
3
2
6

2
.
0
0
0.
0
0
0
0
0
3
2
5

0
.
0
0
3
2
4
25

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

A
c
e
t
o
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

7
5
.
6

8
6
8
43
.
4

4
3
.
4
11
.
5

2
.
0
0
0.
0
1
1
5

4
3
.
4
10

5
0
4.
3
0.
8
7

3
2
%
Po
s
s
i
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

B
e
n
z
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
1
2
8
0.
0
0
0
6
3
7

0
.
0
0
0
6
3
7
0.
0
0
1
5
4

2
.
0
0
0.
0
0
0
0
0
1
5
4

0
.
0
0
0
6
3
9
0.
7

7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Br
o
m
o
f
o
r
m
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
3
4
6

0
.
0
0
0
1
5
0
0.
0
0
0
0
0
7
4
7

0
.
0
0
0
0
0
7
4
7
0.
0
0
0
4
3
2

2
.
0
0
0.
0
0
0
0
0
0
4
3
2

0
.
0
0
0
0
0
7
9
0
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Br
o
m
o
m
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
1
8
2
0.
0
0
0
9
1
0

0
.
0
0
0
9
1
0
0.
0
0
0
9
1
7

2
.
0
0
0.
0
0
0
0
0
0
9
1
6

0
.
0
0
0
9
1
1
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
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d
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

4
.
2
9

0
.
0
0
2
6
1
0.
0
0
0
1
3
0

0
.
0
0
0
1
3
0
0.
0
0
0
6
0
7

2
.
0
0
0.
0
0
0
0
0
0
6
0
7

0
.
0
0
0
1
3
1
16

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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e
l
Ch
l
o
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o
b
e
n
z
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
7
5
2
0.
0
0
0
0
0
3
7
6

0
.
0
0
0
0
0
3
7
6
0.
0
0
0
5
6
0

2
.
0
0
0.
0
0
0
0
0
0
5
5
9

0
.
0
0
0
0
0
4
3
1
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
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l
Ch
l
o
r
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e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
0
9
0.
0
0
0
1
0
4

0
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0
0
0
1
0
4
0.
0
0
0
7
4
8

2
.
0
0
0.
0
0
0
0
0
0
7
4
7

0
.
0
0
0
1
0
5
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
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l
Ch
l
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o
f
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r
m
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
8
7
3

0
.
0
0
0
3
9
9
0.
0
0
0
0
1
9
9

0
.
0
0
0
0
1
9
9
0.
0
0
0
4
5
7

2
.
0
0
0.
0
0
0
0
0
0
4
5
6

0
.
0
0
0
0
2
0
4
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
5
7
8
0.
0
0
0
2
8
9

0
.
0
0
0
2
8
9
0.
0
0
0
7
3
8

2
.
0
0
0.
0
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0
0
0
0
7
3
8

0
.
0
0
0
2
8
9
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
5
2
8
0.
0
0
0
2
6
4

0
.
0
0
0
2
6
4
0.
0
0
0
4
9
7

2
.
0
0
0.
0
0
0
0
0
0
4
9
6

0
.
0
0
0
2
6
4
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
ci
s
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1
,
3
-
D
i
c
h
l
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p
r
o
p
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
3
8
0
0.
0
0
0
1
9
0

0
.
0
0
0
1
9
0
0.
0
0
0
5
3
5

2
.
0
0
0.
0
0
0
0
0
0
5
3
4

0
.
0
0
0
1
9
1
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
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h
y
l
b
e
n
z
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
3
8
9
0.
0
0
0
0
0
1
9
4

0
.
0
0
0
0
0
1
9
4
0.
0
0
0
5
6
3

2
.
0
0
0.
0
0
0
0
0
0
5
6
2

0
.
0
0
0
0
0
2
5
0
97

2
9
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l
m,
p
-
X
y
l
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
2
9
3
0.
0
0
0
1
4
6

0
.
0
0
0
1
4
6
0.
0
0
0
9
6
5

2
.
0
0
0.
0
0
0
0
0
0
9
6
4

0
.
0
0
0
1
4
7
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
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r
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l
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t
h
y
l
e
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e

c
h
l
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r
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d
e
0.
3
2
5

0
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0
5
0

1

0
.
0
5
0

0

-

0

0

0

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0
0
10
0

4
.
1
0

0
.
0
0
6
0
1
0.
0
0
0
3
0
0

0
.
0
0
0
3
0
0
0.
0
0
1
4
6

2
.
0
0
0.
0
0
0
0
0
1
4
6

0
.
0
0
0
3
0
2
5.
8
5

5
0

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0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
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l

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y
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e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

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0

0

0

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0
0
10
0

3
.
3
4

0
.
0
0
3
9
3
0.
0
0
0
1
9
6

0
.
0
0
0
1
9
6
0.
0
0
1
1
8

2
.
0
0
0.
0
0
0
0
0
1
1
8

0
.
0
0
0
1
9
7
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
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t
r
a
c
h
l
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e
t
h
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
1
6
5
0.
0
0
0
0
8
2
6

0
.
0
0
0
0
8
2
6
0.
0
0
0
6
5
6

2
.
0
0
0.
0
0
0
0
0
0
6
5
5

0
.
0
0
0
0
8
3
2
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
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l

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o
l
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e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
6
7
0
0.
0
0
3
3
5

0
.
0
0
3
3
5
0.
0
1
4
2

2
.
0
0
0.
0
0
0
0
1
4
2

0
.
0
0
3
3
6
52

5
2
0

<
0
.
0
1

<
0
.
0
1

2
3
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
3
8
0.
0
0
0
0
6
9
0

0
.
0
0
0
0
6
9
0
0.
0
0
0
5
5
2

2
.
0
0
0.
0
0
0
0
0
0
5
5
2

0
.
0
0
0
0
6
9
6
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
4
0.
0
0
0
0
2
1
2

0
.
0
0
0
0
2
1
2
0.
0
0
0
5
1
9

2
.
0
0
0.
0
0
0
0
0
0
5
1
8

0
.
0
0
0
0
2
1
7
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

0
.
3
3
1

0
.
0
0
0
1
6
9
0.
0
0
0
0
0
8
4
3

0
.
0
0
0
0
0
8
4
3
0.
0
0
0
5
0
9

2
.
0
0
0.
0
0
0
0
0
0
5
0
9

0
.
0
0
0
0
0
8
9
4
0.
7

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0
0
10
0

3
.
1
0

0
.
0
0
2
2
9
0.
0
0
0
1
1
4

0
.
0
0
0
1
1
4
0.
0
0
0
7
3
8

2
.
0
0
0.
0
0
0
0
0
0
7
3
7

0
.
0
0
0
1
1
5
0.
1
7

1
.
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

V
O
C
s
4.
3
0.
8
7
(d
e
t
s
)
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
5

1
.
2
0
0.
0
8
5
8

0
.
0
8
5
8
0.
0
8
0
0

6
.
3
0
0.
0
0
0
3
6
0

0
.
0
8
6
2
0.
0
4

0
.
2
2.
2
0.
4
3

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
7
6

0
.
7
5
2
0.
0
5
3
7

0
.
0
5
3
7
2.
0
0

6
.
3
0
0.
0
0
9
0
0

0
.
0
6
2
7
2

8

0
.
0
3
1

<
0
.
0
1

2
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
1
4

3
3
2.
3
6

2
.
3
6
10
.
5

6
.
3
0
0.
0
4
7
3

2
.
4
0
28
1.
2
0.
3
0

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

H
M
X

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
8
.
3
3.
4
5

3
.
4
5
8.
1
2

6
.
3
0
0.
0
3
6
5

3
.
4
9
15
3.
5
0.
7
0

3
1
%
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
RD
X
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
2.
6
9

2
.
6
9
1.
5
0

6
.
3
0
0.
0
0
6
7
5

2
.
6
9
22
0
1.
4
0.
1
4

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

E
n
e
r
g
e
t
i
c
s
3.
5
0.
7
1
(d
e
t
s
)
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
n
t
i
m
o
n
y

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
2

0
.
6
8
4
0.
0
4
8
9

0
.
0
4
8
9
67

6
.
3
0
0.
3
0
2

0
.
3
5
1
0.
0
5
9

0
.
6
4
5.
9
0.
5
5

7
9
%
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

C
a
d
m
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
9
1
0.
1
3
6

0
.
1
3
6
7.
8
0

6
.
3
0
0.
0
3
5
1

0
.
1
7
1
0.
7
7

1
.
4
2

0
.
2
2

0
.
1
2

4
4
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

C
o
p
p
e
r

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
2
3.
7
2

3
.
7
2
41
5
0

6
.
3
0
18
.
7

2
2
.
4
11
.
7

1
5
.
1
4
1.
9
1.
5
85
%
Pr
o
b
a
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

L
e
a
d

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
9
.
1
3.
5
1

3
.
5
1
11
0
0
0

6
.
3
0
49
.
6

5
3
.
1
0.
9
2

4
.
7
58
11
83
%
Pr
o
b
a
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

M
o
l
y
b
d
e
n
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

1
.
9
7
0.
1
4
1

0
.
1
4
1
4.
9
3

6
.
3
0
0.
0
2
2
2

0
.
1
6
3
0.
2
6

2
.
6

0
.
6
3

0
.
0
6
3

9
1
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

N
i
t
r
a
t
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
0
0

1
2
.
8
0.
9
1
3

0
.
9
1
3
12
.
8

6
.
3
0
0.
0
5
7
5

0
.
9
7
0
50
7

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
2
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

P
e
r
c
h
l
o
r
a
t
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
8
2

7
6
9
55

5
5
2.
7
3

6
.
3
0
0.
0
1
2
3

5
5
2.
5
9

2
5
.
9
21
2.
1
50
%
Pr
o
b
a
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Se
l
e
n
i
u
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
2
1
4

0
.
2
1
4
5.
0
0

6
.
3
0
0.
0
2
2
5

0
.
2
3
7
0.
2

0
.
3
3
1.
2
0.
7
2

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

S
i
l
v
e
r

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
0

0
.
0
1
4
2
0.
0
0
1
0
1

0
.
0
0
1
0
1
1.
0
1

6
.
3
0
0.
0
0
4
5
6

0
.
0
0
5
5
7
2.
3
8

2
3
.
8

<
0
.
0
1

<
0
.
0
1

8
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

Z
i
n
c

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
2
8.
7
3

8
.
7
3
33
7

6
.
3
0
1.
5
2

1
0
.
2
16
0

3
2
0

0
.
0
6
4

0
.
0
3
2

1
0
0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

I
n
o
r
g
a
n
i
c
s
88

1
6
(d
e
t
s
)
Pr
o
b
a
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
8
7

1
8
1
13

1
3
97

6
.
3
0
0.
4
3
7

1
3
.
4
5.
0
3

5
0
.
3
2.
7
0.
2
7

1
4
%
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
n
t
h
r
a
c
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
5
3
2

0
.
5
3
2
3.
7
0

6
.
3
0
0.
0
1
6
7

0
.
5
4
8
10
0
0

N
S
V

<
0
.
0
1
--
7%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
2.
9
3

2
.
9
3
10
.
5

6
.
3
0
0.
0
4
7
3

2
.
9
7
11
0
3.
0
0.
3
0

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

F
l
u
o
r
a
n
t
h
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
5
1
4

0
.
0
0
5
1
4
0.
1
4
4

6
.
3
0
0.
0
0
0
6
4
8

0
.
0
0
5
7
9
12
5

2
5
0

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

F
l
u
o
r
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
6
0
22
6

2
2
6
18
.
5

6
.
3
0
0.
0
8
3
2

2
2
6
12
5

2
5
0
1.
8
0.
9
0

1
4
%
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

N
a
p
h
t
h
a
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
2
.
2

1
2
1
8.
6
7

8
.
6
7
9.
9
5

6
.
3
0
0.
0
4
4
8

8
.
7
1
50

1
5
0

0
.
1
7

0
.
0
5
8

2
5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

P
h
e
n
a
n
t
h
r
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
3
.
2
0.
9
4
4

0
.
9
4
4
49
.
1

6
.
3
0
0.
2
2
1

1
.
1
7
17
5

3
5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

P
A
H
s
4.
6

1
.
2
(d
e
t
s
)
Pr
o
b
a
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
2
0
2

1
.
0
1
0.
0
7
2
2

0
.
0
7
2
2
50

6
.
3
0
0.
2
2
5

0
.
2
9
7
0.
2
4

2
.
4
1.
2
0.
1
2

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
1
6
9
0.
0
0
0
1
2
1

0
.
0
0
0
1
2
1
0.
0
0
0
4
7
5

6
.
3
0
0.
0
0
0
0
0
2
1
4

0
.
0
0
0
1
2
3
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
2
7
9

0
.
0
0
0
1
7
2
0.
0
0
0
0
1
2
3

0
.
0
0
0
0
1
2
3
0.
0
0
0
6
1
6

6
.
3
0
0.
0
0
0
0
0
2
7
7

0
.
0
0
0
0
1
5
1
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
2
4
5
0.
0
0
0
0
1
7
5

0
.
0
0
0
0
1
7
5
0.
0
0
0
6
9
2

6
.
3
0
0.
0
0
0
0
0
3
1
2

0
.
0
0
0
0
2
0
6
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
2
9
8

0
.
0
0
0
1
7
8
0.
0
0
0
0
1
2
7

0
.
0
0
0
0
1
2
7
0.
0
0
0
5
9
7

6
.
3
0
0.
0
0
0
0
0
2
6
9

0
.
0
0
0
0
1
5
4
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
6
1
6
0.
0
0
0
0
4
4
0

0
.
0
0
0
0
4
4
0
0.
0
0
0
4
7
9

6
.
3
0
0.
0
0
0
0
0
2
1
6

0
.
0
0
0
0
4
6
2
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
7
4
1
0.
0
0
0
5
2
9

0
.
0
0
0
5
2
9
0.
0
0
0
8
9
7

6
.
3
0
0.
0
0
0
0
0
4
0
4

0
.
0
0
0
5
3
4
2.
5

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
3
7
3
0.
0
0
0
2
6
7

0
.
0
0
0
2
6
7
0.
0
0
0
6
3
8

6
.
3
0
0.
0
0
0
0
0
2
8
7

0
.
0
0
0
2
6
9
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
4
6
0.
0
0
0
1
0
5

0
.
0
0
0
1
0
5
0.
0
0
0
5
8
5

6
.
3
0
0.
0
0
0
0
0
2
6
3

0
.
0
0
0
1
0
7
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
1
0.
0
0
0
0
3
0
1

0
.
0
0
0
0
3
0
1
0.
0
0
0
5
1
5

6
.
3
0
0.
0
0
0
0
0
2
3
2

0
.
0
0
0
0
3
2
4
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

2
-
B
u
t
a
n
o
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
3
4
9
0.
0
2
4
9

0
.
0
2
4
9
0.
0
0
7
5
8

6
.
3
0
0.
0
0
0
0
3
4
1

0
.
0
2
5
0
10

5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
6
Pa
g
e

2

o
f

7
Ta
b
l
e

2
6
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b

/
d
a

)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n
fr
o
m

S
i
t
e

(k
g
/
k
g
-
b

/
d
a

)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r
Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r

F
a
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

S
o
i
l

EP
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b

/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n
Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2-
H
e
x
a
n
o
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
4
6
8
0.
0
0
3
3
4

0
.
0
0
3
3
4
0.
0
0
2
8
1

6
.
3
0
0.
0
0
0
0
1
2
7

0
.
0
0
3
3
5
10

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
6
4
7
0.
0
0
4
6
3

0
.
0
0
4
6
3
0.
0
0
3
2
6

6
.
3
0
0.
0
0
0
0
1
4
7

0
.
0
0
4
6
4
25

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
c
e
t
o
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

7
5
.
6

8
6
8
62

6
2
11
.
5

6
.
3
0
0.
0
5
1
7

6
2
.
1
10

5
0
6.
2
1.
2
32
%
Pr
o
b
a
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

B
e
n
z
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
1
2
8
0.
0
0
0
9
1
1

0
.
0
0
0
9
1
1
0.
0
0
1
5
4

6
.
3
0
0.
0
0
0
0
0
6
9
5

0
.
0
0
0
9
1
8
0.
7

7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Br
o
m
o
f
o
r
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
4
6

0
.
0
0
0
1
5
0
0.
0
0
0
0
1
0
7

0
.
0
0
0
0
1
0
7
0.
0
0
0
4
3
2

6
.
3
0
0.
0
0
0
0
0
1
9
4

0
.
0
0
0
0
1
2
6
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Br
o
m
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
1
8
2
0.
0
0
1
3
0

0
.
0
0
1
3
0
0.
0
0
0
9
1
7

6
.
3
0
0.
0
0
0
0
0
4
1
3

0
.
0
0
1
3
1
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
.
2
9

0
.
0
0
2
6
1
0.
0
0
0
1
8
6

0
.
0
0
0
1
8
6
0.
0
0
0
6
0
7

6
.
3
0
0.
0
0
0
0
0
2
7
3

0
.
0
0
0
1
8
9
16

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
7
5
2
0.
0
0
0
0
0
5
3
7

0
.
0
0
0
0
0
5
3
7
0.
0
0
0
5
6
0

6
.
3
0
0.
0
0
0
0
0
2
5
2

0
.
0
0
0
0
0
7
8
9
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
0
9
0.
0
0
0
1
4
9

0
.
0
0
0
1
4
9
0.
0
0
0
7
4
8

6
.
3
0
0.
0
0
0
0
0
3
3
7

0
.
0
0
0
1
5
2
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
f
o
r
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
8
7
3

0
.
0
0
0
3
9
9
0.
0
0
0
0
2
8
5

0
.
0
0
0
0
2
8
5
0.
0
0
0
4
5
7

6
.
3
0
0.
0
0
0
0
0
2
0
6

0
.
0
0
0
0
3
0
5
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
5
7
8
0.
0
0
0
4
1
3

0
.
0
0
0
4
1
3
0.
0
0
0
7
3
8

6
.
3
0
0.
0
0
0
0
0
3
3
2

0
.
0
0
0
4
1
6
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
5
2
8
0.
0
0
0
3
7
7

0
.
0
0
0
3
7
7
0.
0
0
0
4
9
7

6
.
3
0
0.
0
0
0
0
0
2
2
4

0
.
0
0
0
3
8
0
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
3
8
0
0.
0
0
0
2
7
2

0
.
0
0
0
2
7
2
0.
0
0
0
5
3
5

6
.
3
0
0.
0
0
0
0
0
2
4
1

0
.
0
0
0
2
7
4
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Et
h
y
l
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
3
8
9
0.
0
0
0
0
0
2
7
8

0
.
0
0
0
0
0
2
7
8
0.
0
0
0
5
6
3

6
.
3
0
0.
0
0
0
0
0
2
5
3

0
.
0
0
0
0
0
5
3
1
97

2
9
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
m,
p
-
X
y
l
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
2
9
3
0.
0
0
0
2
1
0

0
.
0
0
0
2
1
0
0.
0
0
0
9
6
5

6
.
3
0
0.
0
0
0
0
0
4
3
4

0
.
0
0
0
2
1
4
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
.
1
0

0
.
0
0
6
0
1
0.
0
0
0
4
2
9

0
.
0
0
0
4
2
9
0.
0
0
1
4
6

6
.
3
0
0.
0
0
0
0
0
6
5
9

0
.
0
0
0
4
3
6
5.
8
5

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

o
-
X
y
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
3
4

0
.
0
0
3
9
3
0.
0
0
0
2
8
1

0
.
0
0
0
2
8
1
0.
0
0
1
1
8

6
.
3
0
0.
0
0
0
0
0
5
3
0

0
.
0
0
0
2
8
6
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
1
6
5
0.
0
0
0
1
1
8

0
.
0
0
0
1
1
8
0.
0
0
0
6
5
6

6
.
3
0
0.
0
0
0
0
0
2
9
5

0
.
0
0
0
1
2
1
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

T
o
l
u
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
6
7
0
0.
0
0
4
7
9

0
.
0
0
4
7
9
0.
0
1
4
2

6
.
3
0
0.
0
0
0
0
6
3
9

0
.
0
0
4
8
5
52

5
2
0

<
0
.
0
1

<
0
.
0
1

2
3
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
3
8
0.
0
0
0
0
9
8
8

0
.
0
0
0
0
9
8
8
0.
0
0
0
5
5
2

6
.
3
0
0.
0
0
0
0
0
2
4
9

0
.
0
0
0
1
0
1
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
4
0.
0
0
0
0
3
0
3

0
.
0
0
0
0
3
0
3
0.
0
0
0
5
1
9

6
.
3
0
0.
0
0
0
0
0
2
3
4

0
.
0
0
0
0
3
2
6
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

0
.
3
3
1

0
.
0
0
0
1
6
9
0.
0
0
0
0
1
2
1

0
.
0
0
0
0
1
2
1
0.
0
0
0
5
0
9

6
.
3
0
0.
0
0
0
0
0
2
2
9

0
.
0
0
0
0
1
4
4
0.
7

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Vi
n
y
l

c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0
0
10
0

3
.
1
0

0
.
0
0
2
2
9
0.
0
0
0
1
6
4

0
.
0
0
0
1
6
4
0.
0
0
0
7
3
8

6
.
3
0
0.
0
0
0
0
0
3
3
2

0
.
0
0
0
1
6
7
0.
1
7

1
.
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

V
O
C
s
6.
2

1
.
2
(d
e
t
s
)
Pr
o
b
a
b
l
e
Pr
o
n
g
h
o
r
n
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
5

1
.
2
0
0.
0
4
1
3

0
.
0
4
1
3
0.
0
8
0
0

2
.
0
0
0.
0
0
0
0
5
5
0

0
.
0
4
1
4
0.
0
4

0
.
2
1.
0
0.
2
1

0
%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
7
6

0
.
7
5
2
0.
0
2
5
9

0
.
0
2
5
9
2.
0
0

2
.
0
0
0.
0
0
1
3
8

0
.
0
2
7
2
2

8

0
.
0
1
4

<
0
.
0
1

2
%
No
n
e
Pr
o
n
g
h
o
r
n
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
1
4

3
3
1.
1
3

1
.
1
3
10
.
5

2
.
0
0
0.
0
0
7
2
2

1
.
1
4
2

8

0
.
5
7

0
.
1
4

0
%
No
n
e
Pr
o
n
g
h
o
r
n

H
M
X

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
8
.
3
1.
6
6

1
.
6
6
8.
1
2

2
.
0
0
0.
0
0
5
5
8

1
.
6
7
15
1.
7
0.
3
3

3
1
%
Po
s
s
i
b
l
e
Pr
o
n
g
h
o
r
n
HI

-

E
n
e
r
g
e
t
i
c
s
1.
7
0.
3
4
(d
e
t
s
)
Po
s
s
i
b
l
e
Pr
o
n
g
h
o
r
n

A
n
t
i
m
o
n
y

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
1
0
2

0
.
6
8
4
0.
0
2
3
5

0
.
0
2
3
5
67

2
.
0
0
0.
0
4
6
1

0
.
0
6
9
6
0.
0
5
9

0
.
6
4
1.
2
0.
1
1

7
9
%
Po
s
s
i
b
l
e
Pr
o
n
g
h
o
r
n

C
a
d
m
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
9
1
0.
0
6
5
6

0
.
0
6
5
6
7.
8
0

2
.
0
0
0.
0
0
5
3
6

0
.
0
7
0
9
0.
7
7

1
.
4
2

0
.
0
9
2

0
.
0
5
0

4
4
%
No
n
e
Pr
o
n
g
h
o
r
n

C
o
p
p
e
r

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
2
1.
7
9

1
.
7
9
41
5
0

2
.
0
0
2.
8
6

4
.
6
5
11
.
7

1
5
.
1
4

0
.
4
0

0
.
3
1

8
5
%
No
n
e
Pr
o
n
g
h
o
r
n

L
e
a
d

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
9
.
1
1.
6
9

1
.
6
9
11
0
0
0

2
.
0
0
7.
5
7

9
.
2
6
0.
9
2

4
.
7
10
2.
0
83
%
Pr
o
b
a
b
l
e
Pr
o
n
g
h
o
r
n

M
o
l
y
b
d
e
n
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

1
.
9
7
0.
0
6
7
9

0
.
0
6
7
9
4.
9
3

2
.
0
0
0.
0
0
3
3
9

0
.
0
7
1
3
0.
2
6

2
.
6

0
.
2
7

0
.
0
2
7

9
1
%
No
n
e
Pr
o
n
g
h
o
r
n

N
i
t
r
a
t
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
0
0

1
2
.
8
0.
4
3
9

0
.
4
3
9
12
.
8

2
.
0
0
0.
0
0
8
7
9

0
.
4
4
8
50
7

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
2
%
No
n
e
Pr
o
n
g
h
o
r
n

P
e
r
c
h
l
o
r
a
t
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
8
2

7
6
9
26
.
4

2
6
.
4
2.
7
3

2
.
0
0
0.
0
0
1
8
8

2
6
.
5
2.
5
9

2
5
.
9
10
1.
0
50
%
Pr
o
b
a
b
l
e
Pr
o
n
g
h
o
r
n

S
i
l
v
e
r

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
1
4
0

0
.
0
1
4
2
0.
0
0
0
4
8
7

0
.
0
0
0
4
8
7
1.
0
1

2
.
0
0
0.
0
0
0
6
9
6

0
.
0
0
1
1
8
2.
3
8

2
3
.
8

<
0
.
0
1

<
0
.
0
1

8
%
No
n
e
Pr
o
n
g
h
o
r
n

Z
i
n
c

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
2
4.
2
0

4
.
2
0
33
7

2
.
0
0
0.
2
3
2

4
.
4
3
16
0

3
2
0

0
.
0
2
8

0
.
0
1
4

1
0
0
%
No
n
e
Pr
o
n
g
h
o
r
n
HI

-

I
n
o
r
g
a
n
i
c
s
22

3
.
5
(d
e
t
s
)
Pr
o
b
a
b
l
e
Pr
o
n
g
h
o
r
n

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
8
7

1
8
1
6.
2
4

6
.
2
4
97

2
.
0
0
0.
0
6
6
7

6
.
3
0
5.
0
3

5
0
.
3
1.
2
0.
1
2

1
4
%
Po
s
s
i
b
l
e
Pr
o
n
g
h
o
r
n

A
n
t
h
r
a
c
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
2
5
6

0
.
2
5
6
3.
7
0

2
.
0
0
0.
0
0
2
5
5

0
.
2
5
8
10
0
0

N
S
V

<
0
.
0
1
--
7%
No
n
e
Pr
o
n
g
h
o
r
n
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
1
1.
4
1

1
.
4
1
10
.
5

2
.
0
0
0.
0
0
7
2
2

1
.
4
2
11
0
1.
4
0.
1
4

0
%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

F
l
u
o
r
a
n
t
h
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
2
4
8

0
.
0
0
2
4
8
0.
1
4
4

2
.
0
0
0.
0
0
0
0
9
9
1

0
.
0
0
2
5
8
12
5

2
5
0

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Pr
o
n
g
h
o
r
n

F
l
u
o
r
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
6
0
10
9

1
0
9
18
.
5

2
.
0
0
0.
0
1
2
7

1
0
9
12
5

2
5
0

0
.
8
7

0
.
4
3

1
4
%
No
n
e
Pr
o
n
g
h
o
r
n

N
a
p
h
t
h
a
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
2
.
2

1
2
1
4.
1
7

4
.
1
7
9.
9
5

2
.
0
0
0.
0
0
6
8
4

4
.
1
8
50

1
5
0

0
.
0
8
4

0
.
0
2
8

2
5
%
No
n
e
Pr
o
n
g
h
o
r
n

P
h
e
n
a
n
t
h
r
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
3
.
2
0.
4
5
5

0
.
4
5
5
49
.
1

2
.
0
0
0.
0
3
3
8

0
.
4
8
8
17
5

3
5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
Pr
o
n
g
h
o
r
n
HI

-

P
A
H
s
2.
2
0.
5
9
(d
e
t
s
)
Po
s
s
i
b
l
e
Pr
o
n
g
h
o
r
n
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
1
6
9
0.
0
0
0
0
5
8
2

0
.
0
0
0
0
5
8
2
0.
0
0
0
4
7
5

2
.
0
0
0.
0
0
0
0
0
0
3
2
7

0
.
0
0
0
0
5
8
5
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
2
7
9

0
.
0
0
0
1
7
2
0.
0
0
0
0
0
5
9
1

0
.
0
0
0
0
0
5
9
1
0.
0
0
0
6
1
6

2
.
0
0
0.
0
0
0
0
0
0
4
2
4

0
.
0
0
0
0
0
6
3
4
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
2
4
5
0.
0
0
0
0
0
8
4
3

0
.
0
0
0
0
0
8
4
3
0.
0
0
0
6
9
2

2
.
0
0
0.
0
0
0
0
0
0
4
7
6

0
.
0
0
0
0
0
8
9
1
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
2
9
8

0
.
0
0
0
1
7
8
0.
0
0
0
0
0
6
1
1

0
.
0
0
0
0
0
6
1
1
0.
0
0
0
5
9
7

2
.
0
0
0.
0
0
0
0
0
0
4
1
1

0
.
0
0
0
0
0
6
5
3
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
6
1
6
0.
0
0
0
0
2
1
2

0
.
0
0
0
0
2
1
2
0.
0
0
0
4
7
9

2
.
0
0
0.
0
0
0
0
0
0
3
3
0

0
.
0
0
0
0
2
1
5
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
7
4
1
0.
0
0
0
2
5
5

0
.
0
0
0
2
5
5
0.
0
0
0
8
9
7

2
.
0
0
0.
0
0
0
0
0
0
6
1
7

0
.
0
0
0
2
5
5
2.
5

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
3
7
3
0.
0
0
0
1
2
8

0
.
0
0
0
1
2
8
0.
0
0
0
6
3
8

2
.
0
0
0.
0
0
0
0
0
0
4
3
9

0
.
0
0
0
1
2
9
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
4
6
0.
0
0
0
0
5
0
4

0
.
0
0
0
0
5
0
4
0.
0
0
0
5
8
5

2
.
0
0
0.
0
0
0
0
0
0
4
0
2

0
.
0
0
0
0
5
0
8
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
1
0.
0
0
0
0
1
4
5

0
.
0
0
0
0
1
4
5
0.
0
0
0
5
1
5

2
.
0
0
0.
0
0
0
0
0
0
3
5
4

0
.
0
0
0
0
1
4
8
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n

2
-
B
u
t
a
n
o
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
3
4
9
0.
0
1
2
0

0
.
0
1
2
0
0.
0
0
7
5
8

2
.
0
0
0.
0
0
0
0
0
5
2
1

0
.
0
1
2
0
10

5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
Pr
o
n
g
h
o
r
n
2-
H
e
x
a
n
o
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
4
6
8
0.
0
0
1
6
1

0
.
0
0
1
6
1
0.
0
0
2
8
1

2
.
0
0
0.
0
0
0
0
0
1
9
3

0
.
0
0
1
6
1
10

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
6
4
7
0.
0
0
2
2
3

0
.
0
0
2
2
3
0.
0
0
3
2
6

2
.
0
0
0.
0
0
0
0
0
2
2
4

0
.
0
0
2
2
3
25

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n

A
c
e
t
o
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

7
5
.
6

8
6
8
29
.
9

2
9
.
9
11
.
5

2
.
0
0
0.
0
0
7
9
0

2
9
.
9
10

5
0
3.
0
0.
6
0

3
2
%
Po
s
s
i
b
l
e
Pr
o
n
g
h
o
r
n

B
e
n
z
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
1
2
8
0.
0
0
0
4
3
9

0
.
0
0
0
4
3
9
0.
0
0
1
5
4

2
.
0
0
0.
0
0
0
0
0
1
0
6

0
.
0
0
0
4
4
0
0.
7

7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Pr
o
n
g
h
o
r
n
Br
o
m
o
f
o
r
m
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
4
6

0
.
0
0
0
1
5
0
0.
0
0
0
0
0
5
1
4

0
.
0
0
0
0
0
5
1
4
0.
0
0
0
4
3
2

2
.
0
0
0.
0
0
0
0
0
0
2
9
7

0
.
0
0
0
0
0
5
4
4
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
Br
o
m
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
1
8
2
0.
0
0
0
6
2
7

0
.
0
0
0
6
2
7
0.
0
0
0
9
1
7

2
.
0
0
0.
0
0
0
0
0
0
6
3
1

0
.
0
0
0
6
2
7
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
2
9

0
.
0
0
2
6
1
0.
0
0
0
0
8
9
7

0
.
0
0
0
0
8
9
7
0.
0
0
0
6
0
7

2
.
0
0
0.
0
0
0
0
0
0
4
1
8

0
.
0
0
0
0
9
0
1
16

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
7
5
2
0.
0
0
0
0
0
2
5
9

0
.
0
0
0
0
0
2
5
9
0.
0
0
0
5
6
0

2
.
0
0
0.
0
0
0
0
0
0
3
8
5

0
.
0
0
0
0
0
2
9
7
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
0
9
0.
0
0
0
0
7
1
7

0
.
0
0
0
0
7
1
7
0.
0
0
0
7
4
8

2
.
0
0
0.
0
0
0
0
0
0
5
1
4

0
.
0
0
0
0
7
2
2
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
f
o
r
m
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
8
7
3

0
.
0
0
0
3
9
9
0.
0
0
0
0
1
3
7

0
.
0
0
0
0
1
3
7
0.
0
0
0
4
5
7

2
.
0
0
0.
0
0
0
0
0
0
3
1
4

0
.
0
0
0
0
1
4
0
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
5
7
8
0.
0
0
0
1
9
9

0
.
0
0
0
1
9
9
0.
0
0
0
7
3
8

2
.
0
0
0.
0
0
0
0
0
0
5
0
8

0
.
0
0
0
1
9
9
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
5
2
8
0.
0
0
0
1
8
2

0
.
0
0
0
1
8
2
0.
0
0
0
4
9
7

2
.
0
0
0.
0
0
0
0
0
0
3
4
2

0
.
0
0
0
1
8
2
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
3
8
0
0.
0
0
0
1
3
1

0
.
0
0
0
1
3
1
0.
0
0
0
5
3
5

2
.
0
0
0.
0
0
0
0
0
0
3
6
8

0
.
0
0
0
1
3
1
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
Et
h
y
l
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
3
8
9
0.
0
0
0
0
0
1
3
4

0
.
0
0
0
0
0
1
3
4
0.
0
0
0
5
6
3

2
.
0
0
0.
0
0
0
0
0
0
3
8
7

0
.
0
0
0
0
0
1
7
2
97

2
9
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
m,
p
-
X
y
l
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
2
9
3
0.
0
0
0
1
0
1

0
.
0
0
0
1
0
1
0.
0
0
0
9
6
5

2
.
0
0
0.
0
0
0
0
0
0
6
6
4

0
.
0
0
0
1
0
2
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
1
0

0
.
0
0
6
0
1
0.
0
0
0
2
0
7

0
.
0
0
0
2
0
7
0.
0
0
1
4
6

2
.
0
0
0.
0
0
0
0
0
1
0
1

0
.
0
0
0
2
0
8
5.
8
5

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n

o
-
X
y
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
3
4

0
.
0
0
3
9
3
0.
0
0
0
1
3
5

0
.
0
0
0
1
3
5
0.
0
0
1
1
8

2
.
0
0
0.
0
0
0
0
0
0
8
0
9

0
.
0
0
0
1
3
6
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Pr
o
n
g
h
o
r
n
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
1
6
5
0.
0
0
0
0
5
6
9

0
.
0
0
0
0
5
6
9
0.
0
0
0
6
5
6

2
.
0
0
0.
0
0
0
0
0
0
4
5
1

0
.
0
0
0
0
5
7
3
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n

T
o
l
u
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
6
7
0
0.
0
0
2
3
0

0
.
0
0
2
3
0
0.
0
1
4
2

2
.
0
0
0.
0
0
0
0
0
9
7
7

0
.
0
0
2
3
1
52

5
2
0

<
0
.
0
1

<
0
.
0
1

2
3
%
No
n
e
Pr
o
n
g
h
o
r
n
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
3
8
0.
0
0
0
0
4
7
5

0
.
0
0
0
0
4
7
5
0.
0
0
0
5
5
2

2
.
0
0
0.
0
0
0
0
0
0
3
8
0

0
.
0
0
0
0
4
7
9
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
6
Pa
g
e

3

o
f

7
Ta
b
l
e

2
6
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b

/
d
a

)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n
fr
o
m

S
i
t
e

(k
g
/
k
g
-
b

/
d
a

)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r
Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r

F
a
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

S
o
i
l

EP
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b

/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n
Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Pr
o
n
g
h
o
r
n
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
4
0.
0
0
0
0
1
4
6

0
.
0
0
0
0
1
4
6
0.
0
0
0
5
1
9

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
1
4
9
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Pr
o
n
g
h
o
r
n
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

0
.
3
3
1

0
.
0
0
0
1
6
9
0.
0
0
0
0
0
5
8
1

0
.
0
0
0
0
0
5
8
1
0.
0
0
0
5
0
9

2
.
0
0
0.
0
0
0
0
0
0
3
5
0

0
.
0
0
0
0
0
6
1
6
0.
7

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
Vi
n
y
l

c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0
0
10
0

3
.
1
0

0
.
0
0
2
2
9
0.
0
0
0
0
7
8
7

0
.
0
0
0
0
7
8
7
0.
0
0
0
7
3
8

2
.
0
0
0.
0
0
0
0
0
0
5
0
8

0
.
0
0
0
0
7
9
2
0.
1
7

1
.
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n
HI

-

V
O
C
s
3.
0
0.
6
0
(d
e
t
s
)
Po
s
s
i
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
6

2
.
1
3
0.
5
3
2
0-
0
00
.
5
3
2
0.
0
8
0
0

1
3
0.
0
0
2
6
0

0
.
5
3
5
0.
0
4

0
.
2
13
2.
7
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
7
1

7
.
4
2
1.
8
6
0-
0
01
.
8
6
2.
0
0

1
3
0.
0
6
5
0

1
.
9
2
2

8

0
.
9
6

0
.
2
4

2
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
1
6

3
3
.
2
8.
3
0
0-
0
08
.
3
0
10
.
5

1
3
0.
3
4
1

8
.
6
4
28
4.
3
1.
1
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

H
M
X
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
3
1
3

2
.
5
4
0.
6
3
5
0-
0
00
.
6
3
5
8.
1
2

1
3
0.
2
6
4

0
.
8
9
9
1

5

0
.
9
0

0
.
1
8

3
1
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
RD
X
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
87
.
3
21
.
8
0-
0
0

2
1
.
8
1.
5
0

1
3
0.
0
4
8
8

2
1
.
9
22
0
11
1.
1
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Te
t
r
y
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
1

6
.
6
9
1.
6
7
0-
0
01
.
6
7
0.
2
3
0

1
3
0.
0
0
7
4
8

1
.
6
8
1.
3

6
.
2
1.
3
0.
2
7

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

E
n
e
r
g
e
t
i
c
s
1.
9
0.
4
2
(d
e
t
s
)
Po
s
s
i
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
n
t
i
m
o
n
y
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
0
1
6
2

1
.
0
9
0.
2
7
1
0-
0
00
.
2
7
1
67

1
3
2.
1
8

2
.
4
5
0.
0
5
9

0
.
6
4
42
3.
8
79
%
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

C
a
d
m
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
42
.
4
10
.
6
0-
0
0

1
0
.
6
7.
8
0

1
3
0.
2
5
3

1
0
.
8
0.
7
7

1
.
4
2
14
7.
6
44
%
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

C
o
p
p
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
48
.
2
12
0-
0
01
2
41
5
0

1
3
13
5

1
4
7
11
.
7

1
5
.
1
4
13
9.
7
85
%
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

L
e
a
d
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
14
7
0
36
7
0-
0
03
6
7
11
0
0
0

1
3
35
8

7
2
5
0.
9
2

4
.
7
79
0
15
0
83
%
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

M
o
l
y
b
d
e
n
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
9
5
3

4
.
7
0
1.
1
8
0-
0
01
.
1
8
4.
9
3

1
3
0.
1
6
0

1
.
3
4
0.
2
6

2
.
6
5.
1
0.
5
1

9
1
%
Po
s
s
i
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

N
i
t
r
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
0
0

1
2
.
8
3.
1
9
0-
0
03
.
1
9
12
.
8

1
3
0.
4
1
5

3
.
6
1
50
7

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
2
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

P
e
r
c
h
l
o
r
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
0
0

2
.
7
3
0.
6
8
2
0-
0
00
.
6
8
2
2.
7
3

1
3
0.
0
8
8
6

0
.
7
7
0
2.
5
9

2
5
.
9

0
.
3
0

0
.
0
3
0

5
0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Se
l
e
n
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
3.
0
2
0.
7
5
5
0-
0
00
.
7
5
5
5.
0
0

1
3
0.
1
6
2

0
.
9
1
7
0.
2

0
.
3
3
4.
6
2.
8
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

S
i
l
v
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
0
4

2
.
0
7
0.
5
1
8
0-
0
00
.
5
1
8
1.
0
1

1
3
0.
0
3
2
9

0
.
5
5
0
2.
3
8

2
3
.
8

0
.
2
3

0
.
0
2
3

8
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

Z
i
n
c
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
57
7
14
4
0-
0
01
4
4
33
7

1
3
11

1
5
5
16
0

3
2
0

0
.
9
7

0
.
4
8

1
0
0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

I
n
o
r
g
a
n
i
c
s
86
0

1
8
0
(d
e
t
s
)
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9

2
8
2
0
70
4
0-
0
07
0
4
97

1
3
3.
1
5

7
0
7
5.
0
3

5
0
.
3
14
0
14
14
%
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
4
2

8
.
9
5
2.
2
4
0-
0
02
.
2
4
3.
7
0

1
3
0.
1
2
0

2
.
3
6
10
0
0

N
S
V

<
0
.
0
1
--
7%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
5
9

1
6
.
7
4.
1
7
0-
0
04
.
1
7
10
.
5

1
3
0.
3
4
1

4
.
5
1
11
0
4.
5
0.
4
5

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
3
3

1
4
3.
4
9
0-
0
03
.
4
9
10
.
5

1
3
0.
3
4
1

3
.
8
3
11
0
3.
8
0.
3
8

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
6
0

2
7
.
3
6.
8
2
0-
0
06
.
8
2
10
.
5

1
3
0.
3
4
1

7
.
1
7
11
0
7.
2
0.
7
2

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
9
4

3
0
.
9
7.
7
2
0-
0
07
.
7
2
10
.
5

1
3
0.
3
4
1

8
.
0
6
11
0
8.
1
0.
8
1

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
6
0

2
7
.
3
6.
8
2
0-
0
06
.
8
2
10
.
5

1
3
0.
3
4
1

7
.
1
7
11
0
7.
2
0.
7
2

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
r
y
s
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
2
9

2
4
6.
0
1
0-
0
06
.
0
1
10
.
5

1
3
0.
3
4
1

6
.
3
5
11
0
6.
4
0.
6
4

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
3
1

2
4
.
3
6.
0
6
0-
0
06
.
0
6
10
.
5

1
3
0.
3
4
1

6
.
4
0
11
0
6.
4
0.
6
4

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

F
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
0
4

0
.
4
3
8
0.
1
0
9
0-
0
00
.
1
0
9
0.
1
4
4

1
3
0.
0
0
4
6
8

0
.
1
1
4
12
5

2
5
0

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

F
l
u
o
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

9
.
5
7

1
7
7
44
.
2
0-
0
0

4
4
.
2
18
.
5

1
3
0.
6
0
1

4
4
.
8
12
5

2
5
0

0
.
3
6

0
.
1
8

1
4
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
8
6

3
0
7.
5
1
0-
0
07
.
5
1
10
.
5

1
3
0.
3
4
1

7
.
8
5
11
0
7.
8
0.
7
8

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

N
a
p
h
t
h
a
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

4
.
4
0

4
3
.
8
10
.
9
0-
0
0

1
0
.
9
9.
9
5

1
3
0.
3
2
3

1
1
.
3
50

1
5
0

0
.
2
2

0
.
0
7
5

2
5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

P
h
e
n
a
n
t
h
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
7
2

8
4
.
4
21
.
1
0-
0
0

2
1
.
1
49
.
1

1
3
1.
5
9

2
2
.
7
17
5

3
5
0

0
.
1
3

0
.
0
6
5

1
8
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

P
A
H
s
14
0

1
4
(d
e
t
s
)
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

T
P
H
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

-

0

0

0

-

0
00
47
0
0
0

1
3
15
3
0

1
5
3
0
10
0
0

1
5
0
0
0
1.
5
0.
1
0

1
0
0
%
Po
s
s
i
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

P
e
t
r
o
l
e
u
m
0.
2
2

0
.
0
7
5
(d
e
t
s
)
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
5
.
1

1
7
6
0
43
9
0-
0
04
3
9
50

1
3
1.
6
2

4
4
0
0.
2
4

2
.
4
18
0
0
18
0
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
5
.
6

3
7
4
93
.
4
0-
0
0

9
3
.
4
10
.
5

1
3
0.
3
4
1

9
3
.
7
0.
2
4

2
.
4
39
0
39
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
2
.
6

3
4
2
85
.
6
0-
0
0

8
5
.
6
10
.
5

1
3
0.
3
4
1

8
5
.
9
0.
2
4

2
.
4
36
0
36
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

4
0
.
2

4
2
2
10
6
0-
0
01
0
6
10
.
5

1
3
0.
3
4
1

1
0
6
1.
6

3
.
2
66
33
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
6

3
7
8
94
.
5
0-
0
0

9
4
.
5
10
.
5

1
3
0.
3
4
1

9
4
.
8
1.
6

3
.
2
59
30
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
8

3
9
9
99
.
7
0-
0
0

9
9
.
7
10
.
5

1
3
0.
3
4
1

1
0
0
1.
6

3
.
2
63
31
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

5
.
9
3

2
9
7
74
.
1
0-
0
0

7
4
.
1
50

1
3
1.
6
2

7
5
.
8
0.
2
4

2
.
4
32
0
32
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
3

0
.
0
1
3
4
0.
0
0
3
3
5
0-
0
0

0
.
0
0
3
3
5
0.
0
0
0
4
7
5

1
3
0.
0
0
0
0
1
5
4

0
.
0
0
3
3
7
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
4

0
.
0
1
9
4
0.
0
0
4
8
4
0-
0
0

0
.
0
0
4
8
4
0.
0
0
0
6
1
6

1
3
0.
0
0
0
0
2
0
0

0
.
0
0
4
8
6
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
1

0
.
0
2
1
6
0.
0
0
5
3
9
0-
0
0

0
.
0
0
5
3
9
0.
0
0
0
6
9
2

1
3
0.
0
0
0
0
2
2
5

0
.
0
0
5
4
1
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
4

0
.
0
1
8
7
0.
0
0
4
6
8
0-
0
0

0
.
0
0
4
6
8
0.
0
0
0
5
9
7

1
3
0.
0
0
0
0
1
9
4

0
.
0
0
4
7
0
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
5

0
.
0
1
4
1
0.
0
0
3
5
4
0-
0
0

0
.
0
0
3
5
4
0.
0
0
0
4
7
9

1
3
0.
0
0
0
0
1
5
6

0
.
0
0
3
5
5
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
2
4
5
0.
0
0
6
1
2
0-
0
0

0
.
0
0
6
1
2
0.
0
0
0
8
9
7

1
3
0.
0
0
0
0
2
9
2

0
.
0
0
6
1
5
2.
5

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
7

0
.
0
1
7
7
0.
0
0
4
4
2
0-
0
0

0
.
0
0
4
4
2
0.
0
0
0
6
3
8

1
3
0.
0
0
0
0
2
0
7

0
.
0
0
4
4
4
10
0
0

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
1
6
8
0.
0
0
4
2
0
0-
0
0

0
.
0
0
4
2
0
0.
0
0
0
5
8
5

1
3
0.
0
0
0
0
1
9
0

0
.
0
0
4
2
1
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
1

0
.
0
1
5
5
0.
0
0
3
8
7
0-
0
0

0
.
0
0
3
8
7
0.
0
0
0
5
1
5

1
3
0.
0
0
0
0
1
6
7

0
.
0
0
3
8
8
50

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
-
B
u
t
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
5
.
4

0
.
1
9
2
0.
0
4
8
1
0-
0
0

0
.
0
4
8
1
0.
0
0
7
5
8

1
3
0.
0
0
0
2
4
6

0
.
0
4
8
3
10

5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
H
e
x
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
5

0
.
0
7
4
5
0.
0
1
8
6
0-
0
0

0
.
0
1
8
6
0.
0
0
2
8
1

1
3
0.
0
0
0
0
9
1
3

0
.
0
1
8
7
10

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
3

0
.
0
8
5
7
0.
0
2
1
4
0-
0
0

0
.
0
2
1
4
0.
0
0
3
2
6

1
3
0.
0
0
0
1
0
6

0
.
0
2
1
5
25

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
c
e
t
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
4
.
9

2
8
6
71
.
4
0-
0
0

7
1
.
4
11
.
5

1
3
0.
3
7
3

7
1
.
8
10

5
0
7.
2
1.
4
32
%
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

B
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
4
2
1
0.
0
1
0
5
0-
0
0

0
.
0
1
0
5
0.
0
0
1
5
4

1
3
0.
0
0
0
0
5
0
2

0
.
0
1
0
6
0.
7

7

0
.
0
1
5

<
0
.
0
1

1
4
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Br
o
m
o
f
o
r
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
2

0
.
0
1
3
5
0.
0
0
3
3
7
0-
0
0

0
.
0
0
3
3
7
0.
0
0
0
4
3
2

1
3
0.
0
0
0
0
1
4
0

0
.
0
0
3
3
8
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Br
o
m
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
3

0
.
0
2
4
1
0.
0
0
6
0
3
0-
0
0

0
.
0
0
6
0
3
0.
0
0
0
9
1
7

1
3
0.
0
0
0
0
2
9
8

0
.
0
0
6
0
6
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8

0
.
0
1
7
0
0.
0
0
4
2
6
0-
0
0

0
.
0
0
4
2
6
0.
0
0
0
6
0
7

1
3
0.
0
0
0
0
1
9
7

0
.
0
0
4
2
8
16

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
2
.
4

0
.
0
1
8
2
0.
0
0
4
5
4
0-
0
0

0
.
0
0
4
5
4
0.
0
0
0
5
6
0

1
3
0.
0
0
0
0
1
8
2

0
.
0
0
4
5
6
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
6

0
.
0
2
1
4
0.
0
0
5
3
4
0-
0
0

0
.
0
0
5
3
4
0.
0
0
0
7
4
8

1
3
0.
0
0
0
0
2
4
3

0
.
0
0
5
3
6
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
f
o
r
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0

0
.
0
1
3
7
0.
0
0
3
4
2
0-
0
0

0
.
0
0
3
4
2
0.
0
0
0
4
5
7

1
3
0.
0
0
0
0
1
4
8

0
.
0
0
3
4
4
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
2
0
2
0.
0
0
5
0
5
0-
0
0

0
.
0
0
5
0
5
0.
0
0
0
7
3
8

1
3
0.
0
0
0
0
2
4
0

0
.
0
0
5
0
7
15

4
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7

0
.
0
1
3
4
0.
0
0
3
3
5
0-
0
0

0
.
0
0
3
3
5
0.
0
0
0
4
9
7

1
3
0.
0
0
0
0
1
6
1

0
.
0
0
3
3
7
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
5

0
.
0
1
4
7
0.
0
0
3
6
7
0-
0
0

0
.
0
0
3
6
7
0.
0
0
0
5
3
5

1
3
0.
0
0
0
0
1
7
4

0
.
0
0
3
6
9
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Et
h
y
l
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
3
.
3

0
.
0
1
8
8
0.
0
0
4
6
9
0-
0
0

0
.
0
0
4
6
9
0.
0
0
0
5
6
3

1
3
0.
0
0
0
0
1
8
3

0
.
0
0
4
7
1
97

2
9
1

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
m,
p
-
X
y
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
5

0
.
0
2
7
5
0.
0
0
6
8
6
0-
0
0

0
.
0
0
6
8
6
0.
0
0
0
9
6
5

1
3
0.
0
0
0
0
3
1
4

0
.
0
0
6
9
0
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
1

0
.
0
4
1
2
0.
0
1
0
3
0-
0
0

0
.
0
1
0
3
0.
0
0
1
4
6

1
3
0.
0
0
0
0
4
7
6

0
.
0
1
0
3
5.
8
5

5
0

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

o
-
X
y
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
3

0
.
0
3
3
3
0.
0
0
8
3
4
0-
0
0

0
.
0
0
8
3
4
0.
0
0
1
1
8

1
3
0.
0
0
0
0
3
8
2

0
.
0
0
8
3
7
17
9

3
5
7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ph
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
6

3
0
1
75
.
2
0-
0
0

7
5
.
2
10
.
5

1
3
0.
3
4
1

7
5
.
5
17
.
1

N
S
V
4.
4
--
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
1
8
8
0.
0
0
4
7
0
0-
0
0

0
.
0
0
4
7
0
0.
0
0
0
6
5
6

1
3
0.
0
0
0
0
2
1
3

0
.
0
0
4
7
2
1.
4

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

T
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
9

0
.
3
9
7
0.
0
9
9
2
0-
0
0

0
.
0
9
9
2
0.
0
1
4
2

1
3
0.
0
0
0
4
6
2

0
.
0
9
9
7
52

5
2
0

<
0
.
0
1

<
0
.
0
1

2
3
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
1
5
8
0.
0
0
3
9
6
0-
0
0

0
.
0
0
3
9
6
0.
0
0
0
5
5
2

1
3
0.
0
0
0
0
1
8
0

0
.
0
0
3
9
8
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
6
Pa
g
e

4

o
f

7
Ta
b
l
e

2
6
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b

/
d
a

)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n
fr
o
m

S
i
t
e

(k
g
/
k
g
-
b

/
d
a

)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r
Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r

F
a
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

S
o
i
l

EP
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b

/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n
Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
1

0
.
0
1
5
6
0.
0
0
3
9
0
0-
0
0

0
.
0
0
3
9
0
0.
0
0
0
5
1
9

1
3
0.
0
0
0
0
1
6
9

0
.
0
0
3
9
1
45
.
2

N
S
V

<
0
.
0
1
--
5%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
2

0
.
0
1
5
9
0.
0
0
3
9
8
0-
0
0

0
.
0
0
3
9
8
0.
0
0
0
5
0
9

1
3
0.
0
0
0
0
1
6
6

0
.
0
0
3
9
9
0.
7

7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
4

0
.
0
2
1
0
0.
0
0
5
2
4
0-
0
0

0
.
0
0
5
2
4
0.
0
0
0
7
3
8

1
3
0.
0
0
0
0
2
4
0

0
.
0
0
5
2
7
0.
1
7

1
.
7

0
.
0
3
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

V
O
C
s
7.
2

1
.
4
(d
e
t
s
)
Pr
o
b
a
b
l
e
Co
y
o
t
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

1
.
0
5

2
.
1
1

0
.
0
0
5
9
5

0

-

0
0
0-
0
0

0
.
0
0
5
9
5
2.
0
0

2
.
8
0
0.
0
0
0
1
5
8

0
.
0
0
6
1
0
2

8

<
0
.
0
1

<
0
.
0
1

2
%
No
n
e
Co
y
o
t
e

H
M
X

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

2
.
1
3

1
7
.
3

0
.
0
4
8
9

0

-

0
0
0-
0
0

0
.
0
4
8
9
8.
1
2

2
.
8
0
0.
0
0
0
6
4
1

0
.
0
4
9
5
1

5

0
.
0
5
0

<
0
.
0
1

3
1
%
No
n
e
Co
y
o
t
e
HI

-

E
n
e
r
g
e
t
i
c
s
0.
0
5
3

0
.
0
1
1
(d
e
t
s
)
No
n
e
Co
y
o
t
e

A
n
t
i
m
o
n
y

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

1
.
0
0

6
7

0
.
1
8
9

0

-

0
0
0-
0
00
.
1
8
9
67

2
.
8
0
0.
0
0
5
3
0

0
.
1
9
4
0.
0
5
9

0
.
6
4
3.
3
0.
3
0

7
9
%
Po
s
s
i
b
l
e
Co
y
o
t
e

C
a
d
m
i
u
m

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
1.
8
1

0
.
0
0
5
1
2

0

-

0
0
0-
0
0

0
.
0
0
5
1
2
7.
8
0

2
.
8
0
0.
0
0
0
6
1
6

0
.
0
0
5
7
4
0.
7
7

1
.
4
2

<
0
.
0
1

<
0
.
0
1

4
4
%
No
n
e
Co
y
o
t
e

C
o
p
p
e
r

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
25
.
7

0
.
0
7
2
4

0

-

0
0
0-
0
0

0
.
0
7
2
4
41
5
0

2
.
8
0
0.
3
2
8

0
.
4
0
1
11
.
7

1
5
.
1
4

0
.
0
3
4

0
.
0
2
6

8
5
%
No
n
e
Co
y
o
t
e

L
e
a
d

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
66
.
1

0
.
1
8
7

0

-

0
0
0-
0
0

0
.
1
8
7
11
0
0
0

2
.
8
0
0.
8
7
0

1
.
0
6
0.
9
2

4
.
7
1.
2
0.
2
2

8
3
%
Po
s
s
i
b
l
e
Co
y
o
t
e

M
o
l
y
b
d
e
n
u
m

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

1
.
0
0

4
.
9
3

0
.
0
1
3
9

0

-

0
0
0-
0
0

0
.
0
1
3
9
4.
9
3

2
.
8
0
0.
0
0
0
3
9
0

0
.
0
1
4
3
0.
2
6

2
.
6

0
.
0
5
5

<
0
.
0
1

9
1
%
No
n
e
Co
y
o
t
e

N
i
t
r
a
t
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

1
.
0
0

1
2
.
8

0
.
0
3
6
1

0

-

0
0
0-
0
0

0
.
0
3
6
1
12
.
8

2
.
8
0
0.
0
0
1
0
1

0
.
0
3
7
1
50
7

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
2
%
No
n
e
Co
y
o
t
e

P
e
r
c
h
l
o
r
a
t
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0
.
1
0
0

0
.
2
7
3

0
.
0
0
0
7
7
0

0

-

0
0
0-
0
0

0
.
0
0
0
7
7
0
2.
7
3

2
.
8
0
0.
0
0
0
2
1
6

0
.
0
0
0
9
8
5
2.
5
9

2
5
.
9

<
0
.
0
1

<
0
.
0
1

5
0
%
No
n
e
Co
y
o
t
e

S
i
l
v
e
r

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0
.
8
1
0

0
.
8
2
0

0
.
0
0
2
3
1

0

-

0
0
0-
0
0

0
.
0
0
2
3
1
1.
0
1

2
.
8
0
0.
0
0
0
0
8
0
0

0
.
0
0
2
3
9
2.
3
8

2
3
.
8

<
0
.
0
1

<
0
.
0
1

8
%
No
n
e
Co
y
o
t
e

Z
i
n
c

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
13
4

0
.
3
7
9

0

-

0
0
0-
0
00
.
3
7
9
33
7

2
.
8
0
0.
0
2
6
6

0
.
4
0
6
16
0

3
2
0

<
0
.
0
1

<
0
.
0
1

1
0
0
%
No
n
e
Co
y
o
t
e
HI

-

I
n
o
r
g
a
n
i
c
s
4.
6
0.
5
7
(d
e
t
s
)
Po
s
s
i
b
l
e
Co
y
o
t
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0
.
6
2
9

6
1

0
.
1
7
2

0

-

0
0
0-
0
00
.
1
7
2
97

2
.
8
0
0.
0
0
7
6
6

0
.
1
8
0
5.
0
3

5
0
.
3

0
.
0
3
6

<
0
.
0
1

1
4
%
No
n
e
Co
y
o
t
e

A
n
t
h
r
a
c
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0
0
0-
0
00
3.
7
0

2
.
8
0
0.
0
0
0
2
9
2

0
.
0
0
0
2
9
2
10
0
0

N
S
V

<
0
.
0
1
--
7%
No
n
e
Co
y
o
t
e

F
l
u
o
r
a
n
t
h
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0
0
0-
0
00
0.
1
4
4

2
.
8
0
0.
0
0
0
0
1
1
4

0
.
0
0
0
0
1
1
4
12
5

2
5
0

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Co
y
o
t
e

F
l
u
o
r
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0
0
0-
0
00
18
.
5

2
.
8
0
0.
0
0
1
4
6

0
.
0
0
1
4
6
12
5

2
5
0

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Co
y
o
t
e

N
a
p
h
t
h
a
l
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0
0
0-
0
00
9.
9
5

2
.
8
0
0.
0
0
0
7
8
6

0
.
0
0
0
7
8
6
50

1
5
0

<
0
.
0
1

<
0
.
0
1

2
5
%
No
n
e
Co
y
o
t
e

P
h
e
n
a
n
t
h
r
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0
0
0-
0
00
49
.
1

2
.
8
0
0.
0
0
3
8
8

0
.
0
0
3
8
8
17
5

3
5
0

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
Co
y
o
t
e
HI

-

P
A
H
s
0.
0
3
6
<0
.
0
1

(
d
e
t
s
)
No
n
e
Co
y
o
t
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0
.
1
2
5

6
.
2
4

0
.
0
1
7
6

0

-

0
0
0-
0
0

0
.
0
1
7
6
50

2
.
8
0
0.
0
0
3
9
5

0
.
0
2
1
6
0.
2
4

2
.
4

0
.
0
9
0

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
7
1

2
.
5
6
0.
0
6
5
4

0
.
0
6
5
4
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
0
6
6
2
0.
0
7

1
.
8

0
.
9
5

0
.
0
3
7

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
1
4

3
3
0.
8
4
1

0
.
8
4
1
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
8
4
7
0.
0
7

1
.
8
12
0.
4
7

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
.
7
2
0.
0
6
9
4

0
.
0
6
9
4
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
0
7
0
1
0.
0
7

1
.
8
1.
0
0.
0
3
9

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Ni
t
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
1
3

1
1
.
9
0.
3
0
3

0
.
3
0
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
3
0
8
0.
0
7

1
.
8
4.
4
0.
1
7

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
RD
X
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
0.
9
6
0

0
.
9
6
0
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
9
6
1
0.
0
7

1
.
8
14
0.
5
3

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

C
a
d
m
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
9
1
0.
0
4
8
6

0
.
0
4
8
6
7.
8
0

2
.
0
0
0.
0
0
3
9
8

0
.
0
5
2
6
0.
1
6

0
.
6
1

0
.
3
3

0
.
0
8
6

4
4
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

C
o
p
p
e
r

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

5
2
1.
3
3

1
.
3
3
41
5
0

2
.
0
0
2.
1
2

3
.
4
5
47

6
1
.
7

0
.
0
7
3

0
.
0
5
6

8
5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

L
e
a
d

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
9
.
1
1.
2
5

1
.
2
5
11
0
0
0

2
.
0
0
5.
6
2

6
.
8
7
0.
1
9

1
.
7
8
36
3.
9
83
%
Pr
o
b
a
b
l
e
Sa
g
e

S
p
a
r
r
o
w

M
o
l
y
b
d
e
n
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
4
0
0

1
.
9
7
0.
0
5
0
4

0
.
0
5
0
4
4.
9
3

2
.
0
0
0.
0
0
2
5
2

0
.
0
5
2
9
3.
5

3
5
.
3

0
.
0
1
5

<
0
.
0
1

9
1
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

P
e
r
c
h
l
o
r
a
t
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
8
2

7
6
9
19
.
6

1
9
.
6
2.
7
3

2
.
0
0
0.
0
0
1
3
9

1
9
.
6
3.
2
6

3
2
.
6
6.
0
0.
6
0

5
0
%
Po
s
s
i
b
l
e
Sa
g
e

S
p
a
r
r
o
w

Z
i
n
c

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
2
3.
1
2

3
.
1
2
33
7

2
.
0
0
0.
1
7
2

3
.
2
9
14
.
5

1
3
1

0
.
2
3

0
.
0
2
5

1
0
0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
HI

-

I
n
o
r
g
a
n
i
c
s
43

4
.
6
(d
e
t
s
)
Pr
o
b
a
b
l
e
Sa
g
e

S
p
a
r
r
o
w

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
8
7

1
8
1
4.
6
3

4
.
6
3
97

2
.
0
0
0.
0
4
9
5

4
.
6
8
26
.
9

2
6
9

0
.
1
7

0
.
0
1
7

1
4
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

A
n
t
h
r
a
c
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

7
.
4
4
0.
1
9
0

0
.
1
9
0
3.
7
0

2
.
0
0
0.
0
0
1
8
9

0
.
1
9
2
32
5
.
2

N
S
V

<
0
.
0
1
--
7%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
5
0
0

0
.
0
7
2
0
0.
0
0
1
8
4

0
.
0
0
1
8
4
0.
1
4
4

2
.
0
0
0.
0
0
0
0
7
3
5

0
.
0
0
1
9
1
32
5
.
2

N
S
V

<
0
.
0
1
--
4%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

F
l
u
o
r
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
1
6
0
80
.
6

8
0
.
6
18
.
5

2
.
0
0
0.
0
0
9
4
3

8
0
.
6
32
5
.
2

N
S
V

0
.
2
5
--
14
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

N
a
p
h
t
h
a
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
2
.
2

1
2
1
3.
1
0

3
.
1
0
9.
9
5

2
.
0
0
0.
0
0
5
0
7

3
.
1
0
26
.
9

2
6
9

0
.
1
2

0
.
0
1
2

2
5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
3
.
2
0.
3
3
7

0
.
3
3
7
49
.
1

2
.
0
0
0.
0
2
5
0

0
.
3
6
2
32
5
.
2

N
S
V

<
0
.
0
1
--
18
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
HI

-

P
A
H
s
0.
5
4

0
.
0
2
9
(d
e
t
s
)
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
1
1

2
2
.
1
0.
5
6
5

0
.
5
6
5
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
5
7
0
0.
1
1

1
1
5.
2
0.
0
5
2

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
4
6
1

4
.
8
4
0.
1
2
3

0
.
1
2
3
10
.
5

2
.
0
0
0.
0
0
5
3
6

0
.
1
2
9
0.
1
1

1
1
1.
2
0.
0
1
2

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
5
6

0
.
0
0
1
6
9
0.
0
0
0
0
4
3
1

0
.
0
0
0
0
4
3
1
0.
0
0
0
4
7
5

2
.
0
0
0.
0
0
0
0
0
0
2
4
2

0
.
0
0
0
0
4
3
4
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
2
7
9

0
.
0
0
0
1
7
2
0.
0
0
0
0
0
4
3
9

0
.
0
0
0
0
0
4
3
9
0.
0
0
0
6
1
6

2
.
0
0
0.
0
0
0
0
0
0
3
1
4

0
.
0
0
0
0
0
4
7
0
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
3
5
4

0
.
0
0
0
2
4
5
0.
0
0
0
0
0
6
2
6

0
.
0
0
0
0
0
6
2
6
0.
0
0
0
6
9
2

2
.
0
0
0.
0
0
0
0
0
0
3
5
3

0
.
0
0
0
0
0
6
6
1
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
2
9
8

0
.
0
0
0
1
7
8
0.
0
0
0
0
0
4
5
4

0
.
0
0
0
0
0
4
5
4
0.
0
0
0
5
9
7

2
.
0
0
0.
0
0
0
0
0
0
3
0
5

0
.
0
0
0
0
0
4
8
4
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
2
8

0
.
0
0
0
6
1
6
0.
0
0
0
0
1
5
7

0
.
0
0
0
0
1
5
7
0.
0
0
0
4
7
9

2
.
0
0
0.
0
0
0
0
0
0
2
4
5

0
.
0
0
0
0
1
6
0
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
0
7
4
1
0.
0
0
0
1
8
9

0
.
0
0
0
1
8
9
0.
0
0
0
8
9
7

2
.
0
0
0.
0
0
0
0
0
0
4
5
8

0
.
0
0
0
1
9
0
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
.
3
7

0
.
0
0
0
9
9
6
0.
0
0
0
0
2
5
4

0
.
0
0
0
0
2
5
4
0.
0
0
0
7
2
5

2
.
0
0
0.
0
0
0
0
0
0
3
7
0

0
.
0
0
0
0
2
5
8
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

5
.
8
4

0
.
0
0
3
7
3
0.
0
0
0
0
9
5
2

0
.
0
0
0
0
9
5
2
0.
0
0
0
6
3
8

2
.
0
0
0.
0
0
0
0
0
0
3
2
6

0
.
0
0
0
0
9
5
5
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
0
5
8
0

0
.
0
0
0
0
1
8
5
0.
0
0
0
0
0
0
4
7
3

0
.
0
0
0
0
0
0
4
7
3
0.
0
0
3
2
0

2
.
0
0
0.
0
0
0
0
0
1
6
3

0
.
0
0
0
0
0
2
1
1
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
5
7

0
.
0
0
3
6
0
0.
0
0
0
0
9
1
8

0
.
0
0
0
0
9
1
8
0.
0
0
1
4
0

2
.
0
0
0.
0
0
0
0
0
0
7
1
4

0
.
0
0
0
0
9
2
5
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
4
6
0.
0
0
0
0
3
7
4

0
.
0
0
0
0
3
7
4
0.
0
0
0
5
8
5

2
.
0
0
0.
0
0
0
0
0
0
2
9
9

0
.
0
0
0
0
3
7
7
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
1
0.
0
0
0
0
1
0
7

0
.
0
0
0
0
1
0
7
0.
0
0
0
5
1
5

2
.
0
0
0.
0
0
0
0
0
0
2
6
3

0
.
0
0
0
0
1
1
0
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
4
9
8
0.
0
0
0
0
0
1
2
7

0
.
0
0
0
0
0
1
2
7
0.
0
0
1
9
0

2
.
0
0
0.
0
0
0
0
0
0
9
7
0

0
.
0
0
0
0
0
2
2
4
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
2
6
2

0
.
0
0
0
0
8
1
2
0.
0
0
0
0
0
2
0
7

0
.
0
0
0
0
0
2
0
7
0.
0
0
3
1
0

2
.
0
0
0.
0
0
0
0
0
1
5
8

0
.
0
0
0
0
0
3
6
5
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

2
-
B
u
t
a
n
o
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
6
.
1

0
.
3
4
9
0.
0
0
8
9
0

0
.
0
0
8
9
0
0.
0
0
7
5
8

2
.
0
0
0.
0
0
0
0
0
3
8
7

0
.
0
0
8
9
1
39
.
3

3
9
3

<
0
.
0
1

<
0
.
0
1

1
8
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
2-
H
e
x
a
n
o
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
6
.
6

0
.
0
4
6
8
0.
0
0
1
1
9

0
.
0
0
1
1
9
0.
0
0
2
8
1

2
.
0
0
0.
0
0
0
0
0
1
4
3

0
.
0
0
1
1
9
39
.
3

3
9
3

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
9
.
9

0
.
0
6
4
7
0.
0
0
1
6
5

0
.
0
0
1
6
5
0.
0
0
3
2
6

2
.
0
0
0.
0
0
0
0
0
1
6
6

0
.
0
0
1
6
5
39
.
3

3
9
3

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

A
c
e
t
o
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

7
5
.
6

8
6
8
22
.
1

2
2
.
1
11
.
5

2
.
0
0
0.
0
0
5
8
6

2
2
.
2
39
.
3

N
S
V

0
.
5
6
--
32
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

B
e
n
z
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

8
.
2
6

0
.
0
1
2
8
0.
0
0
0
3
2
5

0
.
0
0
0
3
2
5
0.
0
0
1
5
4

2
.
0
0
0.
0
0
0
0
0
0
7
8
8

0
.
0
0
0
3
2
6
10
.
2

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
1
3
4

0
.
0
0
0
0
7
5
2
0.
0
0
0
0
0
1
9
2

0
.
0
0
0
0
0
1
9
2
0.
0
0
0
5
6
0

2
.
0
0
0.
0
0
0
0
0
0
2
8
6

0
.
0
0
0
0
0
2
2
0
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
7
9

0
.
0
0
2
0
9
0.
0
0
0
0
5
3
2

0
.
0
0
0
0
5
3
2
0.
0
0
0
7
4
8

2
.
0
0
0.
0
0
0
0
0
0
3
8
2

0
.
0
0
0
0
5
3
6
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

7
.
8
3

0
.
0
0
5
7
8
0.
0
0
0
1
4
7

0
.
0
0
0
1
4
7
0.
0
0
0
7
3
8

2
.
0
0
0.
0
0
0
0
0
0
3
7
7

0
.
0
0
0
1
4
8
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
0
.
6

0
.
0
0
5
2
8
0.
0
0
0
1
3
5

0
.
0
0
0
1
3
5
0.
0
0
0
4
9
7

2
.
0
0
0.
0
0
0
0
0
0
2
5
4

0
.
0
0
0
1
3
5
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

7
.
1
1

0
.
0
0
3
8
0
0.
0
0
0
0
9
7
0

0
.
0
0
0
0
9
7
0
0.
0
0
0
5
3
5

2
.
0
0
0.
0
0
0
0
0
0
2
7
3

0
.
0
0
0
0
9
7
3
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
6
7
4

0
.
0
0
0
3
8
2
0.
0
0
0
0
0
9
7
5

0
.
0
0
0
0
0
9
7
5
0.
0
0
0
5
6
7

2
.
0
0
0.
0
0
0
0
0
0
2
8
9

0
.
0
0
0
0
1
0
0
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
b
r
o
m
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

1
3
.
3

0
.
0
0
5
8
7
0.
0
0
0
1
5
0

0
.
0
0
0
1
5
0
0.
0
0
0
4
4
2

2
.
0
0
0.
0
0
0
0
0
0
2
2
5

0
.
0
0
0
1
5
0
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
5
8
0

0
.
0
0
0
3
8
6
0.
0
0
0
0
0
9
8
4

0
.
0
0
0
0
0
9
8
4
0.
0
0
0
6
6
5

2
.
0
0
0.
0
0
0
0
0
0
3
3
9

0
.
0
0
0
0
1
0
2
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Et
h
y
l
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
0
6
9
0

0
.
0
0
0
0
3
8
9
0.
0
0
0
0
0
0
9
9
1

0
.
0
0
0
0
0
0
9
9
1
0.
0
0
0
5
6
3

2
.
0
0
0.
0
0
0
0
0
0
2
8
7

0
.
0
0
0
0
0
1
2
8
10
.
2

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
m,
p
-
X
y
l
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
0
4

0
.
0
0
2
9
3
0.
0
0
0
0
7
4
8

0
.
0
0
0
0
7
4
8
0.
0
0
0
9
6
5

2
.
0
0
0.
0
0
0
0
0
0
4
9
2

0
.
0
0
0
0
7
5
3
10
.
2

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

o
-
X
y
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

3
.
3
4

0
.
0
0
3
9
3
0.
0
0
0
1
0
0

0
.
0
0
0
1
0
0
0.
0
0
1
1
8

2
.
0
0
0.
0
0
0
0
0
0
6
0
0

0
.
0
0
0
1
0
1
10
.
2

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

1
4
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
5
2

0
.
0
0
1
6
5
0.
0
0
0
0
4
2
2

0
.
0
0
0
0
4
2
2
0.
0
0
0
6
5
6

2
.
0
0
0.
0
0
0
0
0
0
3
3
5

0
.
0
0
0
0
4
2
5
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
6
Pa
g
e

5

o
f

7
Ta
b
l
e

2
6
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b

/
d
a

)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n
fr
o
m

S
i
t
e

(k
g
/
k
g
-
b

/
d
a

)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r
Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r

F
a
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

S
o
i
l

EP
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b

/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n
Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Sa
g
e

S
p
a
r
r
o
w

T
o
l
u
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

4
.
7
1

0
.
0
6
7
0
0.
0
0
1
7
1

0
.
0
0
1
7
1
0.
0
1
4
2

2
.
0
0
0.
0
0
0
0
0
7
2
5

0
.
0
0
1
7
2
10
.
2

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

2
3
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

2
.
5
0

0
.
0
0
1
3
8
0.
0
0
0
0
3
5
3

0
.
0
0
0
0
3
5
3
0.
0
0
0
5
5
2

2
.
0
0
0.
0
0
0
0
0
0
2
8
2

0
.
0
0
0
0
3
5
6
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0
0
10
0

0
.
8
1
8

0
.
0
0
0
4
2
4
0.
0
0
0
0
1
0
8

0
.
0
0
0
0
1
0
8
0.
0
0
0
5
1
9

2
.
0
0
0.
0
0
0
0
0
0
2
6
5

0
.
0
0
0
0
1
1
1
17
.
2

3
4
.
4

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
HI

-

V
O
C
s
0.
5
6
<0
.
0
1

(
d
e
t
s
)
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
7
1

7
.
4
2
0.
1
6
6
0-
0
00
.
1
6
6
2.
0
0

0
0

0
.
1
6
6
0.
0
7

1
.
8
2.
4
0.
0
9
2

2
%
Po
s
s
i
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
1
6

3
3
.
2
0.
7
4
0
0-
0
00
.
7
4
0
10
.
5

0
0

0
.
7
4
0
0.
0
7

1
.
8
11
0.
4
1

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
6.
7
1
0.
1
5
0
0-
0
00
.
1
5
0
1.
5
0

0
0

0
.
1
5
0
0.
0
7

1
.
8
2.
1
0.
0
8
3

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
9

4
.
3
2
0.
0
9
6
5
0-
0
0

0
.
0
9
6
5
0.
1
4
0

0
00
.
0
9
6
5
0.
0
7

1
.
8
1.
4
0.
0
5
4

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
6

4
.
1
4
0.
0
9
2
4
0-
0
0

0
.
0
9
2
4
0.
1
5
0

0
00
.
0
9
2
4
0.
0
7

1
.
8
1.
3
0.
0
5
1

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
5

5
.
2
3
0.
1
1
7
0-
0
00
.
1
1
7
0.
1
9
0

0
0

0
.
1
1
7
0.
0
7

1
.
8
1.
7
0.
0
6
5

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

H
M
X

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
3
1
3

2
.
5
4
0.
0
5
6
7
0-
0
0

0
.
0
5
6
7
8.
1
2

0
0

0
.
0
5
6
7
9

6
2
.
5

<
0
.
0
1

<
0
.
0
1

3
1
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ni
t
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
7

3
1
1
6.
9
5
0-
0
06
.
9
5
10
.
5

0
06
.
9
5
0.
0
7

1
.
8
99
3.
9
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
RD
X
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
87
.
3
1.
9
5
0-
0
01
.
9
5
1.
5
0

0
01
.
9
5
0.
0
7

1
.
8
28
1.
1
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

E
n
e
r
g
e
t
i
c
s
2.
4
0.
0
9
3
(d
e
t
s
)
Po
s
s
i
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

C
a
d
m
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
42
.
4
0.
9
4
5
0-
0
00
.
9
4
5
7.
8
0

0
0

0
.
9
4
5
0.
1
6

0
.
6
1
5.
9
1.
6
44
%
Pr
o
b
a
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

C
o
p
p
e
r

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
48
.
2
1.
0
7
0-
0
01
.
0
7
41
5
0

0
01
.
0
7
47

6
1
.
7

0
.
0
2
3

0
.
0
1
7

8
5
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

L
e
a
d

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
14
7
0
32
.
8
0-
0
0

3
2
.
8
11
0
0
0

0
0

3
2
.
8
0.
1
9

1
.
7
8
17
0
18
83
%
Pr
o
b
a
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

M
o
l
y
b
d
e
n
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
9
5
3

4
.
7
0
0.
1
0
5
0-
0
00
.
1
0
5
4.
9
3

0
0

0
.
1
0
5
3.
5

3
5
.
3

0
.
0
3
0

<
0
.
0
1

9
1
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

P
e
r
c
h
l
o
r
a
t
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
0
0

2
.
7
3
0.
0
6
0
8
0-
0
0

0
.
0
6
0
8
2.
7
3

0
0

0
.
0
6
0
8
3.
2
6

3
2
.
6

0
.
0
1
9

<
0
.
0
1

5
0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

Z
i
n
c

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
57
7
12
.
9
0-
0
01
2
.
9
33
7

0
01
2
.
9
14
.
5

1
3
1

0
.
8
9

0
.
0
9
8

1
0
0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

I
n
o
r
g
a
n
i
c
s
18
0

2
0
(d
e
t
s
)
Pr
o
b
a
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9

2
8
2
0
62
.
8
0-
0
06
2
.
8
97

0
06
2
.
8
26
.
9

2
6
9
2.
3
0.
2
3

1
4
%
Po
s
s
i
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

A
n
t
h
r
a
c
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
4
2

8
.
9
5
0.
2
0
0
0-
0
00
.
2
0
0
3.
7
0

0
0

0
.
2
0
0
32
5
.
2

N
S
V

<
0
.
0
1
--
7%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
0
4

0
.
4
3
8
0.
0
0
9
7
6
0-
0
0

0
.
0
0
9
7
6
0.
1
4
4

0
0

0
.
0
0
9
7
6
32
5
.
2

N
S
V

<
0
.
0
1
--
4%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

F
l
u
o
r
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

9
.
5
7

1
7
7
3.
9
4
0-
0
03
.
9
4
18
.
5

0
03
.
9
4
32
5
.
2

N
S
V

0
.
0
1
2
--
14
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

N
a
p
h
t
h
a
l
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

4
.
4
0

4
3
.
8
0.
9
7
6
0-
0
00
.
9
7
6
9.
9
5

0
0

0
.
9
7
6
26
.
9

2
6
9

0
.
0
3
6

<
0
.
0
1

2
5
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
7
2

8
4
.
4
1.
8
8
0-
0
01
.
8
8
49
.
1

0
01
.
8
8
32
5
.
2

N
S
V

<
0
.
0
1
--
18
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

P
A
H
s
2.
4
0.
2
4
(d
e
t
s
)
Po
s
s
i
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
TP
H
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

-

0

0

0

-

0
00
47
0
0
0

0
00
50
0

5
0
0
0

<
0
.
0
1

<
0
.
0
1

1
0
0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

P
e
t
r
o
l
e
u
m
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
5
.
1

1
7
6
0
39
.
1
0-
0
0

3
9
.
1
50

0
03
9
.
1
16
.
9

3
8
.
4
2.
3
1.
0
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
3
.
4

5
0
.
1
1.
1
2
0-
0
01
.
1
2
1.
5
0

0
01
.
1
2
1.
1

N
S
V
--
18
%
Po
s
s
i
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8
.
8

4
0
8
9.
0
9
0-
0
09
.
0
9
10
.
5

0
09
.
0
9
0.
1
1

1
1
83
0.
8
3

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
3

3
2
9
7.
3
4
0-
0
07
.
3
4
10
.
5

0
07
.
3
4
0.
1
1

1
1
67
0.
6
7

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
9

3
0
3
6.
7
7
0-
0
06
.
7
7
10
.
5

0
06
.
7
7
0.
1
1

1
1
62
0.
6
2

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8

3
9
9
8.
9
1
0-
0
08
.
9
1
10
.
5

0
08
.
9
1
0.
1
1

1
1
81
0.
8
1

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
8

3
2
3
7.
2
1
0-
0
07
.
2
1
10
.
5

0
07
.
2
1
0.
1
1

1
1
66
0.
6
6

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

4
0
.
2

4
2
2
9.
4
2
0-
0
09
.
4
2
10
.
5

0
09
.
4
2
0.
5
6

2
.
2
5
17
4.
2
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8
.
6

0
.
0
3
0
9
0.
0
0
0
6
8
9
0-
0
0

0
.
0
0
0
6
8
9
0.
0
0
0
8
0
0

0
0

0
.
0
0
0
6
8
9
0.
5
6

2
.
2
5

<
0
.
0
1

<
0
.
0
1

4
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
6

3
7
8
8.
4
3
0-
0
08
.
4
3
10
.
5

0
08
.
4
3
0.
5
6

2
.
2
5
15
3.
8
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8

3
9
9
8.
9
0
0-
0
08
.
9
0
10
.
5

0
08
.
9
0
0.
5
6

2
.
2
5
16
4.
0
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

S
V
O
C
s
1.
0
0
(d
e
t
s
)
Po
s
s
i
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
7
1

7
.
4
2
0.
1
4
7
0-
0
00
.
1
4
7
2.
0
0

2
.
0
0
0.
0
0
0
7
9
3

0
.
1
4
8
0.
0
7

1
.
8
2.
1
0.
0
8
2

2
%
Po
s
s
i
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
1
6

3
3
.
2
0.
6
5
8
0-
0
00
.
6
5
8
10
.
5

2
.
0
0
0.
0
0
4
1
7

0
.
6
6
2
0.
0
7

1
.
8
9.
5
0.
3
7

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
6.
7
1
0.
1
3
3
0-
0
00
.
1
3
3
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

0
.
1
3
4
0.
0
7

1
.
8
1.
9
0.
0
7
4

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
0
.
9

4
.
3
2
0.
0
8
5
8
0-
0
0

0
.
0
8
5
8
0.
1
4
0

2
.
0
0
0.
0
0
0
0
5
5
5

0
.
0
8
5
8
0.
0
7

1
.
8
1.
2
0.
0
4
8

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
6

4
.
1
4
0.
0
8
2
2
0-
0
0

0
.
0
8
2
2
0.
1
5
0

2
.
0
0
0.
0
0
0
0
5
9
5

0
.
0
8
2
3
0.
0
7

1
.
8
1.
2
0.
0
4
6

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
5

5
.
2
3
0.
1
0
4
0-
0
00
.
1
0
4
0.
1
9
0

2
.
0
0
0.
0
0
0
0
7
5
4

0
.
1
0
4
0.
0
7

1
.
8
1.
5
0.
0
5
8

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

H
M
X

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
3
1
3

2
.
5
4
0.
0
5
0
4
0-
0
0

0
.
0
5
0
4
8.
1
2

2
.
0
0
0.
0
0
3
2
2

0
.
0
5
3
6
9

6
2
.
5

<
0
.
0
1

<
0
.
0
1

3
1
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Ni
t
r
o
b
e
n
z
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9
.
7

3
1
1
6.
1
8
0-
0
06
.
1
8
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
1
8
0.
0
7

1
.
8
88
3.
4
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
RD
X
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
87
.
3
1.
7
3
0-
0
01
.
7
3
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

1
.
7
3
0.
0
7

1
.
8
25
0.
9
6

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

E
n
e
r
g
e
t
i
c
s
2.
1
0.
0
8
3
(d
e
t
s
)
Po
s
s
i
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

C
a
d
m
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
42
.
4
0.
8
4
1
0-
0
00
.
8
4
1
7.
8
0

2
.
0
0
0.
0
0
3
0
9

0
.
8
4
4
0.
1
6

0
.
6
1
5.
3
1.
4
44
%
Pr
o
b
a
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

C
o
p
p
e
r

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
48
.
2
0.
9
5
5
0-
0
00
.
9
5
5
41
5
0

2
.
0
0
1.
6
5

2
.
6
0
47

6
1
.
7

0
.
0
5
5

0
.
0
4
2

8
5
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

L
e
a
d

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
14
7
0
29
.
1
0-
0
0

2
9
.
1
11
0
0
0

2
.
0
0
4.
3
7

3
3
.
5
0.
1
9

1
.
7
8
18
0
19
83
%
Pr
o
b
a
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

M
o
l
y
b
d
e
n
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
9
5
3

4
.
7
0
0.
0
9
3
3
0-
0
0

0
.
0
9
3
3
4.
9
3

2
.
0
0
0.
0
0
1
9
6

0
.
0
9
5
2
3.
5

3
5
.
3

0
.
0
2
7

<
0
.
0
1

9
1
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

P
e
r
c
h
l
o
r
a
t
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
0
0

2
.
7
3
0.
0
5
4
1
0-
0
0

0
.
0
5
4
1
2.
7
3

2
.
0
0
0.
0
0
1
0
8

0
.
0
5
5
2
3.
2
6

3
2
.
6

0
.
0
1
7

<
0
.
0
1

5
0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

Z
i
n
c

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
57
7
11
.
4
0-
0
01
1
.
4
33
7

2
.
0
0
0.
1
3
4

1
1
.
6
14
.
5

1
3
1

0
.
8
0

0
.
0
8
8

1
0
0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

I
n
o
r
g
a
n
i
c
s
18
0

2
0
(d
e
t
s
)
Pr
o
b
a
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9

2
8
2
0
55
.
9
0-
0
05
5
.
9
97

2
.
0
0
0.
0
3
8
5

5
5
.
9
26
.
9

2
6
9
2.
1
0.
2
1

1
4
%
Po
s
s
i
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

A
n
t
h
r
a
c
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
4
2

8
.
9
5
0.
1
7
8
0-
0
00
.
1
7
8
3.
7
0

2
.
0
0
0.
0
0
1
4
7

0
.
1
7
9
32
5
.
2

N
S
V

<
0
.
0
1
--
7%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

F
l
u
o
r
a
n
t
h
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
0
4

0
.
4
3
8
0.
0
0
8
6
8
0-
0
0

0
.
0
0
8
6
8
0.
1
4
4

2
.
0
0
0.
0
0
0
0
5
7
1

0
.
0
0
8
7
4
32
5
.
2

N
S
V

<
0
.
0
1
--
4%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

F
l
u
o
r
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

9
.
5
7

1
7
7
3.
5
1
0-
0
03
.
5
1
18
.
5

2
.
0
0
0.
0
0
7
3
3

3
.
5
2
32
5
.
2

N
S
V

0
.
0
1
1
--
14
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

N
a
p
h
t
h
a
l
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

4
.
4
0

4
3
.
8
0.
8
6
8
0-
0
00
.
8
6
8
9.
9
5

2
.
0
0
0.
0
0
3
9
5

0
.
8
7
2
26
.
9

2
6
9

0
.
0
3
2

<
0
.
0
1

2
5
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

P
h
e
n
a
n
t
h
r
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
7
2

8
4
.
4
1.
6
7
0-
0
01
.
6
7
49
.
1

2
.
0
0
0.
0
1
9
5

1
.
6
9
32
5
.
2

N
S
V

<
0
.
0
1
--
18
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

P
A
H
s
2.
1
0.
2
1
(d
e
t
s
)
Po
s
s
i
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
5
.
1

1
7
6
0
34
.
8
0-
0
0

3
4
.
8
50

2
.
0
0
0.
0
1
9
8

3
4
.
8
16
.
9

3
8
.
4
2.
1
0.
9
1

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8
.
8

4
0
8
8.
0
9
0-
0
08
.
0
9
10
.
5

2
.
0
0
0.
0
0
4
1
7

8
.
0
9
0.
1
1

1
1
74
0.
7
4

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
1
.
3

3
2
9
6.
5
3
0-
0
06
.
5
3
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
5
3
0.
1
1

1
1
59
0.
5
9

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
8
.
9

3
0
3
6.
0
2
0-
0
06
.
0
2
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
0
2
0.
1
1

1
1
55
0.
5
5

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8

3
9
9
7.
9
2
0-
0
07
.
9
2
10
.
5

2
.
0
0
0.
0
0
4
1
7

7
.
9
3
0.
1
1

1
1
72
0.
7
2

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
0
.
8

3
2
3
6.
4
1
0-
0
06
.
4
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

6
.
4
2
0.
1
1

1
1
58
0.
5
8

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

4
0
.
2

4
2
2
8.
3
8
0-
0
08
.
3
8
10
.
5

2
.
0
0
0.
0
0
4
1
7

8
.
3
8
0.
5
6

2
.
2
5
15
3.
7
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
6

3
7
8
7.
5
0
0-
0
07
.
5
0
10
.
5

2
.
0
0
0.
0
0
4
1
7

7
.
5
0
0.
5
6

2
.
2
5
13
3.
3
0%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8

3
9
9
7.
9
1
0-
0
07
.
9
1
10
.
5

2
.
0
0
0.
0
0
4
1
7

7
.
9
2
0.
5
6

2
.
2
5
14
3.
5
0%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
5

2
.
1
1

0
.
2
3
4

0

-

0
0
0-
0
0

0
.
2
3
4
2.
0
0

5
.
0
0
0.
0
1
1
1

0
.
2
4
5
0.
0
7

1
.
8
3.
5
0.
1
4

2
%
Po
s
s
i
b
l
e
Bu
r
r
o
w
i
n
g

O
w
l
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
0

1
1
.
5

1
.
2
8

0

-

0
0
0-
0
01
.
2
8
10
.
5

5
.
0
0
0.
0
5
8
3

1
.
3
4
0.
0
7

1
.
8
19
0.
7
4

0
%
Un
c
e
r
t
a
i
n
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
6
Pa
g
e

6

o
f

7
Ta
b
l
e

2
6
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b

/
d
a

)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n
fr
o
m

S
i
t
e

(k
g
/
k
g
-
b

/
d
a

)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r
Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

Tr
a
n
s
f
e
r

F
a
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

S
o
i
l

EP
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b

/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n
Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Bu
r
r
o
w
i
n
g

O
w
l
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
8

1
.
7
7

0
.
1
9
6

0

-

0
0
0-
0
00
.
1
9
6
1.
5
0

5
.
0
0
0.
0
0
8
3
3

0
.
2
0
5
0.
0
7

1
.
8
2.
9
0.
1
1

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

H
M
X

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

2
.
1
3

1
7
.
3

1
.
9
2

0

-

0
0
0-
0
01
.
9
2
8.
1
2

5
.
0
0
0.
0
4
5
1

1
.
9
7
9

6
2
.
5

0
.
2
2

0
.
0
3
2

3
1
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l
Ni
t
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
2
5

5
.
5
1

0
.
6
1
2

0

-

0
0
0-
0
00
.
6
1
2
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
6
7
1
0.
0
7

1
.
8
9.
6
0.
3
7

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

E
n
e
r
g
e
t
i
c
s
3.
7
0.
1
7
(d
e
t
s
)
Po
s
s
i
b
l
e
Bu
r
r
o
w
i
n
g

O
w
l

C
a
d
m
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
1.
8
1

0
.
2
0
1

0

-

0
0
0-
0
0

0
.
2
0
1
7.
8
0

5
.
0
0
0.
0
4
3
3

0
.
2
4
5
0.
1
6

0
.
6
1
1.
5
0.
4
0

4
4
%
Po
s
s
i
b
l
e
Bu
r
r
o
w
i
n
g

O
w
l

C
o
p
p
e
r

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
25
.
7

2
.
8
5

0

-

0
0
0-
0
02
.
8
5
41
5
0

5
.
0
0
23
.
1

2
5
.
9
47

6
1
.
7

0
.
5
5

0
.
4
2

8
5
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

L
e
a
d

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
66
.
1

7
.
3
4

0

-

0
0
0-
0
07
.
3
4
11
0
0
0

5
.
0
0
61
.
1

6
8
.
5
0.
1
9

1
.
7
8
36
0
39
83
%
Pr
o
b
a
b
l
e
Bu
r
r
o
w
i
n
g

O
w
l

M
o
l
y
b
d
e
n
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
0

4
.
9
3

0
.
5
4
8

0

-

0
0
0-
0
0

0
.
5
4
8
4.
9
3

5
.
0
0
0.
0
2
7
4

0
.
5
7
5
3.
5

3
5
.
3

0
.
1
6

0
.
0
1
6

9
1
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

P
e
r
c
h
l
o
r
a
t
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
0
0

0
.
2
7
3

0
.
0
3
0
3

0

-

0
0
0-
0
0

0
.
0
3
0
3
2.
7
3

5
.
0
0
0.
0
1
5
1

0
.
0
4
5
4
3.
2
6

3
2
.
6

0
.
0
1
4

<
0
.
0
1

5
0
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

Z
i
n
c

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0
egr
e
s
s
i
o
n

B
a
s
e
13
4

1
4
.
9

0

-

0
0
0-
0
01
4
.
9
33
7

5
.
0
0
1.
8
7

1
6
.
8
14
.
5

1
3
1
1.
2
0.
1
3

1
0
0
%
Po
s
s
i
b
l
e
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

I
n
o
r
g
a
n
i
c
s
36
4

3
9
.
4
(d
e
t
s
)
Pr
o
b
a
b
l
e
Bu
r
r
o
w
i
n
g

O
w
l
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
5
2
7

0
.
5
5
4

0
.
0
6
1
5

0

-

0
0
0-
0
0

0
.
0
6
1
5
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
2
0
0.
1
1

1
1
1.
0
9
0.
0
1
0
9

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
2
9

3
.
4
5

0
.
3
8
3

0

-

0
0
0-
0
00
.
3
8
3
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
4
4
2
0.
1
1

1
1
4.
0
2
0.
0
4
0
2

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
6
5
6

6
.
8
9

0
.
7
6
5

0

-

0
0
0-
0
00
.
7
6
5
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
8
2
4
0.
1
1

1
1
7.
4
9
0.
0
7
4
9

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
6
2
9

0
.
6
6
1

0
.
0
7
3
4

0

-

0
0
0-
0
0

0
.
0
7
3
4
10
.
5

5
.
0
0
0.
0
5
8
3

0
.
1
3
2
0.
1
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s
i
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
RD
X
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
4.
1
8

4
.
1
8
1.
5
0

2
.
0
0
0.
0
0
3
3
3

4
.
1
8
2.
0

2
0
2.
1
0.
2
1

0
%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

E
n
e
r
g
e
t
i
c
s
3.
3
0.
6
7
(d
e
t
s
)
Po
s
s
i
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
n
t
i
m
o
n
y

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
0
1
0
2

0
.
0
3
8
8
0.
0
0
4
3
0

0
.
0
0
4
3
0
3.
8
0

2
.
0
0

0
.
0
0
8
4
4

0
.
0
1
2
7

0
.
1

0
.
6
4

0
.
2
2

0
.
0
2
0

8
8
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

C
a
d
m
i
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
6
9
6
0.
0
7
7
3

0
.
0
7
7
3
1.
2
3

2
.
0
0

0
.
0
0
2
7
3

0
.
0
8
0
0

0
.
8

1
.
4
2

0
.
1
0

0
.
0
5
6

6
2
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

C
o
p
p
e
r

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
8
0.
7
5
3

0
.
7
5
3
23
.
6
0
0
0
0
0
0

2
.
0
0

0
.
0
5
2
4

0
.
8
0
6

1
1
.
7

1
5
.
1
4

0
.
0
6
9

0
.
0
5
3

9
5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

L
e
a
d

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
3
8
0.
1
5
4

0
.
1
5
4
19
.
0
0
0
0
0
0
0

2
.
0
0

0
.
0
4
2
2

0
.
1
9
6

0
.
9

4
.
7

0
.
2
1

0
.
0
4
2

9
5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

M
o
l
y
b
d
e
n
u
m

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
4
0
0

0
.
4
0
0
0.
0
4
4
4

0
.
0
4
4
4
1.
0
0

2
.
0
0

0
.
0
0
2
2
2

0
.
0
4
6
6

0
.
3

2
.
6

0
.
1
8

0
.
0
1
8

8
7
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

N
i
t
r
a
t
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

1

1
0
1.
1
1
0
5
6
4
9
6
5

1
.
1
1
0
5
6
4
9
6
5
10
.
0
0
0
0
0
0
0

2
.
0
0

0
.
0
2
2

1
.
1
3
3

5
0
7
.
0

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

P
e
r
c
h
l
o
r
a
t
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

2
8
2

1
5
.
1
0
1.
6
8

1
.
6
8
0.
0
5
3
7

2
.
0
0

0
.
0
0
0
1
1
9

1
.
6
8

2
.
6

2
5
.
9

0
.
6
5

0
.
0
6
5

3
3
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Se
l
e
n
i
u
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
3
3
3

0
.
3
3
3
5.
0
0

2
.
0
0

0
.
0
1
1
1

0
.
3
4
4

0
.
2

0
.
3
3
1.
7
1.
0
0%
Un
c
e
r
t
a
i
n
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

S
i
l
v
e
r

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
0
1
4
0

0
.
0
0
2
5
2
0.
0
0
0
2
8
0

0
.
0
0
0
2
8
0
0.
1
8
0

2
.
0
0

0
.
0
0
0
4
0
0

0
.
0
0
0
6
8
0

2
.
4

2
3
.
8

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

Z
i
n
c

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
7
.
2
5.
24
5.
24
60
.
8
0
0
0
0
0
0

2
.
0
0

0
.
1
3
5

5
.
3
8

1
6
0
.
0

3
2
0

0
.
0
3
4

0
.
0
1
7

1
0
0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

I
n
o
r
g
a
n
i
c
s
1.
5
0.
2
7
(d
e
t
s
)
Po
s
s
i
b
l
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

1
.
8
7

0
.
3
3
7
0.
0
3
7
4

0
.
0
3
7
4
0.
1
8
0

2
.
0
0
0.
0
0
0
4
0
0

0
.
0
3
7
8
5.
0

5
0
.
3

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
n
t
h
r
a
c
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
7
0
7
0.
0
7
8
6

0
.
0
7
8
6
0.
1
8
0

2
.
0
0
0.
0
0
0
4
0
0

0
.
0
7
9
0
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
2
0
0
0.
0
2
2
2

0
.
0
2
2
2
0.
1
8
0

2
.
0
0
0.
0
0
0
4
0
0

0
.
0
2
2
6
1.
0

1
0

0
.
0
2
3

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
3
3
4
0.
0
3
7
1

0
.
0
3
7
1
0.
1
8
0

2
.
0
0
0.
0
0
0
4
0
0

0
.
0
3
7
5
1.
0

1
0

0
.
0
3
8

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
2
6
8
0.
0
2
9
8

0
.
0
2
9
8
0.
1
8
0

2
.
0
0
0.
0
0
0
4
0
0

0
.
0
3
0
2
1.
0

1
0

0
.
0
3
0

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
5
0
0

0
.
0
5
3
5
0.
0
0
5
9
4

0
.
0
0
5
9
4
0.
1
0
7

2
.
0
0
0.
0
0
0
2
3
8

0
.
0
0
6
1
8
12
5
.
0

2
5
0

<
0
.
0
1

<
0
.
0
1

6
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

F
l
u
o
r
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
0
6.
6
7

6
.
6
7
0.
1
8
0

2
.
0
0
0.
0
0
0
4
0
0

6
.
6
7
12
5
.
0

2
5
0

0
.
0
5
3

0
.
0
2
7

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

N
a
p
h
t
h
a
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

1
2
.
2

2
.
2
0
0.
2
4
4

0
.
2
4
4
0.
1
8
0

2
.
0
0
0.
0
0
0
4
0
0

0
.
2
4
4
50
.
0

1
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
4
0
8
0.
0
4
5
3

0
.
0
4
5
3
0.
1
8
0

2
.
0
0
0.
0
0
0
4
0
0

0
.
0
4
5
7
17
5
.
0

3
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

P
A
H
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

3
.
5
6

0
.
0
0
2
6
7
0.
0
0
0
2
9
7

0
.
0
0
0
2
9
7
0.
0
0
0
7
5
0

2
.
0
0
0.
0
0
0
0
0
1
6
7

0
.
0
0
0
2
9
8
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
2
7
9

0
.
0
0
0
1
8
1
0.
0
0
0
0
2
0
2

0
.
0
0
0
0
2
0
2
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
1
4
4

0
.
0
0
0
0
2
1
6
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
3
5
4

0
.
0
0
0
2
4
8
0.
0
0
0
0
2
7
5

0
.
0
0
0
0
2
7
5
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
0
2
9
1
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
2
9
8

0
.
0
0
0
2
0
8
0.
0
0
0
0
2
3
1

0
.
0
0
0
0
2
3
1
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
0
2
4
7
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

1
.
2
8

0
.
0
0
0
5
7
8
0.
0
0
0
0
6
4
2

0
.
0
0
0
0
6
4
2
0.
0
0
0
4
5
0

2
.
0
0
0.
0
0
0
0
0
1
0
0
0

0
.
0
0
0
0
6
5
2
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
1
2
0
0.
0
0
1
3
3

0
.
0
0
1
3
3
0.
0
0
1
4
5

2
.
0
0
0.
0
0
0
0
0
3
2
2

0
.
0
0
1
3
3
2.
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

5
.
8
4

0
.
0
0
6
1
4
0.
0
0
0
6
8
2

0
.
0
0
0
6
8
2
0.
0
0
1
0
5

2
.
0
0
0.
0
0
0
0
0
2
3
3

0
.
0
0
0
6
8
4
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
1
9
5

0
.
0
0
0
1
9
5
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
1
9
6
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
4
5
0
0.
0
0
0
0
5
0
0

0
.
0
0
0
0
5
0
0
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
1
2
2

0
.
0
0
0
0
5
1
2
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

2
-
B
u
t
a
n
o
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

4
6
.
1

0
.
2
1
0
0.
0
2
3
3

0
.
0
2
3
3
0.
0
0
4
5
5

2
.
0
0
0.
0
0
0
0
1
0
1

0
.
0
2
3
3
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
2-
H
e
x
a
n
o
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

1
6
.
6

0
.
0
6
4
9
0.
0
0
7
2
1

0
.
0
0
7
2
1
0.
0
0
3
9
0

2
.
0
0
0.
0
0
0
0
0
8
6
6

0
.
0
0
7
2
2
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
6
7
6
0.
0
0
7
5
0

0
.
0
0
7
5
0
0.
0
0
3
4
0

2
.
0
0
0.
0
0
0
0
0
7
5
5

0
.
0
0
7
5
1
25
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

A
c
e
t
o
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

7
5
.
6

3
.
4
2
0.
3
8
0

0
.
3
8
0
0.
0
4
5
3

2
.
0
0
0.
0
0
0
1
0
1

0
.
3
8
0
10
.
0

5
0

0
.
0
3
8

<
0
.
0
1

1
3
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

B
e
n
z
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
0
4
7
1
0.
0
0
0
5
2
3

0
.
0
0
0
5
2
3
0.
0
0
0
5
7
0

2
.
0
0
0.
0
0
0
0
0
1
2
7

0
.
0
0
0
5
2
4
0.
7

7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Br
o
m
o
f
o
r
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
3
4
6

0
.
0
0
0
2
7
7
0.
0
0
0
0
3
0
8

0
.
0
0
0
0
3
0
8
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
1
7
8

0
.
0
0
0
0
3
2
5
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Br
o
m
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
1
9
9
0.
0
0
2
2
1

0
.
0
0
2
2
1
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
2
2
2

0
.
0
0
2
2
1
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

4
.
2
9

0
.
0
0
2
7
9
0.
0
0
0
3
1
0

0
.
0
0
0
3
1
0
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
1
4
4

0
.
0
0
0
3
1
1
16
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
1
3
4

0
.
0
0
0
0
8
0
5
0.
0
0
0
0
0
8
9
5

0
.
0
0
0
0
0
8
9
5
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
0
1
0
3
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

2
.
7
9

0
.
0
0
2
9
3
0.
0
0
0
3
2
5

0
.
0
0
0
3
2
5
0.
0
0
1
0
5

2
.
0
0
0.
0
0
0
0
0
2
3
3

0
.
0
0
0
3
2
8
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
f
o
r
m
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
8
7
3

0
.
0
0
0
5
2
4
0.
0
0
0
0
5
8
1

0
.
0
0
0
0
5
8
1
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
0
5
9
5
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
8
6
9

0
.
0
0
0
8
6
9
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
2
2
2

0
.
0
0
0
8
7
2
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

1
0
.
6

0
.
0
0
6
9
1
0.
0
0
0
7
6
7

0
.
0
0
0
7
6
7
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
1
4
4

0
.
0
0
0
7
6
9
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

7
.
1
1

0
.
0
0
3
9
1
0.
0
0
0
4
3
4

0
.
0
0
0
4
3
4
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
1
2
2

0
.
0
0
0
4
3
6
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Et
h
y
l
b
e
n
z
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
0
6
9
0

0
.
0
0
0
0
4
1
4
0.
0
0
0
0
0
4
6
0

0
.
0
0
0
0
0
4
6
0
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
0
0
5
9
3
97
.
0

2
9
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
m,
p
-
X
y
l
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

3
.
0
4

0
.
0
0
3
8
0
0.
0
0
0
4
2
2

0
.
0
0
0
4
2
2
0.
0
0
1
2
5

2
.
0
0
0.
0
0
0
0
0
2
7
8

0
.
0
0
0
4
2
5
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

4
.
1
0

0
.
0
0
6
5
6
0.
0
0
0
7
2
9

0
.
0
0
0
7
2
9
0.
0
0
1
6
0

2
.
0
0
0.
0
0
0
0
0
3
5
5

0
.
0
0
0
7
3
2
5.
9

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

o
-
X
y
l
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

3
.
3
4

0
.
0
0
3
6
0
0.
0
0
0
4
0
0

0
.
0
0
0
4
0
0
0.
0
0
1
0
8

2
.
0
0
0.
0
0
0
0
0
2
4
0

0
.
0
0
0
4
0
3
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

2
.
5
2

0
.
0
0
1
6
4
0.
0
0
0
1
8
2

0
.
0
0
0
1
8
2
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
1
4
4

0
.
0
0
0
1
8
3
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

T
o
l
u
e
n
e

0
.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

4
.
7
1

0
.
0
7
0
2
0.
0
0
7
8
0

0
.
0
0
7
8
0
0.
0
1
4
9

2
.
0
0
0.
0
0
0
0
3
3
1

0
.
0
0
7
8
3
52
.
0

5
2
0

<
0
.
0
1

<
0
.
0
1

1
3
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

2
.
5
0

0
.
0
0
1
5
0
0.
0
0
0
1
6
7

0
.
0
0
0
1
6
7
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
1
3
3

0
.
0
0
0
1
6
8
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
5
7
3
0.
0
0
0
0
6
3
6

0
.
0
0
0
0
6
3
6
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
1
5
5

0
.
0
0
0
0
6
5
1
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

0
.
3
3
1

0
.
0
0
0
1
8
2
0.
0
0
0
0
2
0
2

0
.
0
0
0
0
2
0
2
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
1
2
2

0
.
0
0
0
0
2
1
5
0.
7

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
0
5
2

0
.
1
1
1

1

0
.
1
1
1

0

-

0

0

0

-

0

0

1
0
0

3
.
1
0

0
.
0
0
2
6
4
0.
0
0
0
2
9
3

0
.
0
0
0
2
9
3
0.
0
0
0
8
5
0

2
.
0
0
0.
0
0
0
0
0
1
8
9

0
.
0
0
0
2
9
5
0.
2

1
.
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t
HI

-

V
O
C
s
0.
0
4
1
<0
.
0
1

(
d
e
t
s
)
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

1
5

1
.
2
0
0.
0
6
0
0

0
.
0
6
0
0
0.
0
8
0
0

2
.
0
0
0.
0
0
0
0
7
9
9

0
.
0
6
0
1
0.
0

0
.
2
1.
5
0.
3
0

0
%
Un
c
e
r
t
a
i
n
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
3
7
6

0
.
3
7
6
0.
0
1
8
8

0
.
0
1
8
8
1.
0
0

2
.
0
0
0.
0
0
0
9
9
9

0
.
0
1
9
8
2.
0

8

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

3
.
1
4

4
.
7
1
0.
2
3
5

0
.
2
3
5
1.
5
0

2
.
0
0
0.
0
0
1
5
0

0
.
2
3
7
2.
0

8

0
.
1
2

0
.
0
3
0

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

H
M
X

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
0
1.
5
0

1
.
5
0
3.
3
0

2
.
0
0
0.
0
0
3
3
0

1
.
5
0
1.
0

5
1.
5
0.
3
0

2
0
%
Po
s
s
i
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

E
n
e
r
g
e
t
i
c
s
1.
5
0.
3
0
(d
e
t
s
)
Po
s
s
i
b
l
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

A
n
t
i
m
o
n
y

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
0
1
0
2

0
.
0
3
8
8
0.
0
0
1
9
4

0
.
0
0
1
9
4
3.
8
0

2
.
0
0
0.
0
0
3
8
0

0
.
0
0
5
7
3
0.
1

0
.
6
4

0
.
0
9
7

<
0
.
0
1

8
8
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

C
a
d
m
i
u
m

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
6
9
6
0.
0
3
4
7

0
.
0
3
4
7
1.
2
3

2
.
0
0
0.
0
0
1
2
3

0
.
0
3
6
0
0.
8

1
.
4
2

0
.
0
4
7

0
.
0
2
5

6
2
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

C
o
p
p
e
r

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
8
0.
3
3
9

0
.
3
3
9
23
.
6
0
0
0
0
0
0

2
.
0
0
0.
0
2
3
6

0
.
3
6
2
11
.
7

1
5
.
1
4

0
.
0
3
1

0
.
0
2
4

9
5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

L
e
a
d

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
3
8
0.
0
6
9
1

0
.
0
6
9
1
19
.
0
0
0
0
0
0
0

2
.
0
0
0.
0
1
9
0

0
.
0
8
8
0
0.
9

4
.
7

0
.
0
9
6

0
.
0
1
9

9
5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

M
o
l
y
b
d
e
n
u
m

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
4
0
0

0
.
4
0
0
0.
0
2
0
0

0
.
0
2
0
0
1.
0
0

2
.
0
0
0.
0
0
0
9
9
9

0
.
0
2
1
0
0.
3

2
.
6

0
.
0
8
1

<
0
.
0
1

8
7
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

N
i
t
r
a
t
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

1

1
0
0.
4
9
9
5
0
5
5
0
8

0
.
4
9
9
5
0
5
5
0
8
10
.
0
0
0
0
0
0
0

2
.
0
0
0.
0
1
0
0

0
.
5
0
9
50
7
.
0

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

P
e
r
c
h
l
o
r
a
t
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

2
8
2

1
5
.
1
0
0.
7
5
6

0
.
7
5
6
0.
0
5
3
7

2
.
0
0
0.
0
0
0
0
5
3
6

0
.
7
5
6
2.
6

2
5
.
9

0
.
2
9

0
.
0
2
9

3
3
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

S
i
l
v
e
r

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
0
1
4
0

0
.
0
0
2
5
2
0.
0
0
0
1
2
6

0
.
0
0
0
1
2
6
0.
1
8
0

2
.
0
0
0.
0
0
0
1
8
0

0
.
0
0
0
3
0
6
2.
4

2
3
.
8

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

Z
i
n
c

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
7
.
2
2.36
2.36
60
.
8
0
0
0
0
0
0

2
.
0
0
0.
0
6
0
7

2
.
4
2
16
0
.
0

3
2
0

0
.
0
1
5

<
0
.
0
1

1
0
0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

I
n
o
r
g
a
n
i
c
s
0.
6
6

0
.
1
2
(d
e
t
s
)
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

1
.
8
7

0
.
3
3
7
0.
0
1
6
8

0
.
0
1
6
8
0.
1
8
0

2
.
0
0
0.
0
0
0
1
8
0

0
.
0
1
7
0
5.
0

5
0
.
3

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

A
n
t
h
r
a
c
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
7
0
7
0.
0
3
5
3

0
.
0
3
5
3
0.
1
8
0

2
.
0
0
0.
0
0
0
1
8
0

0
.
0
3
5
5
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
3
3
4
0.
0
1
6
7

0
.
0
1
6
7
0.
1
8
0

2
.
0
0
0.
0
0
0
1
8
0

0
.
0
1
6
9
1.
0

1
0

0
.
0
1
7

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

F
l
u
o
r
a
n
t
h
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
5
0
0

0
.
0
5
3
5
0.
0
0
2
6
7

0
.
0
0
2
6
7
0.
1
0
7

2
.
0
0
0.
0
0
0
1
0
7

0
.
0
0
2
7
8
12
5
.
0

2
5
0

<
0
.
0
1

<
0
.
0
1

6
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

F
l
u
o
r
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
0
3.
0
0

3
.
0
0
0.
1
8
0

2
.
0
0
0.
0
0
0
1
8
0

3
.
0
0
12
5
.
0

2
5
0

0
.
0
2
4

0
.
0
1
2

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

N
a
p
h
t
h
a
l
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

1
2
.
2

2
.
2
0
0.
1
1
0

0
.
1
1
0
0.
1
8
0

2
.
0
0
0.
0
0
0
1
8
0

0
.
1
1
0
50
.
0

1
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
ve
r
t
e
b
r
a
t
e
s
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
7
Pa
g
e

1

o
f

7
Ta
b
l
e

2
7
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s

W
i
t
h
i
n

H
a
b
i
t
a
t

A
r
e
a
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

H
a
b
i
t
a
t

So
i
l

E
P
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

P
h
e
n
a
n
t
h
r
e
n
e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
4
0
8
0.
0
2
0
4

0
.
0
2
0
4
0.
1
8
0

2
.
0
0
0.
0
0
0
1
8
0

0
.
0
2
0
5
17
5
.
0

3
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
HI

-

P
A
H
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

3
.
5
6

0
.
0
0
2
6
7
0.
0
0
0
1
3
3

0
.
0
0
0
1
3
3
0.
0
0
0
7
5
0

2
.
0
0
0.
0
0
0
0
0
0
7
4
9

0
.
0
0
0
1
3
4
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
2
7
9

0
.
0
0
0
1
8
1
0.
0
0
0
0
0
9
0
6

0
.
0
0
0
0
0
9
0
6
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
6
4
9

0
.
0
0
0
0
0
9
7
1
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
3
5
4

0
.
0
0
0
2
4
8
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0
0
0
0
1
2
4

0
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0
0
0
0
1
2
4
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
9
9

0
.
0
0
0
0
1
3
1
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
1,
1
,
2
-
T
r
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c
h
l
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r
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e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
2
9
8

0
.
0
0
0
2
0
8
0.
0
0
0
0
1
0
4

0
.
0
0
0
0
1
0
4
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
9
9

0
.
0
0
0
0
1
1
1
10
0
0
.
0

N
S
V

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0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l
1,
1
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D
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c
h
l
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t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

1
.
2
8

0
.
0
0
0
5
7
8
0.
0
0
0
0
2
8
9

0
.
0
0
0
0
2
8
9
0.
0
0
0
4
5
0

2
.
0
0
0.
0
0
0
0
0
0
4
5
0

0
.
0
0
0
0
2
9
3
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l
1,
1
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D
i
c
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e
t
h
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e
0.
3
2
5

0
.
0
5
0

1

0
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0
5
0

0

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0

0

0

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0

0

1
0
0

8
.
2
6

0
.
0
1
2
0
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0
0
0
5
9
8

0
.
0
0
0
5
9
8
0.
0
0
1
4
5

2
.
0
0
0.
0
0
0
0
0
1
4
5

0
.
0
0
0
6
0
0
2.
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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l
1,
2
,
3
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T
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e
0.
3
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5

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1

0
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0
5
0

0

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0

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1
0
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5
.
8
4

0
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0
0
6
1
4
0.
0
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3
0
7

0
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0
0
0
3
0
7
0.
0
0
1
0
5

2
.
0
0
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0
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5

0
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0
0
0
3
0
8
10
0
0
.
0

N
S
V

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0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l
1,
2
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D
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0.
3
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5

0
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0
5
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1

0
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0
5
0

0

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0

0

0

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0

1
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0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
0
8
7
5

0
.
0
0
0
0
8
7
5
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
9
9

0
.
0
0
0
0
8
8
2
50
.
0

N
S
V

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0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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1,
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i
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p
r
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p
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e
0.
3
2
5

0
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0
5
0

1

0
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0
5
0

0

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0

0

0

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0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
4
5
0
0.
0
0
0
0
2
2
5

0
.
0
0
0
0
2
2
5
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
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5
4
9

0
.
0
0
0
0
2
3
0
50
.
0

N
S
V

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0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l

2
-
B
u
t
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e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

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0

0

1
0
0

4
6
.
1

0
.
2
1
0
0.
0
1
0
5

0
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0
1
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5
0.
0
0
4
5
5

2
.
0
0
0.
0
0
0
0
0
4
5
5

0
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0
1
0
5
10
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0

5
0

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0
.
0
1

<
0
.
0
1

7
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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l
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H
e
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a
n
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e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

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0

0

0

-

0

0

1
0
0

1
6
.
6

0
.
0
6
4
9
0.
0
0
3
2
4

0
.
0
0
3
2
4
0.
0
0
3
9
0

2
.
0
0
0.
0
0
0
0
0
3
9
0

0
.
0
0
3
2
5
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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e
l
4-
M
e
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h
y
l
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2
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p
e
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t
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n
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n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
6
7
6
0.
0
0
3
3
7

0
.
0
0
3
3
7
0.
0
0
3
4
0

2
.
0
0
0.
0
0
0
0
0
3
4
0

0
.
0
0
3
3
8
25
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l

A
c
e
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o
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e

0
.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

7
5
.
6

3
.
4
2
0.
1
7
1

0
.
1
7
1
0.
0
4
5
3

2
.
0
0
0.
0
0
0
0
4
5
2

0
.
1
7
1
10
.
0

5
0

0
.
0
1
7

<
0
.
0
1

1
3
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l

B
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e
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e

0
.
3
2
5

0
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0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
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4
7
1
0.
0
0
0
2
3
5

0
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0
0
0
2
3
5
0.
0
0
0
5
7
0

2
.
0
0
0.
0
0
0
0
0
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5
6
9

0
.
0
0
0
2
3
6
0.
7

7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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Br
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m
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f
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m
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
3
4
6

0
.
0
0
0
2
7
7
0.
0
0
0
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1
3
8

0
.
0
0
0
0
1
3
8
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
7
9
9

0
.
0
0
0
0
1
4
6
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
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l
Br
o
m
o
m
e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
1
9
9
0.
0
0
0
9
9
3

0
.
0
0
0
9
9
3
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
9
9
9

0
.
0
0
0
9
9
4
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
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d
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

4
.
2
9

0
.
0
0
2
7
9
0.
0
0
0
1
3
9

0
.
0
0
0
1
3
9
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
6
4
9

0
.
0
0
0
1
4
0
16
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

0
.
1
3
4

0
.
0
0
0
0
8
0
5
0.
0
0
0
0
0
4
0
2

0
.
0
0
0
0
0
4
0
2
0.
0
0
0
6
0
0

2
.
0
0
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0
0
0
0
0
0
5
9
9

0
.
0
0
0
0
0
4
6
2
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
Ch
l
o
r
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e
t
h
a
n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

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0

0

1
0
0

2
.
7
9

0
.
0
0
2
9
3
0.
0
0
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1
4
6

0
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0
0
0
1
4
6
0.
0
0
1
0
5

2
.
0
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0
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0
5

0
.
0
0
0
1
4
7
15
.
0

4
1

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0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l
Ch
l
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f
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m
0.
3
2
5

0
.
0
5
0

1

0
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0
5
0

0

-

0

0

0

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0

0

1
0
0

0
.
8
7
3

0
.
0
0
0
5
2
4
0.
0
0
0
0
2
6
2

0
.
0
0
0
0
2
6
2
0.
0
0
0
6
0
0

2
.
0
0
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0
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0
0
0
0
5
9
9

0
.
0
0
0
0
2
6
8
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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e
l
Ch
l
o
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o
m
e
t
h
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n
e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

-

0

0

1
0
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
3
9
1

0
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0
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0
3
9
1
0.
0
0
1
0
0

2
.
0
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0.
0
0
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0
0
9
9
9

0
.
0
0
0
3
9
2
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l
ci
s
-
1
,
2
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D
i
c
h
l
o
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e
t
h
e
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e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

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0

0

1
0
0

1
0
.
6

0
.
0
0
6
9
1
0.
0
0
0
3
4
5

0
.
0
0
0
3
4
5
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
6
4
9

0
.
0
0
0
3
4
6
45
.
2

N
S
V

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0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l
ci
s
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1
,
3
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D
i
c
h
l
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p
r
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e
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e
0.
3
2
5

0
.
0
5
0

1

0
.
0
5
0

0

-

0

0

0

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0

0

1
0
0

7
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1
1

0
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0
0
3
9
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0
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9
5

0
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0
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9
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0
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5
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2
.
0
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0
0
0
0
0
0
5
4
9

0
.
0
0
0
1
9
6
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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3
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5

0
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0
5
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1

0
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0
5
0

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0

1
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0
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9
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0
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1
4
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0
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0
7

0
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0
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0
7
0.
0
0
0
6
0
0

2
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0
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0
5
9
9

0
.
0
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0
2
6
7
97
.
0

2
9
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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e
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3
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5

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0
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0
5
0

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-

0

0

0

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0

1
0
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3
.
0
4

0
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0
0
3
8
0
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0
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1
9
0

0
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0
0
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1
9
0
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0
0
1
2
5

2
.
0
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0
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0
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0
1
2
5

0
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0
0
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1
9
1
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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t
h
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e

c
h
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e
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3
2
5

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0
5
0

1

0
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0
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1
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4
.
1
0

0
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0
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6
5
6
0.
0
0
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3
2
8

0
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0
0
0
3
2
8
0.
0
0
1
6
0

2
.
0
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0
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0
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1
6
0

0
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3
2
9
5.
9

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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r
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e

0
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3
2
5

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0
5
0

1

0
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0
5
0

0

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0

0

0

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1
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3
.
3
4

0
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0
0
3
6
0
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0
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1
8
0

0
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0
0
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8
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0
0
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0
8

2
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0
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0
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8

0
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1
8
1
17
9
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0

3
5
7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
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t
r
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h
l
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e
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e
n
e
0.
3
2
5

0
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0
5
0

1

0
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0
5
0

0

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1
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2
.
5
2

0
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0
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1
6
4
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0
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0
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1
9

0
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0
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8
1
9
0.
0
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6
5
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2
.
0
0
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0
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0
0
6
4
9

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2
5
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l

T
o
l
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e
n
e

0
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3
2
5

0
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0
5
0

1

0
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0
5
0

0

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0

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0

1
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4
.
7
1

0
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0
7
0
2
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0
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3
5
1

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5
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1
4
9

2
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0
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0
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0
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1
4
9

0
.
0
0
3
5
2
52
.
0

5
2
0

<
0
.
0
1

<
0
.
0
1

1
3
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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e
l
Tr
a
n
s
-
1
,
2
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D
i
c
h
l
o
r
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e
t
h
e
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e
0.
3
2
5

0
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0
5
0

1

0
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0
5
0

0

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0

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0

1
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2
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5
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0
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5
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0
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7
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0
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6
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2
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0
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0
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0
5
9
9

0
.
0
0
0
0
7
5
6
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
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l
Tr
a
n
s
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1
,
3
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0.
3
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5

0
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0
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0
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0
5
0

0

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8
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8

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6

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7
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2
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0
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0
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6
9
9

0
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0
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2
9
3
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
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c
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(
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)
0.
3
2
5

0
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5
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1

0
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0
5
0

0

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0

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1
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3
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0
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8
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0
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1

0
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9
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0
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5
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2
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9

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6
5
0.
7

7

<
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.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
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l
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n
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c
h
l
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3
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5

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1

0
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0
5
0

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0

0

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0

1
0
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3
.
1
0

0
.
0
0
2
6
4
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0
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0
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0
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8
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2
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0
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8
4
9

0
.
0
0
0
1
3
3
0.
2

1
.
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
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l
HI

-

V
O
C
s
0.
0
1
8
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.
0
1

(
d
e
t
s
)
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1
5

1
.
2
0
0.
0
8
5
8

0
.
0
8
5
8
0.
0
8
0
0

6
.
3
0
0.
0
0
0
3
6
0

0
.
0
8
6
2
0.
0

0
.
2
2.
2
0.
4
3

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
3
7
6

0
.
3
7
6
0.
0
2
6
9

0
.
0
2
6
9
1.
0
0

6
.
3
0
0.
0
0
4
5
0

0
.
0
3
1
4
2.
0

8

0
.
0
1
6

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

3
.
1
4

4
.
7
1
0.
3
3
7

0
.
3
3
7
1.
5
0

6
.
3
0
0.
0
0
6
7
5

0
.
3
4
3
2.
0

8

0
.
1
7

0
.
0
4
3

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

H
M
X

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
0
2.
1
4

2
.
1
4
3.
3
0

6
.
3
0
0.
0
1
4
9

2
.
1
6
1.
0

5
2.
2
0.
4
3

2
0
%
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
RD
X
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
2.
6
9

2
.
6
9
1.
5
0

6
.
3
0
0.
0
0
6
7
5

2
.
6
9
2.
0

2
0
1.
4
0.
1
4

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

E
n
e
r
g
e
t
i
c
s
2.
2
0.
4
3
(d
e
t
s
)
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
n
t
i
m
o
n
y

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
0
1
0
2

0
.
0
3
8
8
0.
0
0
2
7
7

0
.
0
0
2
7
7
3.
8
0

6
.
3
0
0.
0
1
7
1

0
.
0
1
9
9
0.
1

0
.
6
4

0
.
3
4

0
.
0
3
1

8
8
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

C
a
d
m
i
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
6
9
6
0.
0
4
9
7

0
.
0
4
9
7
1.
2
3

6
.
3
0
0.
0
0
5
5
4

0
.
0
5
5
2
0.
8

1
.
4
2

0
.
0
7
2

0
.
0
3
9

6
2
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

C
o
p
p
e
r

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
8
0.
4
8
5

0
.
4
8
5
23
.
6
0
0
0
0
0
0

6
.
3
0
0.
1
0
6

0
.
5
9
1
11
.
7

1
5
.
1
4

0
.
0
5
0

0
.
0
3
9

9
5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

L
e
a
d

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
3
8
0.
0
9
8
8

0
.
0
9
8
8
19
.
0
0
0
0
0
0
0

6
.
3
0
0.
0
8
5
5

0
.
1
8
4
0.
9

4
.
7

0
.
2
0

0
.
0
3
9

9
5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

M
o
l
y
b
d
e
n
u
m

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
4
0
0

0
.
4
0
0
0.
0
2
8
6

0
.
0
2
8
6
1.
0
0

6
.
3
0
0.
0
0
4
5
0

0
.
0
3
3
1
0.
3

2
.
6

0
.
1
3

0
.
0
1
3

8
7
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

N
i
t
r
a
t
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1

1
0
0.
7
1
4
5
6
5
7
3
3

0
.
7
1
4
5
6
5
7
3
3
10
.
0
0
0
0
0
0
0

6
.
3
0
0.
0
4
5

0
.
7
6
0
50
7
.
0

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

P
e
r
c
h
l
o
r
a
t
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

2
8
2

1
5
.
1
0
1.
0
8

1
.
0
8
0.
0
5
3
7

6
.
3
0
0.
0
0
0
2
4
2

1
.
0
8
2.
6

2
5
.
9

0
.
4
2

0
.
0
4
2

3
3
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Se
l
e
n
i
u
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
0
0.
2
1
4

0
.
2
1
4
5.
0
0

6
.
3
0
0.
0
2
2
5

0
.
2
3
7
0.
2

0
.
3
3
1.
2
0.
7
2

0
%
Un
c
e
r
t
a
i
n
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

S
i
l
v
e
r

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
0
1
4
0

0
.
0
0
2
5
2
0.
0
0
0
1
8
0

0
.
0
0
0
1
8
0
0.
1
8
0

6
.
3
0
0.
0
0
0
8
1
0

0
.
0
0
0
9
9
0
2.
4

2
3
.
8

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

Z
i
n
c

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
7
.
2
3.37
3.37
60
.
8
0
0
0
0
0
0

6
.
3
0
0.
2
7
4

3
.
6
5
16
0
.
0

3
2
0

0
.
0
2
3

0
.
0
1
1

1
0
0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

I
n
o
r
g
a
n
i
c
s
1.
2
0.
2
1
(d
e
t
s
)
Po
s
s
i
b
l
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1
.
8
7

0
.
3
3
7
0.
0
2
4
0

0
.
0
2
4
0
0.
1
8
0

6
.
3
0
0.
0
0
0
8
1
0

0
.
0
2
4
9
5.
0

5
0
.
3

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
n
t
h
r
a
c
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
7
0
7
0.
0
5
0
6

0
.
0
5
0
6
0.
1
8
0

6
.
3
0
0.
0
0
0
8
1
0

0
.
0
5
1
4
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
3
3
4
0.
0
2
3
9

0
.
0
2
3
9
0.
1
8
0

6
.
3
0
0.
0
0
0
8
1
0

0
.
0
2
4
7
1.
0

1
0

0
.
0
2
5

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

F
l
u
o
r
a
n
t
h
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
5
0
0

0
.
0
5
3
5
0.
0
0
3
8
2

0
.
0
0
3
8
2
0.
1
0
7

6
.
3
0
0.
0
0
0
4
8
2

0
.
0
0
4
3
0
12
5
.
0

2
5
0

<
0
.
0
1

<
0
.
0
1

6
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

F
l
u
o
r
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
0
4.
2
9

4
.
2
9
0.
1
8
0

6
.
3
0
0.
0
0
0
8
1
0

4
.
2
9
12
5
.
0

2
5
0

0
.
0
3
4

0
.
0
1
7

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

N
a
p
h
t
h
a
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1
2
.
2

2
.
2
0
0.
1
5
7

0
.
1
5
7
0.
1
8
0

6
.
3
0
0.
0
0
0
8
1
0

0
.
1
5
8
50
.
0

1
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

P
h
e
n
a
n
t
h
r
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
4
0
8
0.
0
2
9
1

0
.
0
2
9
1
0.
1
8
0

6
.
3
0
0.
0
0
0
8
1
0

0
.
0
2
9
9
17
5
.
0

3
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

P
A
H
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
0
2
0
2

0
.
0
1
8
2
0.
0
0
1
3
0

0
.
0
0
1
3
0
0.
9
0
0

6
.
3
0
0.
0
0
4
0
5

0
.
0
0
5
3
5
0.
2

2
.
4

0
.
0
2
2

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

3
.
5
6

0
.
0
0
2
6
7
0.
0
0
0
1
9
1

0
.
0
0
0
1
9
1
0.
0
0
0
7
5
0

6
.
3
0
0.
0
0
0
0
0
3
3
8

0
.
0
0
0
1
9
4
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
2
7
9

0
.
0
0
0
1
8
1
0.
0
0
0
0
1
3
0

0
.
0
0
0
0
1
3
0
0.
0
0
0
6
5
0

6
.
3
0
0.
0
0
0
0
0
2
9
3

0
.
0
0
0
0
1
5
9
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
3
5
4

0
.
0
0
0
2
4
8
0.
0
0
0
0
1
7
7

0
.
0
0
0
0
1
7
7
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
2
0
9
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
2
9
8

0
.
0
0
0
2
0
8
0.
0
0
0
0
1
4
9

0
.
0
0
0
0
1
4
9
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
1
8
0
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1
.
2
8

0
.
0
0
0
5
7
8
0.
0
0
0
0
4
1
3

0
.
0
0
0
0
4
1
3
0.
0
0
0
4
5
0

6
.
3
0
0.
0
0
0
0
0
2
0
3

0
.
0
0
0
0
4
3
3
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
1
2
0
0.
0
0
0
8
5
6

0
.
0
0
0
8
5
6
0.
0
0
1
4
5

6
.
3
0
0.
0
0
0
0
0
6
5
3

0
.
0
0
0
8
6
2
2.
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

5
.
8
4

0
.
0
0
6
1
4
0.
0
0
0
4
3
9

0
.
0
0
0
4
3
9
0.
0
0
1
0
5

6
.
3
0
0.
0
0
0
0
0
4
7
3

0
.
0
0
0
4
4
3
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
1
2
5

0
.
0
0
0
1
2
5
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
1
2
8
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
4
5
0
0.
0
0
0
0
3
2
1

0
.
0
0
0
0
3
2
1
0.
0
0
0
5
5
0

6
.
3
0
0.
0
0
0
0
0
2
4
8

0
.
0
0
0
0
3
4
6
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

2
-
B
u
t
a
n
o
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

4
6
.
1

0
.
2
1
0
0.
0
1
5
0

0
.
0
1
5
0
0.
0
0
4
5
5

6
.
3
0
0.
0
0
0
0
2
0
5

0
.
0
1
5
0
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
2-
H
e
x
a
n
o
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1
6
.
6

0
.
0
6
4
9
0.
0
0
4
6
4

0
.
0
0
4
6
4
0.
0
0
3
9
0

6
.
3
0
0.
0
0
0
0
1
7
6

0
.
0
0
4
6
5
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
6
7
6
0.
0
0
4
8
3

0
.
0
0
4
8
3
0.
0
0
3
4
0

6
.
3
0
0.
0
0
0
0
1
5
3

0
.
0
0
4
8
4
25
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

A
c
e
t
o
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

7
5
.
6

3
.
4
2
0.
2
4
4

0
.
2
4
4
0.
0
4
5
3

6
.
3
0
0.
0
0
0
2
0
4

0
.
2
4
5
10
.
0

5
0

0
.
0
2
4

<
0
.
0
1

1
3
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

B
e
n
z
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
0
4
7
1
0.
0
0
0
3
3
6

0
.
0
0
0
3
3
6
0.
0
0
0
5
7
0

6
.
3
0
0.
0
0
0
0
0
2
5
7

0
.
0
0
0
3
3
9
0.
7

7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Br
o
m
o
f
o
r
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
3
4
6

0
.
0
0
0
2
7
7
0.
0
0
0
0
1
9
8

0
.
0
0
0
0
1
9
8
0.
0
0
0
8
0
0

6
.
3
0
0.
0
0
0
0
0
3
6
0

0
.
0
0
0
0
2
3
4
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Br
o
m
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
1
9
9
0.
0
0
1
4
2

0
.
0
0
1
4
2
0.
0
0
1
0
0

6
.
3
0
0.
0
0
0
0
0
4
5
0

0
.
0
0
1
4
2
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

4
.
2
9

0
.
0
0
2
7
9
0.
0
0
0
1
9
9

0
.
0
0
0
1
9
9
0.
0
0
0
6
5
0

6
.
3
0
0.
0
0
0
0
0
2
9
3

0
.
0
0
0
2
0
2
16
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
1
3
4

0
.
0
0
0
0
8
0
5
0.
0
0
0
0
0
5
7
6

0
.
0
0
0
0
0
5
7
6
0.
0
0
0
6
0
0

6
.
3
0
0.
0
0
0
0
0
2
7
0

0
.
0
0
0
0
0
8
4
6
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

2
.
7
9

0
.
0
0
2
9
3
0.
0
0
0
2
0
9

0
.
0
0
0
2
0
9
0.
0
0
1
0
5

6
.
3
0
0.
0
0
0
0
0
4
7
3

0
.
0
0
0
2
1
4
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
f
o
r
m
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
8
7
3

0
.
0
0
0
5
2
4
0.
0
0
0
0
3
7
4

0
.
0
0
0
0
3
7
4
0.
0
0
0
6
0
0

6
.
3
0
0.
0
0
0
0
0
2
7
0

0
.
0
0
0
0
4
0
1
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
7
Pa
g
e

2

o
f

7
Ta
b
l
e

2
7
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s

W
i
t
h
i
n

H
a
b
i
t
a
t

A
r
e
a
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

H
a
b
i
t
a
t

So
i
l

E
P
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Ch
l
o
r
o
m
e
t
h
a
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
5
5
9

0
.
0
0
0
5
5
9
0.
0
0
1
0
0

6
.
3
0
0.
0
0
0
0
0
4
5
0

0
.
0
0
0
5
6
4
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

1
0
.
6

0
.
0
0
6
9
1
0.
0
0
0
4
9
4

0
.
0
0
0
4
9
4
0.
0
0
0
6
5
0

6
.
3
0
0.
0
0
0
0
0
2
9
3

0
.
0
0
0
4
9
7
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

7
.
1
1

0
.
0
0
3
9
1
0.
0
0
0
2
7
9

0
.
0
0
0
2
7
9
0.
0
0
0
5
5
0

6
.
3
0
0.
0
0
0
0
0
2
4
8

0
.
0
0
0
2
8
2
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Et
h
y
l
b
e
n
z
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
0
6
9
0

0
.
0
0
0
0
4
1
4
0.
0
0
0
0
0
2
9
6

0
.
0
0
0
0
0
2
9
6
0.
0
0
0
6
0
0

6
.
3
0
0.
0
0
0
0
0
2
7
0

0
.
0
0
0
0
0
5
6
6
97
.
0

2
9
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
m,
p
-
X
y
l
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

3
.
0
4

0
.
0
0
3
8
0
0.
0
0
0
2
7
1

0
.
0
0
0
2
7
1
0.
0
0
1
2
5

6
.
3
0
0.
0
0
0
0
0
5
6
3

0
.
0
0
0
2
7
7
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

4
.
1
0

0
.
0
0
6
5
6
0.
0
0
0
4
6
9

0
.
0
0
0
4
6
9
0.
0
0
1
6
0

6
.
3
0
0.
0
0
0
0
0
7
2
0

0
.
0
0
0
4
7
6
5.
9

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

o
-
X
y
l
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

3
.
3
4

0
.
0
0
3
6
0
0.
0
0
0
2
5
8

0
.
0
0
0
2
5
8
0.
0
0
1
0
8

6
.
3
0
0.
0
0
0
0
0
4
8
6

0
.
0
0
0
2
6
2
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

2
.
5
2

0
.
0
0
1
6
4
0.
0
0
0
1
1
7

0
.
0
0
0
1
1
7
0.
0
0
0
6
5
0

6
.
3
0
0.
0
0
0
0
0
2
9
3

0
.
0
0
0
1
2
0
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

T
o
l
u
e
n
e

2
.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

4
.
7
1

0
.
0
7
0
2
0.
0
0
5
0
2

0
.
0
0
5
0
2
0.
0
1
4
9

6
.
3
0
0.
0
0
0
0
6
7
1

0
.
0
0
5
0
9
52
.
0

5
2
0

<
0
.
0
1

<
0
.
0
1

1
3
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

2
.
5
0

0
.
0
0
1
5
0
0.
0
0
0
1
0
7

0
.
0
0
0
1
0
7
0.
0
0
0
6
0
0

6
.
3
0
0.
0
0
0
0
0
2
7
0

0
.
0
0
0
1
1
0
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
5
7
3
0.
0
0
0
0
4
0
9

0
.
0
0
0
0
4
0
9
0.
0
0
0
7
0
0

6
.
3
0
0.
0
0
0
0
0
3
1
5

0
.
0
0
0
0
4
4
1
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

0
.
3
3
1

0
.
0
0
0
1
8
2
0.
0
0
0
0
1
3
0

0
.
0
0
0
0
1
3
0
0.
0
0
0
5
5
0

6
.
3
0
0.
0
0
0
0
0
2
4
8

0
.
0
0
0
0
1
5
5
0.
7

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
Vi
n
y
l

c
h
l
o
r
i
d
e
2.
1
0
0

0
.
0
7
1

1

0
.
0
7
1

0

-

0

0

0

-

0

0

1
0
0

3
.
1
0

0
.
0
0
2
6
4
0.
0
0
0
1
8
8

0
.
0
0
0
1
8
8
0.
0
0
0
8
5
0

6
.
3
0
0.
0
0
0
0
0
3
8
3

0
.
0
0
0
1
9
2
0.
2

1
.
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t
HI

-

V
O
C
s
0.
0
2
6
<0
.
0
1

(
d
e
t
s
)
No
n
e
Pr
o
n
g
h
o
r
n
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1
5

1
.
2
0
0.
0
4
1
3

0
.
0
4
1
3
0.
0
8
0
0

2
.
0
0
0.
0
0
0
0
5
5
0

0
.
0
4
1
4
0.
0

0
.
2
1.
0
0.
2
1

0
%
Un
c
e
r
t
a
i
n
Pr
o
n
g
h
o
r
n

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
3
7
6

0
.
3
7
6
0.
0
1
2
9

0
.
0
1
2
9
1.
0
0

2
.
0
0
0.
0
0
0
6
8
8

0
.
0
1
3
6
2.
0

8

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

3
.
1
4

4
.
7
1
0.
1
6
2

0
.
1
6
2
1.
5
0

2
.
0
0
0.
0
0
1
0
3

0
.
1
6
3
2.
0

8

0
.
0
8
2

0
.
0
2
0

0
%
No
n
e
Pr
o
n
g
h
o
r
n

H
M
X

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
0
1.
0
3

1
.
0
3
3.
3
0

2
.
0
0
0.
0
0
2
2
7

1
.
0
3
1.
0

5
1.
0
0.
2
1

2
0
%
Po
s
s
i
b
l
e
Pr
o
n
g
h
o
r
n
HI

-

E
n
e
r
g
e
t
i
c
s
1.
0
0.
2
1
(d
e
t
s
)
Po
s
s
i
b
l
e
Pr
o
n
g
h
o
r
n

A
n
t
i
m
o
n
y

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
0
1
0
2

0
.
0
3
8
8
0.
0
0
1
3
3

0
.
0
0
1
3
3
3.
8
0

2
.
0
0
0.
0
0
2
6
1

0
.
0
0
3
9
5
0.
1

0
.
6
4

0
.
0
6
7

<
0
.
0
1

8
8
%
No
n
e
Pr
o
n
g
h
o
r
n

C
a
d
m
i
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
6
9
6
0.
0
2
3
9

0
.
0
2
3
9
1.
2
3

2
.
0
0
0.
0
0
0
8
4
6

0
.
0
2
4
8
0.
8

1
.
4
2

0
.
0
3
2

0
.
0
1
7

6
2
%
No
n
e
Pr
o
n
g
h
o
r
n

C
o
p
p
e
r

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
8
0.
2
3
3

0
.
2
3
3
23
.
6
0
0
0
0
0
0

2
.
0
0
0.
0
1
6
2

0
.
2
5
0
11
.
7

1
5
.
1
4

0
.
0
2
1

0
.
0
1
6

9
5
%
No
n
e
Pr
o
n
g
h
o
r
n

L
e
a
d

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
3
8
0.
0
4
7
5

0
.
0
4
7
5
19
.
0
0
0
0
0
0
0

2
.
0
0
0.
0
1
3
1

0
.
0
6
0
6
0.
9

4
.
7

0
.
0
6
6

0
.
0
1
3

9
5
%
No
n
e
Pr
o
n
g
h
o
r
n

M
o
l
y
b
d
e
n
u
m

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
4
0
0

0
.
4
0
0
0.
0
1
3
8

0
.
0
1
3
8
1.
0
0

2
.
0
0
0.
0
0
0
6
8
8

0
.
0
1
4
4
0.
3

2
.
6

0
.
0
5
6

<
0
.
0
1

8
7
%
No
n
e
Pr
o
n
g
h
o
r
n

N
i
t
r
a
t
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1

1
0
0.
3
4
3
9
3
7
4
9
8

0
.
3
4
3
9
3
7
4
9
8
10
.
0
0
0
0
0
0
0

2
.
0
0
0.
0
0
6
9

0
.
3
5
1
50
7
.
0

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
Pr
o
n
g
h
o
r
n

P
e
r
c
h
l
o
r
a
t
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

2
8
2

1
5
.
1
0
0.
5
2
0

0
.
5
2
0
0.
0
5
3
7

2
.
0
0
0.
0
0
0
0
3
6
9

0
.
5
2
0
2.
6

2
5
.
9

0
.
2
0

0
.
0
2
0

3
3
%
No
n
e
Pr
o
n
g
h
o
r
n

S
i
l
v
e
r

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
0
1
4
0

0
.
0
0
2
5
2
0.
0
0
0
0
8
6
7

0
.
0
0
0
0
8
6
7
0.
1
8
0

2
.
0
0
0.
0
0
0
1
2
4

0
.
0
0
0
2
1
0
2.
4

2
3
.
8

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Pr
o
n
g
h
o
r
n

Z
i
n
c

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
7
.
2
1.62
1.62
60
.
8
0
0
0
0
0
0

2
.
0
0
0.
0
4
1
8

1
.
6
7
16
0
.
0

3
2
0

0
.
0
1
0

<
0
.
0
1

1
0
0
%
No
n
e
Pr
o
n
g
h
o
r
n
HI

-

I
n
o
r
g
a
n
i
c
s
0.
4
5

0
.
0
8
4
(d
e
t
s
)
No
n
e
Pr
o
n
g
h
o
r
n

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1
.
8
7

0
.
3
3
7
0.
0
1
1
6

0
.
0
1
1
6
0.
1
8
0

2
.
0
0
0.
0
0
0
1
2
4

0
.
0
1
1
7
5.
0

5
0
.
3

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n

A
n
t
h
r
a
c
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
7
0
7
0.
0
2
4
3

0
.
0
2
4
3
0.
1
8
0

2
.
0
0
0.
0
0
0
1
2
4

0
.
0
2
4
5
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
3
3
4
0.
0
1
1
5

0
.
0
1
1
5
0.
1
8
0

2
.
0
0
0.
0
0
0
1
2
4

0
.
0
1
1
6
1.
0

1
0

0
.
0
1
2

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n

F
l
u
o
r
a
n
t
h
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
5
0
0

0
.
0
5
3
5
0.
0
0
1
8
4

0
.
0
0
1
8
4
0.
1
0
7

2
.
0
0
0.
0
0
0
0
7
3
6

0
.
0
0
1
9
1
12
5
.
0

2
5
0

<
0
.
0
1

<
0
.
0
1

6
%
No
n
e
Pr
o
n
g
h
o
r
n

F
l
u
o
r
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
0
2.
0
6

2
.
0
6
0.
1
8
0

2
.
0
0
0.
0
0
0
1
2
4

2
.
0
6
12
5
.
0

2
5
0

0
.
0
1
6

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n

N
a
p
h
t
h
a
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1
2
.
2

2
.
2
0
0.
0
7
5
5

0
.
0
7
5
5
0.
1
8
0

2
.
0
0
0.
0
0
0
1
2
4

0
.
0
7
5
7
50
.
0

1
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n

P
h
e
n
a
n
t
h
r
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
4
0
8
0.
0
1
4
0

0
.
0
1
4
0
0.
1
8
0

2
.
0
0
0.
0
0
0
1
2
4

0
.
0
1
4
1
17
5
.
0

3
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
HI

-

P
A
H
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

3
.
5
6

0
.
0
0
2
6
7
0.
0
0
0
0
9
1
9

0
.
0
0
0
0
9
1
9
0.
0
0
0
7
5
0

2
.
0
0
0.
0
0
0
0
0
0
5
1
6

0
.
0
0
0
0
9
2
4
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
2
7
9

0
.
0
0
0
1
8
1
0.
0
0
0
0
0
6
2
4

0
.
0
0
0
0
0
6
2
4
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
4
4
7

0
.
0
0
0
0
0
6
6
9
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
3
5
4

0
.
0
0
0
2
4
8
0.
0
0
0
0
0
8
5
3

0
.
0
0
0
0
0
8
5
3
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
0
9
0
1
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
2
9
8

0
.
0
0
0
2
0
8
0.
0
0
0
0
0
7
1
7

0
.
0
0
0
0
0
7
1
7
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
0
7
6
5
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1
.
2
8

0
.
0
0
0
5
7
8
0.
0
0
0
0
1
9
9

0
.
0
0
0
0
1
9
9
0.
0
0
0
4
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
1
0

0
.
0
0
0
0
2
0
2
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
1
2
0
0.
0
0
0
4
1
2

0
.
0
0
0
4
1
2
0.
0
0
1
4
5

2
.
0
0
0.
0
0
0
0
0
0
9
9
7

0
.
0
0
0
4
1
3
2.
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

5
.
8
4

0
.
0
0
6
1
4
0.
0
0
0
2
1
1

0
.
0
0
0
2
1
1
0.
0
0
1
0
5

2
.
0
0
0.
0
0
0
0
0
0
7
2
2

0
.
0
0
0
2
1
2
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
0
6
0
3

0
.
0
0
0
0
6
0
3
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
6
0
7
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
4
5
0
0.
0
0
0
0
1
5
5

0
.
0
0
0
0
1
5
5
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
7
8

0
.
0
0
0
0
1
5
8
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n

2
-
B
u
t
a
n
o
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

4
6
.
1

0
.
2
1
0
0.
0
0
7
2
1

0
.
0
0
7
2
1
0.
0
0
4
5
5

2
.
0
0
0.
0
0
0
0
0
3
1
3

0
.
0
0
7
2
1
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Pr
o
n
g
h
o
r
n
2-
H
e
x
a
n
o
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1
6
.
6

0
.
0
6
4
9
0.
0
0
2
2
3

0
.
0
0
2
2
3
0.
0
0
3
9
0

2
.
0
0
0.
0
0
0
0
0
2
6
8

0
.
0
0
2
2
3
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
6
7
6
0.
0
0
2
3
2

0
.
0
0
2
3
2
0.
0
0
3
4
0

2
.
0
0
0.
0
0
0
0
0
2
3
4

0
.
0
0
2
3
3
25
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n

A
c
e
t
o
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

7
5
.
6

3
.
4
2
0.
1
1
8

0
.
1
1
8
0.
0
4
5
3

2
.
0
0
0.
0
0
0
0
3
1
1

0
.
1
1
8
10
.
0

5
0

0
.
0
1
2

<
0
.
0
1

1
3
%
No
n
e
Pr
o
n
g
h
o
r
n

B
e
n
z
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
0
4
7
1
0.
0
0
0
1
6
2

0
.
0
0
0
1
6
2
0.
0
0
0
5
7
0

2
.
0
0
0.
0
0
0
0
0
0
3
9
2

0
.
0
0
0
1
6
2
0.
7

7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Pr
o
n
g
h
o
r
n
Br
o
m
o
f
o
r
m
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
3
4
6

0
.
0
0
0
2
7
7
0.
0
0
0
0
0
9
5
3

0
.
0
0
0
0
0
9
5
3
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
5
0

0
.
0
0
0
0
1
0
1
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
Br
o
m
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
1
9
9
0.
0
0
0
6
8
3

0
.
0
0
0
6
8
3
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
8
8

0
.
0
0
0
6
8
4
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

4
.
2
9

0
.
0
0
2
7
9
0.
0
0
0
0
9
6
0

0
.
0
0
0
0
9
6
0
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
4
4
7

0
.
0
0
0
0
9
6
4
16
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
1
3
4

0
.
0
0
0
0
8
0
5
0.
0
0
0
0
0
2
7
7

0
.
0
0
0
0
0
2
7
7
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
1
3

0
.
0
0
0
0
0
3
1
8
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

2
.
7
9

0
.
0
0
2
9
3
0.
0
0
0
1
0
1

0
.
0
0
0
1
0
1
0.
0
0
1
0
5

2
.
0
0
0.
0
0
0
0
0
0
7
2
2

0
.
0
0
0
1
0
1
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
f
o
r
m
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
8
7
3

0
.
0
0
0
5
2
4
0.
0
0
0
0
1
8
0

0
.
0
0
0
0
1
8
0
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
1
3

0
.
0
0
0
0
1
8
4
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
Ch
l
o
r
o
m
e
t
h
a
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
2
6
9

0
.
0
0
0
2
6
9
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
6
8
8

0
.
0
0
0
2
7
0
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

1
0
.
6

0
.
0
0
6
9
1
0.
0
0
0
2
3
8

0
.
0
0
0
2
3
8
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
4
4
7

0
.
0
0
0
2
3
8
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

7
.
1
1

0
.
0
0
3
9
1
0.
0
0
0
1
3
5

0
.
0
0
0
1
3
5
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
7
8

0
.
0
0
0
1
3
5
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
Et
h
y
l
b
e
n
z
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
0
6
9
0

0
.
0
0
0
0
4
1
4
0.
0
0
0
0
0
1
4
2

0
.
0
0
0
0
0
1
4
2
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
1
3

0
.
0
0
0
0
0
1
8
4
97
.
0

2
9
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
m,
p
-
X
y
l
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

3
.
0
4

0
.
0
0
3
8
0
0.
0
0
0
1
3
1

0
.
0
0
0
1
3
1
0.
0
0
1
2
5

2
.
0
0
0.
0
0
0
0
0
0
8
6
0

0
.
0
0
0
1
3
2
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

4
.
1
0

0
.
0
0
6
5
6
0.
0
0
0
2
2
6

0
.
0
0
0
2
2
6
0.
0
0
1
6
0

2
.
0
0
0.
0
0
0
0
0
1
1
0

0
.
0
0
0
2
2
7
5.
9

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n

o
-
X
y
l
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

3
.
3
4

0
.
0
0
3
6
0
0.
0
0
0
1
2
4

0
.
0
0
0
1
2
4
0.
0
0
1
0
8

2
.
0
0
0.
0
0
0
0
0
0
7
4
3

0
.
0
0
0
1
2
5
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Pr
o
n
g
h
o
r
n
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

2
.
5
2

0
.
0
0
1
6
4
0.
0
0
0
0
5
6
4

0
.
0
0
0
0
5
6
4
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
4
4
7

0
.
0
0
0
0
5
6
8
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n

T
o
l
u
e
n
e

4
8
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

4
.
7
1

0
.
0
7
0
2
0.
0
0
2
4
2

0
.
0
0
2
4
2
0.
0
1
4
9

2
.
0
0
0.
0
0
0
0
1
0
2

0
.
0
0
2
4
3
52
.
0

5
2
0

<
0
.
0
1

<
0
.
0
1

1
3
%
No
n
e
Pr
o
n
g
h
o
r
n
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

2
.
5
0

0
.
0
0
1
5
0
0.
0
0
0
0
5
1
6

0
.
0
0
0
0
5
1
6
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
1
3

0
.
0
0
0
0
5
2
1
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
5
7
3
0.
0
0
0
0
1
9
7

0
.
0
0
0
0
1
9
7
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
8
2

0
.
0
0
0
0
2
0
2
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Pr
o
n
g
h
o
r
n
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

0
.
3
3
1

0
.
0
0
0
1
8
2
0.
0
0
0
0
0
6
2
7

0
.
0
0
0
0
0
6
2
7
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
7
8

0
.
0
0
0
0
0
6
6
5
0.
7

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
Vi
n
y
l

c
h
l
o
r
i
d
e
48
.
7
6
1

0
.
0
3
4

1

0
.
0
3
4

0

-

0

0

0

-

0

0

1
0
0

3
.
1
0

0
.
0
0
2
6
4
0.
0
0
0
0
9
0
7

0
.
0
0
0
0
9
0
7
0.
0
0
0
8
5
0

2
.
0
0
0.
0
0
0
0
0
0
5
8
5

0
.
0
0
0
0
9
1
3
0.
2

1
.
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Pr
o
n
g
h
o
r
n
HI

-

V
O
C
s
0.
0
1
3
<0
.
0
1

(
d
e
t
s
)
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
6

2
.
1
3

0
.
5
3
2

0

-

0
0

0
.
5
3
2
0.
0
8
0
0

1
3
.
0
0
0.
0
0
2
6
0

0
.
5
3
5
0.
0

0
.
2
13
2.
7
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
7
1

3
.
7
1

0
.
9
2
8

0

-

0
0

0
.
9
2
8
1.
0
0

1
3
.
0
0
0.
0
3
2
5

0
.
9
6
0
2.
0

8

0
.
4
8

0
.
1
2

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
1
6

4
.
7
4

1
.
1
8

0

-

0
01
.
1
8
1.
5
0

1
3
.
0
0
0.
0
4
8
8

1
.
2
3
2.
0

8

0
.
6
2

0
.
1
5

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

H
M
X
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
3
1
3

1
.
0
3

0
.
2
5
8

0

-

0
0

0
.
2
5
8
3.
3
0

1
3
.
0
0
0.
1
0
7

0
.
3
6
5
1.
0

5

0
.
3
6

0
.
0
7
3

2
0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
RD
X
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
3

2
1
.
8

0

-

0
0

2
1
.
8
1.
5
0

1
3
.
0
0
0.
0
4
8
8

2
1
.
9
0
0
2.
0

2
0
11
1.
1
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Te
t
r
y
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
1

6
.
6
9

1
.
6
7

0

-

0
01
.
6
7
0.
2
3
0

1
3
.
0
0
0.
0
0
7
4
8

1
.
6
8
1.
3

6
.
2
1.
3
0.
2
7

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

E
n
e
r
g
e
t
i
c
s
0.
3
6

0
.
0
7
3
(d
e
t
s
)
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
n
t
i
m
o
n
y
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
0
1
6
2

0
.
0
6
1
6

0
.
0
1
5
4

0

-

0
0

0
.
0
1
5
4
3.
8
0

1
3
.
0
0
0.
1
2
4

0
.
1
3
9
0.
1

0
.
6
4
2.
4
0.
2
2

8
8
%
Po
s
s
i
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

C
a
d
m
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

9
.
7
6

2
.
4
4

0

-

0
02
.
4
4
1.
2
3

1
3
.
0
0
0.
0
4
0
0

2
.
4
8
0.
8

1
.
4
2
3.
2
1.
8
62
%
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

C
o
p
p
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
.
3

3
.
0
7

0

-

0
03
.
0
7
23
.
6
0
0
0
0
0
0

1
3
.
0
0
0.
7
6
7

3
.
8
4
11
.
7

1
5
.
1
4

0
.
3
3

0
.
2
5

9
5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

L
e
a
d
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
6
6

2
.
1
6

0

-

0
02
.
1
6
19
.
0
0
0
0
0
0
0

1
3
.
0
0
0.
6
1
8

2
.
7
8
0.
9

4
.
7
3.
0
0.
5
9

9
5
%
Po
s
s
i
b
l
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
7
Pa
g
e

3

o
f

7
Ta
b
l
e

2
7
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s

W
i
t
h
i
n

H
a
b
i
t
a
t

A
r
e
a
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

H
a
b
i
t
a
t

So
i
l

E
P
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

M
o
l
y
b
d
e
n
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

0
.
9
5
3

0
.
9
5
3

0
.
2
3
8

0

-

0
0

0
.
2
3
8
1.
0
0

1
3
.
0
0
0.
0
3
2
5

0
.
2
7
1
0.
3

2
.
6
1.
0
0.
1
0

8
7
%
Po
s
s
i
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

N
i
t
r
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1

1
0

2
.
5

0

-

0
02
.
5
10
.
0
0
0
0
0
0
0

1
3
.
0
0
0.
3
2
5

2
.
8
2
5
50
7
.
0

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

P
e
r
c
h
l
o
r
a
t
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
0
0

0
.
0
5
3
7

0
.
0
1
3
4

0

-

0
0

0
.
0
1
3
4
0.
0
5
3
7

1
3
.
0
0
0.
0
0
1
7
4

0
.
0
1
5
2
2.
6

2
5
.
9

<
0
.
0
1

<
0
.
0
1

3
3
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Se
l
e
n
i
u
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
0
2

0
.
7
5
5

0

-

0
0

0
.
7
5
5
5.
0
0

1
3
.
0
0
0.
1
6
2

0
.
9
1
7
0.
2

0
.
3
3
4.
6
2.
8
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

S
i
l
v
e
r
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
0
4

0
.
3
6
8

0
.
0
9
2
0

0

-

0
0

0
.
0
9
2
0
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
0
9
7
9
2.
4

2
3
.
8

0
.
0
4
1

<
0
.
0
1

5
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

Z
i
n
c
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
2
9

8
2
.
3

0

-

0
0
82
.3
60
.
8
0
0
0
0
0
0

1
3
.
0
0
1.
9
7

8
4
.
2
0
0
16
0
.
0

3
2
0

0
.
5
3

0
.
2
6

1
0
0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

I
n
o
r
g
a
n
i
c
s
11

3
.
2
(d
e
t
s
)
Pr
o
b
a
b
l
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9

5
.
2
3

1
.
3
1

0

-

0
01
.
3
1
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

1
.
3
1
5.
0

5
0
.
3

0
.
2
6

0
.
0
2
6

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
4
2

0
.
4
3
6

0
.
1
0
9

0

-

0
0

0
.
1
0
9
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
1
1
5
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
5
9

0
.
2
8
6

0
.
0
7
1
6

0

-

0
0

0
.
0
7
1
6
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
0
7
7
4
1.
0

1
0

0
.
0
7
7

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
a
)
p
y
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
3
3

0
.
2
3
9

0
.
0
5
9
8

0

-

0
0

0
.
0
5
9
8
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
0
6
5
7
1.
0

1
0

0
.
0
6
6

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
6
0

0
.
4
6
8

0
.
1
1
7

0

-

0
0

0
.
1
1
7
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
1
2
3
1.
0

1
0

0
.
1
2

0
.
0
1
2

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
9
4

0
.
5
2
9

0
.
1
3
2

0

-

0
0

0
.
1
3
2
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
1
3
8
1.
0

1
0

0
.
1
4

0
.
0
1
4

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
6
0

0
.
4
6
8

0
.
1
1
7

0

-

0
0

0
.
1
1
7
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
1
2
3
1.
0

1
0

0
.
1
2

0
.
0
1
2

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
r
y
s
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
2
9

0
.
4
1
2

0
.
1
0
3

0

-

0
0

0
.
1
0
3
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
1
0
9
1.
0

1
0

0
.
1
1

0
.
0
1
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
3
1

0
.
4
1
6

0
.
1
0
4

0

-

0
0

0
.
1
0
4
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
1
1
0
1.
0

1
0

0
.
1
1

0
.
0
1
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

F
l
u
o
r
a
n
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
.
0
4

0
.
3
2
5

0
.
0
8
1
3

0

-

0
0

0
.
0
8
1
3
0.
1
0
7

1
3
.
0
0
0.
0
0
3
4
8

0
.
0
8
4
8
12
5
.
0

2
5
0

<
0
.
0
1

<
0
.
0
1

6
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

F
l
u
o
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

9
.
5
7

1
.
7
2

0
.
4
3
1

0

-

0
0

0
.
4
3
1
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
4
3
6
12
5
.
0

2
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
.
8
6

0
.
5
1
5

0
.
1
2
9

0

-

0
0

0
.
1
2
9
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
1
3
5
1.
0

1
0

0
.
1
4

0
.
0
1
4

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

N
a
p
h
t
h
a
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

4
.
4
0

0
.
7
9
2

0
.
1
9
8

0

-

0
0

0
.
1
9
8
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
2
0
4
50
.
0

1
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

P
h
e
n
a
n
t
h
r
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

1
.
7
2

0
.
3
1
0

0
.
0
7
7
4

0

-

0
0

0
.
0
7
7
4
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

0
.
0
8
3
2
17
5
.
0

3
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

P
A
H
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

T
P
H
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

-

0

0

0

-

0

0
0
20
.
0
0
0
0
0
0
0

1
3
.
0
0
0.
6
5
0

0
.
6
5
0
10
0
0
.
0

1
5
0
0
0

<
0
.
0
1

<
0
.
0
1

1
0
0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

P
e
t
r
o
l
e
u
m
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
5
.
1

3
1
.
6

7
.
9
0

0

-

0
07
.
9
0
0.
9
0
0

1
3
.
0
0
0.
0
2
9
2

7
.
9
3
0.
2

2
.
4
33
3.
3
0%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
5
.
6

6
.
4
0

1
.
6
0

0

-

0
01
.
6
0
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

1
.
6
1
0.
2

2
.
4
6.
7
0.
6
7

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
2
.
6

5
.
8
7

1
.
4
7

0

-

0
01
.
4
7
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

1
.
4
7
0.
2

2
.
4
6.
1
0.
6
1

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

4
0
.
2

7
.
2
4

1
.
8
1

0

-

0
01
.
8
1
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

1
.
8
2
1.
6

3
.
2
1.
1
0.
5
7

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
6

7
.
0
2

1
.
7
5

0

-

0
01
.
7
5
0.
1
9
5

1
3
.
0
0
0.
0
0
6
3
4

1
.
7
6
1.
6

3
.
2
1.
1
0.
5
5

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
8

6
.
8
4

1
.
7
1

0

-

0
01
.
7
1
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

1
.
7
2
1.
6

3
.
2
1.
1
0.
5
4

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

5
.
9
3

5
.
3
4

1
.
3
3

0

-

0
01
.
3
3
0.
9
0
0

1
3
.
0
0
0.
0
2
9
2

1
.
3
6
0.
2

2
.
4
5.
7
0.
5
7

0
%
Un
c
e
r
t
a
i
n
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
3

0
.
0
2
1
2

0
.
0
0
5
3
0

0

-

0
0

0
.
0
0
5
3
0
0.
0
0
0
7
5
0

1
3
.
0
0
0.
0
0
0
0
2
4
4

0
.
0
0
5
3
2
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
4

0
.
0
2
0
4

0
.
0
0
5
1
1

0

-

0
0

0
.
0
0
5
1
1
0.
0
0
0
6
5
0

1
3
.
0
0
0.
0
0
0
0
2
1
1

0
.
0
0
5
1
3
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
1

0
.
0
2
1
8

0
.
0
0
5
4
5

0

-

0
0

0
.
0
0
5
4
5
0.
0
0
0
7
0
0

1
3
.
0
0
0.
0
0
0
0
2
2
8

0
.
0
0
5
4
7
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
4

0
.
0
2
2
0

0
.
0
0
5
4
9

0

-

0
0

0
.
0
0
5
4
9
0.
0
0
0
7
0
0

1
3
.
0
0
0.
0
0
0
0
2
2
8

0
.
0
0
5
5
1
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
9
.
5

0
.
0
1
3
3

0
.
0
0
3
3
2

0

-

0
0

0
.
0
0
3
3
2
0.
0
0
0
4
5
0

1
3
.
0
0
0.
0
0
0
0
1
4
6

0
.
0
0
3
3
3
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
3
9
6

0
.
0
0
9
8
9

0

-

0
0

0
.
0
0
9
8
9
0.
0
0
1
4
5

1
3
.
0
0
0.
0
0
0
0
4
7
1

0
.
0
0
9
9
4
2.
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
7

0
.
0
2
9
1

0
.
0
0
7
2
7

0

-

0
0

0
.
0
0
7
2
7
0.
0
0
1
0
5

1
3
.
0
0
0.
0
0
0
0
3
4
1

0
.
0
0
7
3
0
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
2
0
1

0
.
0
0
5
0
2

0

-

0
0

0
.
0
0
5
0
2
0.
0
0
0
7
0
0

1
3
.
0
0
0.
0
0
0
0
2
2
8

0
.
0
0
5
0
4
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
1

0
.
0
1
6
5

0
.
0
0
4
1
3

0

-

0
0

0
.
0
0
4
1
3
0.
0
0
0
5
5
0

1
3
.
0
0
0.
0
0
0
0
1
7
9

0
.
0
0
4
1
5
50
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

2
-
B
u
t
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
5
.
4

0
.
1
1
6

0
.
0
2
8
9

0

-

0
0

0
.
0
2
8
9
0.
0
0
4
5
5

1
3
.
0
0
0.
0
0
0
1
4
8

0
.
0
2
9
0
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
2-
H
e
x
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
5

0
.
1
0
3

0
.
0
2
5
8

0

-

0
0

0
.
0
2
5
8
0.
0
0
3
9
0

1
3
.
0
0
0.
0
0
0
1
2
7

0
.
0
2
6
0
10
.
0

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
3

0
.
0
8
9
4

0
.
0
2
2
4

0

-

0
0

0
.
0
2
2
4
0.
0
0
3
4
0

1
3
.
0
0
0.
0
0
0
1
1
0

0
.
0
2
2
5
25
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

A
c
e
t
o
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
4
.
9

1
.
1
3

0
.
2
8
1

0

-

0
0

0
.
2
8
1
0.
0
4
5
3

1
3
.
0
0
0.
0
0
1
4
7

0
.
2
8
3
10
.
0

5
0

0
.
0
2
8

<
0
.
0
1

1
3
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

B
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
1
5
6

0
.
0
0
3
8
9

0

-

0
0

0
.
0
0
3
8
9
0.
0
0
0
5
7
0

1
3
.
0
0
0.
0
0
0
0
1
8
5

0
.
0
0
3
9
1
0.
7

7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Br
o
m
o
f
o
r
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
2

0
.
0
2
4
9

0
.
0
0
6
2
3

0

-

0
0

0
.
0
0
6
2
3
0.
0
0
0
8
0
0

1
3
.
0
0
0.
0
0
0
0
2
6
0

0
.
0
0
6
2
6
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Br
o
m
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
6
.
3

0
.
0
2
6
3

0
.
0
0
6
5
7

0

-

0
0

0
.
0
0
6
5
7
0.
0
0
1
0
0

1
3
.
0
0
0.
0
0
0
0
3
2
5

0
.
0
0
6
6
1
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ca
r
b
o
n

t
e
t
r
a
c
h
l
o
r
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8

0
.
0
1
8
2

0
.
0
0
4
5
6

0

-

0
0

0
.
0
0
4
5
6
0.
0
0
0
6
5
0

1
3
.
0
0
0.
0
0
0
0
2
1
1

0
.
0
0
4
5
8
16
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
2
.
4

0
.
0
1
9
5

0
.
0
0
4
8
6

0

-

0
0

0
.
0
0
4
8
6
0.
0
0
0
6
0
0

1
3
.
0
0
0.
0
0
0
0
1
9
5

0
.
0
0
4
8
8
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
6

0
.
0
3
0
0

0
.
0
0
7
5
0

0

-

0
0

0
.
0
0
7
5
0
0.
0
0
1
0
5

1
3
.
0
0
0.
0
0
0
0
3
4
1

0
.
0
0
7
5
3
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
f
o
r
m
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0

0
.
0
1
8
0

0
.
0
0
4
5
0

0

-

0
0

0
.
0
0
4
5
0
0.
0
0
0
6
0
0

1
3
.
0
0
0.
0
0
0
0
1
9
5

0
.
0
0
4
5
2
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
3

0
.
0
2
7
3

0
.
0
0
6
8
4

0

-

0
0

0
.
0
0
6
8
4
0.
0
0
1
0
0

1
3
.
0
0
0.
0
0
0
0
3
2
5

0
.
0
0
6
8
7
15
.
0

4
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7

0
.
0
1
7
5

0
.
0
0
4
3
9

0

-

0
0

0
.
0
0
4
3
9
0.
0
0
0
6
5
0

1
3
.
0
0
0.
0
0
0
0
2
1
1

0
.
0
0
4
4
1
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
5

0
.
0
1
5
1

0
.
0
0
3
7
8

0

-

0
0

0
.
0
0
3
7
8
0.
0
0
0
5
5
0

1
3
.
0
0
0.
0
0
0
0
1
7
9

0
.
0
0
3
7
9
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Et
h
y
l
b
e
n
z
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
3
.
3

0
.
0
2
0
0

0
.
0
0
5
0
0

0

-

0
0

0
.
0
0
5
0
0
0.
0
0
0
6
0
0

1
3
.
0
0
0.
0
0
0
0
1
9
5

0
.
0
0
5
0
2
97
.
0

2
9
1

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
m,
p
-
X
y
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
5

0
.
0
3
5
6

0
.
0
0
8
8
9

0

-

0
0

0
.
0
0
8
8
9
0.
0
0
1
2
5

1
3
.
0
0
0.
0
0
0
0
4
0
6

0
.
0
0
8
9
3
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Me
t
h
y
l
e
n
e

c
h
l
o
r
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
1

0
.
0
4
5
0

0
.
0
1
1
2

0

-

0
0

0
.
0
1
1
2
0.
0
0
1
6
0

1
3
.
0
0
0.
0
0
0
0
5
2
0

0
.
0
1
1
3
5.
9

5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

o
-
X
y
l
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
3

0
.
0
3
0
6

0
.
0
0
7
6
5

0

-

0
0

0
.
0
0
7
6
5
0.
0
0
1
0
8

1
3
.
0
0
0.
0
0
0
0
3
5
1

0
.
0
0
7
6
9
17
9
.
0

3
5
7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Ph
e
n
o
l
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
6

5
.
1
5

1
.
2
9

0

-

0
01
.
2
9
0.
1
8
0

1
3
.
0
0
0.
0
0
5
8
5

1
.
2
9
17
.
1

N
S
V

0
.
0
7
6
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
1
8
6

0
.
0
0
4
6
6

0

-

0
0

0
.
0
0
4
6
6
0.
0
0
0
6
5
0

1
3
.
0
0
0.
0
0
0
0
2
1
1

0
.
0
0
4
6
8
1.
4

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

T
o
l
u
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
7
.
9

0
.
4
1
6

0
.
1
0
4

0

-

0
0

0
.
1
0
4
0.
0
1
4
9

1
3
.
0
0
0.
0
0
0
4
8
4

0
.
1
0
5
52
.
0

5
2
0

<
0
.
0
1

<
0
.
0
1

1
3
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
7

0
.
0
1
7
2

0
.
0
0
4
3
0

0

-

0
0

0
.
0
0
4
3
0
0.
0
0
0
6
0
0

1
3
.
0
0
0.
0
0
0
0
1
9
5

0
.
0
0
4
3
2
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
0
.
1

0
.
0
2
1
0

0
.
0
0
5
2
6

0

-

0
0

0
.
0
0
5
2
6
0.
0
0
0
7
0
0

1
3
.
0
0
0.
0
0
0
0
2
2
8

0
.
0
0
5
2
8
45
.
2

N
S
V

<
0
.
0
1
--
0%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Tr
i
c
h
l
o
r
o
e
t
h
y
l
e
n
e

(
T
C
E
)
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

3
1
.
2

0
.
0
1
7
2

0
.
0
0
4
2
9

0

-

0
0

0
.
0
0
4
2
9
0.
0
0
0
5
5
0

1
3
.
0
0
0.
0
0
0
0
1
7
9

0
.
0
0
4
3
1
0.
7

7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
Vi
n
y
l

c
h
l
o
r
i
d
e
0.
0
4
1

0
.
2
5
0
1

0
.
2
5
0

0

-

0

0

1
0
0

2
8
.
4

0
.
0
2
4
2

0
.
0
0
6
0
4

0

-

0
0

0
.
0
0
6
0
4
0.
0
0
0
8
5
0

1
3
.
0
0
0.
0
0
0
0
2
7
6

0
.
0
0
6
0
7
0.
2

1
.
7

0
.
0
3
6

<
0
.
0
1

0
%
No
n
e
Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e
HI

-

V
O
C
s
0.
0
3
9
<0
.
0
1

(
d
e
t
s
)
No
n
e
Co
y
o
t
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

1
.
0
5

1
.
0
5

0
.
0
0
2
9
7

0

-

0

0

0

-

0
0

0
.
0
0
2
9
7
1.
0
0

2
.
8
0
0.
0
0
0
0
7
9
0

0
.
0
0
3
0
5
2.
0

8

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Co
y
o
t
e

H
M
X

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

2
.
1
3

7
.
0
4

0
.
0
1
9
9

0

-

0

0

0

-

0
00
.
0
1
9
9
3.
3
0

2
.
8
0
0.
0
0
0
2
6
1

0
.
0
2
0
1
1.
0

5

0
.
0
2
0

<
0
.
0
1

2
0
%
No
n
e
Co
y
o
t
e
HI

-

E
n
e
r
g
e
t
i
c
s
0.
0
2
0
<0
.
0
1

(
d
e
t
s
)
No
n
e
Co
y
o
t
e

A
n
t
i
m
o
n
y

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

1
.
0
0

3
.
8
0

0
.
0
1
0
7

0

-

0

0

0

-

0
00
.
0
1
0
7
3.
8
0

2
.
8
0
0.
0
0
0
3
0
0

0
.
0
1
1
0
0.
1

0
.
6
4

0
.
1
9

0
.
0
1
7

8
8
%
No
n
e
Co
y
o
t
e

C
a
d
m
i
u
m

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
7
3
9

0
.
0
0
2
0
9

0

-

0

0

0

-

0
0

0
.
0
0
2
0
9
1.
2
3

2
.
8
0
0.
0
0
0
0
9
7
2

0
.
0
0
2
1
8
0.
8

1
.
4
2

<
0
.
0
1

<
0
.
0
1

6
2
%
No
n
e
Co
y
o
t
e

C
o
p
p
e
r

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
.
2

0
.
0
3
4
3

0

-

0

0

0

-

0
00
.
0
3
4
3
23
.
6
0
0
0
0
0
0

2
.
8
0
0.
0
0
1
8
7

0
.
0
3
6
2
11
.
7

1
5
.
1
4

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
Co
y
o
t
e

L
e
a
d

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
9
7

0
.
0
1
1
2

0

-

0

0

0

-

0
00
.
0
1
1
2
19
.
0
0
0
0
0
0
0

2
.
8
0
0.
0
0
1
5
0

0
.
0
1
2
7
0.
9

4
.
7

0
.
0
1
4

<
0
.
0
1

9
5
%
No
n
e
Co
y
o
t
e

M
o
l
y
b
d
e
n
u
m

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

1
.
0
0

1
.
0
0

0
.
0
0
2
8
2

0

-

0

0

0

-

0
0

0
.
0
0
2
8
2
1.
0
0

2
.
8
0
0.
0
0
0
0
7
9
0

0
.
0
0
2
9
0
0.
3

2
.
6

0
.
0
1
1

<
0
.
0
1

8
7
%
No
n
e
Co
y
o
t
e

N
i
t
r
a
t
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

1

1
0

0
.
0
2
8
2
2
6
1
2
9

0

-

0

0

0

-

0
0

0
.
0
2
8
2
2
6
1
2
9
10
.
0
0
0
0
0
0
0

2
.
8
0
0.
0
0
0
8

0
.
0
2
9
50
7
.
0

1
1
3
0

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
Co
y
o
t
e

P
e
r
c
h
l
o
r
a
t
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0
.
1
0
0

0
.
0
0
5
3
7

0
.
0
0
0
0
1
5
1

0

-

0

0

0

-

0
0

0
.
0
0
0
0
1
5
1
0.
0
5
3
7

2
.
8
0
0.
0
0
0
0
0
4
2
4

0
.
0
0
0
0
1
9
4
2.
6

2
5
.
9

<
0
.
0
1

<
0
.
0
1

3
3
%
No
n
e
Co
y
o
t
e

S
i
l
v
e
r

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0
.
8
1
0

0
.
1
4
6

0
.
0
0
0
4
1
2

0

-

0

0

0

-

0
0

0
.
0
0
0
4
1
2
0.
1
8
0

2
.
8
0
0.
0
0
0
0
1
4
2

0
.
0
0
0
4
2
6
2.
4

2
3
.
8

<
0
.
0
1

<
0
.
0
1

5
%
No
n
e
Co
y
o
t
e

Z
i
n
c

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
1
8

0
.
3
3
4

0

-

0

0

0

-

0
0
0.33
4
60
.
8
0
0
0
0
0
0

2
.
8
0
0.
0
0
4
8
0

0
.
3
3
9
16
0
.
0

3
2
0

<
0
.
0
1

<
0
.
0
1

1
0
0
%
No
n
e
Co
y
o
t
e
HI

-

I
n
o
r
g
a
n
i
c
s
0.
2
2

0
.
0
2
6
(d
e
t
s
)
No
n
e
Co
y
o
t
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0
.
6
2
9

0
.
1
1
3

0
.
0
0
0
3
2
0

0

-

0

0

0

-

0
0

0
.
0
0
0
3
2
0
0.
1
8
0

2
.
8
0
0.
0
0
0
0
1
4
2

0
.
0
0
0
3
3
4
5.
0

5
0
.
3

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Co
y
o
t
e

A
n
t
h
r
a
c
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0

0

0

-

0
00
0.
1
8
0

2
.
8
0
0.
0
0
0
0
1
4
2

0
.
0
0
0
0
1
4
2
10
0
0
.
0

N
S
V

<
0
.
0
1
--
0%
No
n
e
Co
y
o
t
e

F
l
u
o
r
a
n
t
h
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0

0

0

-

0
00
0.
1
0
7

2
.
8
0
0.
0
0
0
0
0
8
4
6

0
.
0
0
0
0
0
8
4
6
12
5
.
0

2
5
0

<
0
.
0
1

<
0
.
0
1

6
%
No
n
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
7
Pa
g
e

4

o
f

7
Ta
b
l
e

2
7
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s

W
i
t
h
i
n

H
a
b
i
t
a
t

A
r
e
a
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

H
a
b
i
t
a
t

So
i
l

E
P
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Co
y
o
t
e

F
l
u
o
r
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0

0

0

-

0
00
0.
1
8
0

2
.
8
0
0.
0
0
0
0
1
4
2

0
.
0
0
0
0
1
4
2
12
5
.
0

2
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Co
y
o
t
e

N
a
p
h
t
h
a
l
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0

0

0

-

0
00
0.
1
8
0

2
.
8
0
0.
0
0
0
0
1
4
2

0
.
0
0
0
0
1
4
2
50
.
0

1
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Co
y
o
t
e

P
h
e
n
a
n
t
h
r
e
n
e

1
0
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0

0

0

0

-

0

0

0

-

0
00
0.
1
8
0

2
.
8
0
0.
0
0
0
0
1
4
2

0
.
0
0
0
0
1
4
2
17
5
.
0

3
5
0

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Co
y
o
t
e
HI

-

P
A
H
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Co
y
o
t
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
10
.
3
3
0

0
.
0
4
5
0.
0
6
2
0.
0
0
3

1
0
0

0
.
1
2
5

0
.
1
1
2

0
.
0
0
0
3
1
7

0

-

0

0

0

-

0
0

0
.
0
0
0
3
1
7
0.
9
0
0

2
.
8
0
0.
0
0
0
0
7
1
1

0
.
0
0
0
3
8
8
0.
2

2
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

(
T
N
T
)
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
.
7
1

2
.
5
6
0.
0
6
5
4

0
.
0
6
5
4
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
0
6
6
2
0

1
.
8

0
.
9
5

0
.
0
3
7

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

3
.
1
4

4
.
7
1
0.
1
2
0

0
.
1
2
0
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
1
2
1
01
.
8
1.
7
0.
0
6
7

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

2
.
7
2
0.
0
6
9
4

0
.
0
6
9
4
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
0
7
0
1
01
.
8
1.
0
0.
0
3
9

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w
Ni
t
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
.
1
3

1
.
6
9
0.
0
4
3
2

0
.
0
4
3
2
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
0
4
4
0
0

1
.
8

0
.
6
3

0
.
0
2
4

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
RD
X
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
7
.
6
0.
9
6
0

0
.
9
6
0
1.
5
0

2
.
0
0
0.
0
0
0
7
6
5

0
.
9
6
1
01
.
8
14
0.
5
3

0
%
Un
c
e
r
t
a
i
n
Sa
g
e

S
p
a
r
r
o
w

C
a
d
m
i
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
6
9
6
0.
0
1
7
7

0
.
0
1
7
7
1.
2
3

2
.
0
0
0.
0
0
0
6
2
8

0
.
0
1
8
4
0

0
.
6
1

0
.
1
2

0
.
0
3
0

6
2
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

C
o
p
p
e
r

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
8
0.
1
7
3

0
.
1
7
3
23
.
6
0
0
0
0
0
0

2
.
0
0
0.
0
1
2
0

0
.
1
8
5
47

6
1
.
7

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

L
e
a
d

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
.
3
8
0.
0
3
5
3

0
.
0
3
5
3
19
.
0
0
0
0
0
0
0

2
.
0
0
0.
0
0
9
7
0

0
.
0
4
5
0
0

1
.
7
8

0
.
2
4

0
.
0
2
5

9
5
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

M
o
l
y
b
d
e
n
u
m

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
4
0
0

0
.
4
0
0
0.
0
1
0
2

0
.
0
1
0
2
1.
0
0

2
.
0
0
0.
0
0
0
5
1
0

0
.
0
1
0
7
4

3
5
.
3

<
0
.
0
1

<
0
.
0
1

8
7
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

P
e
r
c
h
l
o
r
a
t
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

2
8
2

1
5
.
1
0
0.
3
8
6

0
.
3
8
6
0.
0
5
3
7

2
.
0
0
0.
0
0
0
0
2
7
4

0
.
3
8
6
3

3
2
.
6

0
.
1
2

0
.
0
1
2

3
3
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Zi
n
c

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

4
7
.
2
1.20
1.20
60
.
8
0
0
0
0
0
0

2
.
0
0
0.
0
3
1
0

1
.
2
4
15

1
3
1

0
.
0
8
5

<
0
.
0
1

1
0
0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
HI

-

I
n
o
r
g
a
n
i
c
s
0.
5
6

0
.
0
8
0
(d
e
t
s
)
No
n
e
Sa
g
e

S
p
a
r
r
o
w

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
.
8
7

0
.
3
3
7
0.
0
0
8
5
9

0
.
0
0
8
5
9
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
0
8
6
8
27

2
6
9

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

A
n
t
h
r
a
c
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
7
0
7
0.
0
1
8
0

0
.
0
1
8
0
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
1
8
1
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
5
0
0

0
.
0
5
3
5
0.
0
0
1
3
6

0
.
0
0
1
3
6
0.
1
0
7

2
.
0
0
0.
0
0
0
0
5
4
6

0
.
0
0
1
4
2
32
5

N
S
V

<
0
.
0
1
--
6%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

F
l
u
o
r
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
0
1.
5
3

1
.
5
3
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

1
.
5
3
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

N
a
p
h
t
h
a
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
2
.
2

2
.
2
0
0.
0
5
6
0

0
.
0
5
6
0
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
5
6
1
27

2
6
9

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
4
0
8
0.
0
1
0
4

0
.
0
1
0
4
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
1
0
5
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
HI

-

P
A
H
s
<0
.
0
1
0
(d
e
t
s
)
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

2
.
1
1

0
.
3
7
9
0.
0
0
9
6
8

0
.
0
0
9
6
8
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
0
9
7
7
0

1
1

0
.
0
8
9

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
4
6
1

0
.
0
8
2
9
0.
0
0
2
1
1

0
.
0
0
2
1
1
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
0
2
2
1
0

1
1

0
.
0
2
0

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

3
.
5
6

0
.
0
0
2
6
7
0.
0
0
0
0
6
8
2

0
.
0
0
0
0
6
8
2
0.
0
0
0
7
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
8
3

0
.
0
0
0
0
6
8
5
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
2
7
9

0
.
0
0
0
1
8
1
0.
0
0
0
0
0
4
6
3

0
.
0
0
0
0
0
4
6
3
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
3
2

0
.
0
0
0
0
0
4
9
6
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
3
5
4

0
.
0
0
0
2
4
8
0.
0
0
0
0
0
6
3
2

0
.
0
0
0
0
0
6
3
2
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
0
6
6
8
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
2
9
8

0
.
0
0
0
2
0
8
0.
0
0
0
0
0
5
3
2

0
.
0
0
0
0
0
5
3
2
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
0
5
6
7
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
.
2
8

0
.
0
0
0
5
7
8
0.
0
0
0
0
1
4
7

0
.
0
0
0
0
1
4
7
0.
0
0
0
4
5
0

2
.
0
0
0.
0
0
0
0
0
0
2
3
0

0
.
0
0
0
0
1
5
0
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
1
2
0
0.
0
0
0
3
0
5

0
.
0
0
0
3
0
5
0.
0
0
1
4
5

2
.
0
0
0.
0
0
0
0
0
0
7
4
0

0
.
0
0
0
3
0
6
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
.
3
7

0
.
0
0
0
7
5
6
0.
0
0
0
0
1
9
3

0
.
0
0
0
0
1
9
3
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
0
2
8
1

0
.
0
0
0
0
1
9
6
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
3
-
T
r
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

5
.
8
4

0
.
0
0
6
1
4
0.
0
0
0
1
5
7

0
.
0
0
0
1
5
7
0.
0
0
1
0
5

2
.
0
0
0.
0
0
0
0
0
0
5
3
6

0
.
0
0
0
1
5
7
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
,
4
-
T
r
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
0
0
5
8
0

0
.
0
0
1
0
4
0.
0
0
0
0
2
6
6

0
.
0
0
0
0
2
6
6
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
0
0
1
1
8
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

2
.
5
7

0
.
4
6
2
0.
0
1
1
8

0
.
0
1
1
8
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
1
1
9
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

2
.
5
0

0
.
0
0
1
7
5
0.
0
0
0
0
4
4
7

0
.
0
0
0
0
4
4
7
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
4
5
1
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
2
-
D
i
c
h
l
o
r
o
p
r
o
p
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
4
5
0
0.
0
0
0
0
1
1
5

0
.
0
0
0
0
1
1
5
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
0
2
8
1

0
.
0
0
0
0
1
1
8
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
0
2
6
2

0
.
0
0
4
7
1
0.
0
0
0
1
2
0

0
.
0
0
0
1
2
0
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
0
0
2
1
2
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
1,
4
-
D
i
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
0
2
6
2

0
.
0
0
4
7
1
0.
0
0
0
1
2
0

0
.
0
0
0
1
2
0
0.
1
8
0

2
.
0
0
0.
0
0
0
0
9
1
8

0
.
0
0
0
2
1
2
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

2
-
B
u
t
a
n
o
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

4
6
.
1

0
.
2
1
0
0.
0
0
5
3
5

0
.
0
0
5
3
5
0.
0
0
4
5
5

2
.
0
0
0.
0
0
0
0
0
2
3
2

0
.
0
0
5
3
5
39

3
9
3

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
2-
H
e
x
a
n
o
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
6
.
6

0
.
0
6
4
9
0.
0
0
1
6
6

0
.
0
0
1
6
6
0.
0
0
3
9
0

2
.
0
0
0.
0
0
0
0
0
1
9
9

0
.
0
0
1
6
6
39

3
9
3

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
4-
M
e
t
h
y
l
-
2
-
p
e
n
t
a
n
o
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
9
.
9

0
.
0
6
7
6
0.
0
0
1
7
2

0
.
0
0
1
7
2
0.
0
0
3
4
0

2
.
0
0
0.
0
0
0
0
0
1
7
3

0
.
0
0
1
7
3
39

3
9
3

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

A
c
e
t
o
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

7
5
.
6

3
.
4
2
0.
0
8
7
3

0
.
0
8
7
3
0.
0
4
5
3

2
.
0
0
0.
0
0
0
0
2
3
1

0
.
0
8
7
3
39

N
S
V

<
0
.
0
1
--
13
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

B
e
n
z
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

8
.
2
6

0
.
0
0
4
7
1
0.
0
0
0
1
2
0

0
.
0
0
0
1
2
0
0.
0
0
0
5
7
0

2
.
0
0
0.
0
0
0
0
0
0
2
9
1

0
.
0
0
0
1
2
0
10

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
1
3
4

0
.
0
0
0
0
8
0
5
0.
0
0
0
0
0
2
0
6

0
.
0
0
0
0
0
2
0
6
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
0
6

0
.
0
0
0
0
0
2
3
6
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

2
.
7
9

0
.
0
0
2
9
3
0.
0
0
0
0
7
4
7

0
.
0
0
0
0
7
4
7
0.
0
0
1
0
5

2
.
0
0
0.
0
0
0
0
0
0
5
3
6

0
.
0
0
0
0
7
5
2
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Ch
l
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

7
.
8
3

0
.
0
0
7
8
3
0.
0
0
0
2
0
0

0
.
0
0
0
2
0
0
0.
0
0
1
0
0

2
.
0
0
0.
0
0
0
0
0
0
5
1
0

0
.
0
0
0
2
0
0
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
ci
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
0
.
6

0
.
0
0
6
9
1
0.
0
0
0
1
7
6

0
.
0
0
0
1
7
6
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
3
2

0
.
0
0
0
1
7
7
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
ci
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

7
.
1
1

0
.
0
0
3
9
1
0.
0
0
0
0
9
9
8

0
.
0
0
0
0
9
9
8
0.
0
0
0
5
5
0

2
.
0
0
0.
0
0
0
0
0
0
2
8
1

0
.
0
0
0
1
0
0
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
6
7
4

0
.
0
0
0
5
3
9
0.
0
0
0
0
1
3
8

0
.
0
0
0
0
1
3
8
0.
0
0
0
8
0
0

2
.
0
0
0.
0
0
0
0
0
0
4
0
8

0
.
0
0
0
0
1
4
2
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
b
r
o
m
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

1
3
.
3

0
.
0
0
9
9
7
0.
0
0
0
2
5
4

0
.
0
0
0
2
5
4
0.
0
0
0
7
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
8
3

0
.
0
0
0
2
5
5
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Di
c
h
l
o
r
o
d
i
f
l
u
o
r
o
m
e
t
h
a
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
5
8
0

0
.
0
0
0
4
3
5
0.
0
0
0
0
1
1
1

0
.
0
0
0
0
1
1
1
0.
0
0
0
7
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
8
3

0
.
0
0
0
0
1
1
5
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Et
h
y
l
b
e
n
z
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
0
6
9
0

0
.
0
0
0
0
4
1
4
0.
0
0
0
0
0
1
0
6

0
.
0
0
0
0
0
1
0
6
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
0
6

0
.
0
0
0
0
0
1
3
6
10

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
m,
p
-
X
y
l
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

3
.
0
4

0
.
0
0
3
8
0
0.
0
0
0
0
9
6
9

0
.
0
0
0
0
9
6
9
0.
0
0
1
2
5

2
.
0
0
0.
0
0
0
0
0
0
6
3
8

0
.
0
0
0
0
9
7
6
10

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

o
-
X
y
l
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

3
.
3
4

0
.
0
0
3
6
0
0.
0
0
0
0
9
1
9

0
.
0
0
0
0
9
1
9
0.
0
0
1
0
8

2
.
0
0
0.
0
0
0
0
0
0
5
5
1

0
.
0
0
0
0
9
2
5
10

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

7
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Te
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

2
.
5
2

0
.
0
0
1
6
4
0.
0
0
0
0
4
1
8

0
.
0
0
0
0
4
1
8
0.
0
0
0
6
5
0

2
.
0
0
0.
0
0
0
0
0
0
3
3
2

0
.
0
0
0
0
4
2
1
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w

T
o
l
u
e
n
e

0
.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

4
.
7
1

0
.
0
7
0
2
0.
0
0
1
7
9

0
.
0
0
1
7
9
0.
0
1
4
9

2
.
0
0
0.
0
0
0
0
0
7
6
0

0
.
0
0
1
8
0
10

1
0
1
.
7

<
0
.
0
1

<
0
.
0
1

1
3
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Tr
a
n
s
-
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

2
.
5
0

0
.
0
0
1
5
0
0.
0
0
0
0
3
8
3

0
.
0
0
0
0
3
8
3
0.
0
0
0
6
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
0
6

0
.
0
0
0
0
3
8
6
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
Tr
a
n
s
-
1
,
3
-
D
i
c
h
l
o
r
o
p
r
o
p
e
n
e
0.
0
1
9

0
.
0
2
6

1

0
.
0
2
6

0

-

0

0

0

-

0

0

1
0
0

0
.
8
1
8

0
.
0
0
0
5
7
3
0.
0
0
0
0
1
4
6

0
.
0
0
0
0
1
4
6
0.
0
0
0
7
0
0

2
.
0
0
0.
0
0
0
0
0
0
3
5
7

0
.
0
0
0
0
1
5
0
17

3
4
.
4

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Sa
g
e

S
p
a
r
r
o
w
HI

-

V
O
C
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
7
1

3
.
7
1

0
.
0
8
2
8

0

-

0
0

0
.
0
8
2
8
1.
0
0

0
0

0
.
0
8
2
8
01
.
8
1.
2
0.
0
4
6

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
1
6

4
.
7
4

0
.
1
0
6

0

-

0
0

0
.
1
0
6
1.
5
0

0
00
.
1
0
6
01
.
8
1.
5
0.
0
5
9

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
1

0
.
1
5
0

0

-

0
0

0
.
1
5
0
1.
5
0

0
00
.
1
5
0
01
.
8
2.
1
0.
0
8
3

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
9

4
.
3
2

0
.
0
9
6
5

0

-

0
0

0
.
0
9
6
5
0.
1
4
0

0
0

0
.
0
9
6
5
01
.
8
1.
4
0.
0
5
4

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
6

4
.
1
4

0
.
0
9
2
4

0

-

0
0

0
.
0
9
2
4
0.
1
5
0

0
0

0
.
0
9
2
4
01
.
8
1.
3
0.
0
5
1

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
7
.
5

5
.
2
3

0
.
1
1
7

0

-

0
0

0
.
1
1
7
0.
1
9
0

0
00
.
1
1
7
01
.
8
1.
7
0.
0
6
5

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

H
M
X

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
3
1
3

1
.
0
3

0
.
0
2
3
0

0

-

0
0

0
.
0
2
3
0
3.
3
0

0
0

0
.
0
2
3
0
9

6
2
.
5

<
0
.
0
1

<
0
.
0
1

2
0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Ni
t
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9
.
7

4
4
.
5

0
.
9
9
2

0

-

0
0

0
.
9
9
2
1.
5
0

0
00
.
9
9
2
01
.
8
14
0.
5
5

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
RD
X
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
3

1
.
9
5

0

-

0
01
.
9
5
1.
5
0

0
01
.
9
5
01
.
8
28
1.
1
0%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

E
n
e
r
g
e
t
i
c
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

C
a
d
m
i
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

9
.
7
6

0
.
2
1
8

0

-

0
0

0
.
2
1
8
1.
2
3

0
00
.
2
1
8
00
.
6
1
1.
4
0.
3
6

6
2
%
Po
s
s
i
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

C
o
p
p
e
r

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
.
3

0
.
2
7
4

0

-

0
0

0
.
2
7
4
23
.
6
0
0
0
0
0
0

0
00
.
2
7
4
47

6
1
.
7

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

L
e
a
d

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
6
6

0
.
1
9
3

0

-

0
0

0
.
1
9
3
19
.
0
0
0
0
0
0
0

0
00
.
1
9
3
01
.
7
8
1.
0
0.
1
1

9
5
%
Po
s
s
i
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

M
o
l
y
b
d
e
n
u
m

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

0
.
9
5
3

0
.
9
5
3

0
.
0
2
1
3

0

-

0
0

0
.
0
2
1
3
1.
0
0

0
0

0
.
0
2
1
3
4

3
5
.
3

<
0
.
0
1

<
0
.
0
1

8
7
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

P
e
r
c
h
l
o
r
a
t
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
0
0

0
.
0
5
3
7

0
.
0
0
1
2
0

0

-

0
0

0
.
0
0
1
2
0
0.
0
5
3
7

0
0

0
.
0
0
1
2
0
3

3
2
.
6

<
0
.
0
1

<
0
.
0
1

3
3
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

Z
i
n
c

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
2
9

7
.
3
4

0

-

0
0
7.
34
60
.
8
0
0
0
0
0
0

0
07
.
3
4
15

1
3
1

0
.
5
1

0
.
0
5
6

1
0
0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

I
n
o
r
g
a
n
i
c
s
2.
9
0.
5
3
(d
e
t
s
)
Po
s
s
i
b
l
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
9

5
.
2
3

0
.
1
1
7

0

-

0
0

0
.
1
1
7
0.
1
8
0

0
00
.
1
1
7
27

2
6
9

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

A
n
t
h
r
a
c
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
.
4
2

0
.
4
3
6

0
.
0
0
9
7
2

0

-

0
0

0
.
0
0
9
7
2
0.
1
8
0

0
0

0
.
0
0
9
7
2
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

F
l
u
o
r
a
n
t
h
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
.
0
4

0
.
3
2
5

0
.
0
0
7
2
6

0

-

0
0

0
.
0
0
7
2
6
0.
1
0
7

0
0

0
.
0
0
7
2
6
32
5

N
S
V

<
0
.
0
1
--
6%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

F
l
u
o
r
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

9
.
5
7

1
.
7
2

0
.
0
3
8
4

0

-

0
0

0
.
0
3
8
4
0.
1
8
0

0
0

0
.
0
3
8
4
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
7
Pa
g
e

5

o
f

7
Ta
b
l
e

2
7
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s

W
i
t
h
i
n

H
a
b
i
t
a
t

A
r
e
a
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

H
a
b
i
t
a
t

So
i
l

E
P
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s
So
i
l

I
n
v
e
r
t
e
b
r
a
t
e
s
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

N
a
p
h
t
h
a
l
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

4
.
4
0

0
.
7
9
2

0
.
0
1
7
7

0

-

0
0

0
.
0
1
7
7
0.
1
8
0

0
0

0
.
0
1
7
7
27

2
6
9

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

P
h
e
n
a
n
t
h
r
e
n
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

1
.
7
2

0
.
3
1
0

0
.
0
0
6
9
1

0

-

0
0

0
.
0
0
6
9
1
0.
1
8
0

0
0

0
.
0
0
6
9
1
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

P
A
H
s
<0
.
0
1
0
(d
e
t
s
)
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
TP
H
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

-

0

0

0

-

0
00
20
.
0
0
0
0
0
0
0

0
00
50
0

5
0
0
0

0

0

1
0
0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

P
e
t
r
o
l
e
u
m
00
(d
e
t
s
)
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
5
.
1

3
1
.
6

0
.
7
0
5

0

-

0
0

0
.
7
0
5
0.
9
0
0

0
00
.
7
0
5
17

3
8
.
4

0
.
0
4
2

0
.
0
1
8

0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

b
i
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

0
.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
3
.
4

2
.
7
4

0
.
0
6
1
1

0

-

0
0

0
.
0
6
1
1
0.
0
8
2
0

0
0

0
.
0
6
1
1
1

N
S
V

0
.
0
5
6
--
0%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8
.
8

6
.
9
9

0
.
1
5
6

0

-

0
0

0
.
1
5
6
0.
1
8
0

0
00
.
1
5
6
01
1
1.
4
0.
0
1
4

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
1
.
3

5
.
6
4

0
.
1
2
6

0

-

0
0

0
.
1
2
6
0.
1
8
0

0
00
.
1
2
6
01
1
1.
1
0.
0
1
1

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

2
8
.
9

5
.
2
0

0
.
1
1
6

0

-

0
0

0
.
1
1
6
0.
1
8
0

0
00
.
1
1
6
01
1
1.
0
0.
0
1
0

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8

6
.
8
5

0
.
1
5
3

0

-

0
0

0
.
1
5
3
0.
1
8
0

0
00
.
1
5
3
01
1
1.
4
0.
0
1
4

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
0
.
8

5
.
5
4

0
.
1
2
4

0

-

0
0

0
.
1
2
4
0.
1
8
0

0
00
.
1
2
4
01
1
1.
1
0.
0
1
1

0
%
Un
c
e
r
t
a
i
n
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

4
0
.
2

7
.
2
4

0
.
1
6
1

0

-

0
0

0
.
1
6
1
0.
1
8
0

0
00
.
1
6
1
1

2
.
2
5

0
.
2
9

0
.
0
7
2

0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8
.
6

6
.
9
5

0
.
1
5
5

0

-

0
0

0
.
1
5
5
0.
1
8
0

0
00
.
1
5
5
1

2
.
2
5

0
.
2
8

0
.
0
6
9

0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
6

7
.
0
2

0
.
1
5
7

0

-

0
0

0
.
1
5
7
0.
1
9
5

0
00
.
1
5
7
1

2
.
2
5

0
.
2
8

0
.
0
7
0

0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
0
4
7

0
.
0
2
2

1

0
.
0
2
2

0

-

0

0

1
0
0

3
8

6
.
8
4

0
.
1
5
3

0

-

0
0

0
.
1
5
3
0.
1
8
0

0
00
.
1
5
3
1

2
.
2
5

0
.
2
7

0
.
0
6
8

0
%
No
n
e
Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e
HI

-

S
V
O
C
s
00
(d
e
t
s
)
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
7
1

3
.
7
1

0
.
0
7
3
6

0

-

0
0

0
.
0
7
3
6
1.
0
0

2
.
0
0
0.
0
0
0
3
9
7

0
.
0
7
4
0
01
.
8
1.
1
0.
0
4
1

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
1
6

4
.
7
4

0
.
0
9
4
0

0

-

0
0

0
.
0
9
4
0
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

0
.
0
9
4
6
01
.
8
1.
4
0.
0
5
3

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

6
.
7
1

0
.
1
3
3

0

-

0
0

0
.
1
3
3
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

0
.
1
3
4
01
.
8
1.
9
0.
0
7
4

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
0
.
9

4
.
3
2

0
.
0
8
5
8

0

-

0
0

0
.
0
8
5
8
0.
1
4
0

2
.
0
0
0.
0
0
0
0
5
5
5

0
.
0
8
5
8
01
.
8
1.
2
0.
0
4
8

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
3-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
6

4
.
1
4

0
.
0
8
2
2

0

-

0
0

0
.
0
8
2
2
0.
1
5
0

2
.
0
0
0.
0
0
0
0
5
9
5

0
.
0
8
2
3
01
.
8
1.
2
0.
0
4
6

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
4-
N
i
t
r
o
t
o
l
u
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
7
.
5

5
.
2
3

0
.
1
0
4

0

-

0
0

0
.
1
0
4
0.
1
9
0

2
.
0
0
0.
0
0
0
0
7
5
4

0
.
1
0
4
01
.
8
1.
5
0.
0
5
8

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

H
M
X

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
3
1
3

1
.
0
3

0
.
0
2
0
5

0

-

0
0

0
.
0
2
0
5
3.
3
0

2
.
0
0
0.
0
0
1
3
1

0
.
0
2
1
8
9

6
2
.
5

<
0
.
0
1

<
0
.
0
1

2
0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Ni
t
r
o
b
e
n
z
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9
.
7

4
4
.
5

0
.
8
8
2

0

-

0
0

0
.
8
8
2
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

0
.
8
8
3
01
.
8
13
0.
4
9

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
RD
X
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
7
.
3

1
.
7
3

0

-

0
01
.
7
3
1.
5
0

2
.
0
0
0.
0
0
0
5
9
5

1
.
7
3
01
.
8
25
0.
9
6

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

E
n
e
r
g
e
t
i
c
s
<0
.
0
1

<
0
.
0
1

(
d
e
t
s
)
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

C
a
d
m
i
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

9
.
7
6

0
.
1
9
4

0

-

0
0

0
.
1
9
4
1.
2
3

2
.
0
0
0.
0
0
0
4
8
8

0
.
1
9
4
00
.
6
1
1.
2
0.
3
2

6
2
%
Po
s
s
i
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

C
o
p
p
e
r

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
.
3

0
.
2
4
4

0

-

0
0

0
.
2
4
4
23
.
6
0
0
0
0
0
0

2
.
0
0
0.
0
0
9
3
6

0
.
2
5
3
47

6
1
.
7

<
0
.
0
1

<
0
.
0
1

9
5
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

L
e
a
d

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

8
.
6
6

0
.
1
7
2

0

-

0
0

0
.
1
7
2
19
.
0
0
0
0
0
0
0

2
.
0
0
0.
0
0
7
5
4

0
.
1
7
9
0

1
.
7
8

0
.
9
4

0
.
1
0

9
5
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

M
o
l
y
b
d
e
n
u
m

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

0
.
9
5
3

0
.
9
5
3

0
.
0
1
8
9

0

-

0
0

0
.
0
1
8
9
1.
0
0

2
.
0
0
0.
0
0
0
3
9
7

0
.
0
1
9
3
4

3
5
.
3

<
0
.
0
1

<
0
.
0
1

8
7
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

P
e
r
c
h
l
o
r
a
t
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
0
0

0
.
0
5
3
7

0
.
0
0
1
0
6

0

-

0
0

0
.
0
0
1
0
6
0.
0
5
3
7

2
.
0
0
0.
0
0
0
0
2
1
3

0
.
0
0
1
0
9
3

3
2
.
6

<
0
.
0
1

<
0
.
0
1

3
3
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

Z
i
n
c

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
2
9

6
.
5
3

0

-

0
0
6.5
3
60
.
8
0
0
0
0
0
0

2
.
0
0
0.
0
2
4
1

6
.
5
5
15

1
3
1

0
.
4
5

0
.
0
5
0

1
0
0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

I
n
o
r
g
a
n
i
c
s
2.
6
0.
4
7
(d
e
t
s
)
Po
s
s
i
b
l
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

2
-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
9

5
.
2
3

0
.
1
0
4

0

-

0
0

0
.
1
0
4
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
1
0
4
27

2
6
9

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

A
n
t
h
r
a
c
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
.
4
2

0
.
4
3
6

0
.
0
0
8
6
4

0

-

0
0

0
.
0
0
8
6
4
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
0
0
8
7
1
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

F
l
u
o
r
a
n
t
h
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
.
0
4

0
.
3
2
5

0
.
0
0
6
4
5

0

-

0
0

0
.
0
0
6
4
5
0.
1
0
7

2
.
0
0
0.
0
0
0
0
4
2
5

0
.
0
0
6
5
0
32
5

N
S
V

<
0
.
0
1
--
6%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

F
l
u
o
r
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

9
.
5
7

1
.
7
2

0
.
0
3
4
2

0

-

0
0

0
.
0
3
4
2
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
0
3
4
2
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

N
a
p
h
t
h
a
l
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

4
.
4
0

0
.
7
9
2

0
.
0
1
5
7

0

-

0
0

0
.
0
1
5
7
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
0
1
5
8
27

2
6
9

<
0
.
0
1

<
0
.
0
1

0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

P
h
e
n
a
n
t
h
r
e
n
e

0
.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

1
.
7
2

0
.
3
1
0

0
.
0
0
6
1
4

0

-

0
0

0
.
0
0
6
1
4
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
0
0
6
2
1
32
5

N
S
V

<
0
.
0
1
--
0%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
HI

-

P
A
H
s
<0
.
0
1
0
(d
e
t
s
)
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
5
.
1

3
1
.
6

0
.
6
2
7

0

-

0
0

0
.
6
2
7
0.
9
0
0

2
.
0
0
0.
0
0
0
3
5
7

0
.
6
2
7
17

3
8
.
4

0
.
0
3
7

0
.
0
1
6

0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8
.
8

6
.
9
9

0
.
1
3
9

0

-

0
0

0
.
1
3
9
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
1
3
9
01
1
1.
3
0.
0
1
3

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
1
.
3

5
.
6
4

0
.
1
1
2

0

-

0
0

0
.
1
1
2
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
1
1
2
01
1
1.
0
0.
0
1
0

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

2
8
.
9

5
.
2
0

0
.
1
0
3

0

-

0
0

0
.
1
0
3
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
1
0
3
0

1
1

0
.
9
4

<
0
.
0
1

0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8

6
.
8
5

0
.
1
3
6

0

-

0
0

0
.
1
3
6
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
1
3
6
01
1
1.
2
0.
0
1
2

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
0
.
8

5
.
5
4

0
.
1
1
0

0

-

0
0

0
.
1
1
0
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
1
1
0
01
1
1.
0
0.
0
1
0

0
%
Un
c
e
r
t
a
i
n
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

4
0
.
2

7
.
2
4

0
.
1
4
4

0

-

0
0

0
.
1
4
4
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
1
4
4
1

2
.
2
5

0
.
2
6

0
.
0
6
4

0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
6

7
.
0
2

0
.
1
3
9

0

-

0
0

0
.
1
3
9
0.
1
9
5

2
.
0
0
0.
0
0
0
0
7
7
4

0
.
1
3
9
1

2
.
2
5

0
.
2
5

0
.
0
6
2

0
%
No
n
e
We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e
0.
1
0
3

0
.
0
2
0

1

0
.
0
2
0

0

-

0

0

1
0
0

3
8

6
.
8
4

0
.
1
3
6

0

-

0
0

0
.
1
3
6
0.
1
8
0

2
.
0
0
0.
0
0
0
0
7
1
4

0
.
1
3
6
1

2
.
2
5

0
.
2
4

0
.
0
6
0

0
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

2
,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
5

1
.
0
5

0
.
1
1
7

0

-

0

0

0

-

0
0

0
.
1
1
7
1.
0
0

5
.
0
0
0.
0
0
5
5
5

0
.
1
2
3
01
.
8
1.
8
0.
0
6
8

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
0

1
.
6
5

0
.
1
8
3

0

-

0

0

0

-

0
0

0
.
1
8
3
1.
5
0

5
.
0
0
0.
0
0
8
3
3

0
.
1
9
1
01
.
8
2.
7
0.
1
1

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
1
8

1
.
7
7

0
.
1
9
6

0

-

0

0

0

-

0
0

0
.
1
9
6
1.
5
0

5
.
0
0
0.
0
0
8
3
3

0
.
2
0
5
01
.
8
2.
9
0.
1
1

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l

H
M
X

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

2
.
1
3

7
.
0
4

0
.
7
8
2

0

-

0

0

0

-

0
0

0
.
7
8
2
3.
3
0

5
.
0
0
0.
0
1
8
3

0
.
8
0
1
9

6
2
.
5

0
.
0
8
9

0
.
0
1
3

2
0
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l
Ni
t
r
o
b
e
n
z
e
n
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
5
2
5

0
.
7
8
8

0
.
0
8
7
5

0

-

0

0

0

-

0
0

0
.
0
8
7
5
1.
5
0

5
.
0
0
0.
0
0
8
3
3

0
.
0
9
5
8
01
.
8
1.
4
0.
0
5
3

0
%
Un
c
e
r
t
a
i
n
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

E
n
e
r
g
e
t
i
c
s
0.
0
8
9

0
.
0
1
3
(d
e
t
s
)
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

C
a
d
m
i
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

0
.
7
3
9

0
.
0
8
2
0

0

-

0

0

0

-

0
0

0
.
0
8
2
0
1.
2
3

5
.
0
0
0.
0
0
6
8
3

0
.
0
8
8
9
0

0
.
6
1

0
.
5
6

0
.
1
5

6
2
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

C
o
p
p
e
r

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
2
.
2

1
.
3
5

0

-

0

0

0

-

0
01
.
3
5
23
.
6
0
0
0
0
0
0

5
.
0
0
0.
1
3
1

1
.
4
8
47

6
1
.
7

0
.
0
3
2

0
.
0
2
4

9
5
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

L
e
a
d

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

3
.
9
7

0
.
4
4
1

0

-

0

0

0

-

0
0

0
.
4
4
1
19
.
0
0
0
0
0
0
0

5
.
0
0
0.
1
0
6

0
.
5
4
6
01
.
7
8
2.
9
0.
3
1

9
5
%
Po
s
s
i
b
l
e
Bu
r
r
o
w
i
n
g

O
w
l

M
o
l
y
b
d
e
n
u
m

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

1
.
0
0

1
.
0
0

0
.
1
1
1

0

-

0

0

0

-

0
0

0
.
1
1
1
1.
0
0

5
.
0
0
0.
0
0
5
5
5

0
.
1
1
7
4

3
5
.
3

0
.
0
3
3

<
0
.
0
1

8
7
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

P
e
r
c
h
l
o
r
a
t
e

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
1
0
0

0
.
0
0
5
3
7

0
.
0
0
0
5
9
6

0

-

0

0

0

-

0
0

0
.
0
0
0
5
9
6
0.
0
5
3
7

5
.
0
0
0.
0
0
0
2
9
8

0
.
0
0
0
8
9
4
3

3
2
.
6

<
0
.
0
1

<
0
.
0
1

3
3
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l

Z
i
n
c

0
.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

R
e
g
r
e
s
s
i
o
n

B
a
s
e
d

1
1
8

1
3
.
2

0

-

0

0

0

-

0
0
13
.2
60
.
8
0
0
0
0
0
0

5
.
0
0
0.
3
3
7

1
3
.
5
0
0
15

1
3
1

0
.
9
3

0
.
1
0

1
0
0
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l
HI

-

I
n
o
r
g
a
n
i
c
s
4.
4
0.
5
8
(d
e
t
s
)
Po
s
s
i
b
l
e
Bu
r
r
o
w
i
n
g

O
w
l
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
0
5
2
7

0
.
0
0
9
4
9

0
.
0
0
1
0
5

0

-

0

0

0

-

0
0

0
.
0
0
1
0
5
0.
1
8
0

5
.
0
0
0.
0
0
1
0
0
0

0
.
0
0
2
0
5
0

1
1

0
.
0
1
9

<
0
.
0
1

0
%
No
n
e
Bu
r
r
o
w
i
n
g

O
w
l
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e
0.
1
5
7

0
.
1
1
1

1

0
.
1
1
1

1
0
0

0
.
3
2
9

0
.
0
5
9
2

0
.
0
0
6
5
7

0

-

0

0

0

-

0
0

0
.
0
0
6
5
7
0.
1
8
0

5
.
0
0
0.
0
0
1
0
0
0

0
.
0
0
7
5
7
0

1
1

0
.
0
6
9

<
0
.
0
1

0
%
No
n
e
SL
C

J
M
S

E
S
1
1
2
0
0
5
0
1
0
S
L
C
/
H
i
l
l
A
F
B
_
T
T
U
_
0
6
O
c
t
0
5
_
C
A
I
-
u
n
a
r
m
e
d
v
2
_
1
0
1
4
0
5
.
x
l
s
/
2
7
Pa
g
e

6

o
f

7
Ta
b
l
e

2
7
Re
f
i
n
e
d

R
i
s
k

E
s
t
i
m
a
t
i
o
n

f
o
r

W
i
l
d
l
i
f
e

E
x
p
o
s
e
d

t
o

S
i
t
e

S
o
i
l
s

W
i
t
h
i
n

H
a
b
i
t
a
t

A
r
e
a
s
At
t
a
c
h
m
e
n
t

1
0
A

-

T
h
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t
,

E
c
o
l
o
g
i
c
a
l

R
i
s
k

A
s
s
e
s
s
m
e
n
t
Re
c
e
p
t
o
r
Ch
e
m
i
c
a
l
Bo
d

W
e
i
g
h
t

(k
g
)
Da
i
l

F
o
o
d

In
t
a
k
e

(
k
g
/
k
g
-
b/
d
a
)
Ar
e
a

U
s
e

Fa
c
t
o
r
Da
i
l

F
o
o
d

In
g
e
s
t
i
o
n

fr
o
m

S
i
t
e

(k
g
/
k
g
-
b/
d
a
)
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

V
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
a
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n

(m
g
/
k
g

D
W
)
To
t
a
l

I
n
v
e
r
t
e
b
r
a
t
e

Fo
o
d

I
n
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
b
Pe
r
c
e
n
t

o
f

Di
e
t
So
i
l

t
o

T
i
s
s
u
e

T
r
a
n
s
f
e
r

Fa
c
t
o
r
Ti
s
s
u
e

Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
k
g

DW
)
To
t
a
l

P
l
a
n
t

F
o
o
d

In
t
a
k
e
(m
g
/
k
g
-
b

/
d
)
c
To
t
a
l

F
o
o
d

I
n
t
a
k
e

(m
g
/
k
g
-
b

/
d
)
d
Re
f
i
n
e
d

H
a
b
i
t
a
t

So
i
l

E
P
C

(
m
g
/
k
g
)
Pe
r
c
e
n
t

o
f

Di
e
t

a
s

S
o
i
l
In
c
i
d
e
n
t
a
l

S
o
i
l

In
t
a
k
e

(
m
g
/
k
g
-
b/
d
)
e
To
t
a
l

C
h
e
m
i
c
a
l

In
t
a
k
e

(
m
g
/
k
g
-
d
a

)
f
NO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
LO
A
E
L

T
R
V

(m
g
/
k
g
-
b

/
d
)
NO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
LO
A
E
L

H
a

a
r
d

Qu
o
t
i
e
n
t
De
t
e
c
t
i
o
n

Fr
e
q
u
e
n
c

(
%
)

R
i
s
k

C
o
n
c
l
u
s
i
o
n
s
Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

O
t
h
e
r

V
e
r
t
e
b
r
a
t
e
s
Te
r
r
e
s
t
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e

2
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

N
o
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

R

P
o
s
s

U

R

P
o
s
s

U

R

P
o
s
s

U
2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

R

U

N
o
n
e

R

N
o
n
e

N
o
n
e

R

U

N
o
n
e

R

N
o
n
e

N
o
n
e

R

U

N
o
n
e

P

-
-

-
-

R

U

U

R

U

U

R

U

U

R

U

U
2-
A
m
i
n
o
-
4
,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

0
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

R

U

U

R

U

U

R

U

U
2-
N
i
t
r
o
a
n
i
l
i
n
e

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
2-
N
i
t
r
o
p
h
e
n
o
l

0
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
2-
N
i
t
r
o
t
o
l
u
e
n
e

0
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

R

U

U

P

-
-

-
-
3-
N
i
t
r
o
a
n
i
l
i
n
e

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
3-
N
i
t
r
o
t
o
l
u
e
n
e

0
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

R

U

U

P

-
-

-
-
4,
6
-
D
i
n
i
t
r
o
-
2
-
m
e
t
h
y
l
p
h
e
n
o
l

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
4-
N
i
t
r
o
a
n
i
l
i
n
e

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
4-
N
i
t
r
o
p
h
e
n
o
l

0
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
4-
N
i
t
r
o
t
o
l
u
e
n
e

0
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

R

U

U

P

-
-

-
-
HM
X

3
1
%
P-
-
-
-
R
No
n
e

N
o
n
e

R
Pr
o
b
a
b
l
e
Po
s
s

R

P
o
s
s

P
o
s
s

R

P
o
s
s

P
o
s
s

R

P
o
s
s

P
o
s
s

R

N
o
n
e

N
o
n
e

R

N
o
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Ni
t
r
o
b
e
n
z
e
n
e

0
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

R

U

N
o
n
e

R

U

U

R

U

U

R

U

U
Ni
t
r
o
g
l
y
c
e
r
i
n

0
%
U

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Ni
t
r
o
g
u
a
n
i
d
i
n
e

5
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
PE
T
N

0
%
U

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Pi
c
r
i
c

a
c
i
d

7
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
RD
X

0
%
P

-
-

-
-

P

-
-

-
-

R

U

U

P

-
-

-
-

R

U

U

P

-
-

-
-

R

U

U

P

-
-

-
-

R

U

U

R

U

U

R

U

U

P

-
-

-
-
Te
t
r
y
l

0
%
P

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
HI

-

E
n
e
r
g
e
t
i
c
s
P
NA
NA
R
NA
NA
R
Pro
babl
e
Pos
s
R
Pos
s
Pos
s
R
Pos
s
Pos
s
R
Pos
s
Pos
s
R
Pos
s
Non
e
R
Non
e
Non
e
P
--

-
-
R
Pos
s
Non
e
R
Pos
s
Non
e
R
Pos
s
Non
e
Al
u
m
i
n
u
m

1
0
0
%
R
<
B
k
g

<

B
k
g

U

-
-

-
-

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

P

-
-

-
-

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g
An
t
i
m
o
n
y

7
9
%
R
Po
s
s

P
o
s
s
R
No
n
e

N
o
n
e

R

P
o
s
s

N
o
n
e

R

P
o
s
s

N
o
n
e

R

P
o
s
s

N
o
n
e

R

P
o
s
s

N
o
n
e

R
Pr
o
b
a
b
l
e
Po
s
s

R

P
o
s
s

N
o
n
e

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Ar
s
e
n
i
c

5
8
%
R
<
B
k
g

<

B
k
g
R
<
B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Ba
r
i
u
m

1
0
0
%
R
<
B
k
g

<

B
k
g
R
<
B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Be
r
y
l
l
i
u
m

4
8
%
P

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Ca
d
m
i
u
m

4
4
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R
Pr
o
b
a
b
l
e

P
r
o
b
a
b
l
e
P

-
-

-
-

P

-
-

-
-

R
Pr
o
b
a
b
l
e
Po
s
s

R
Pr
o
b
a
b
l
e
Po
s
s

R

P
o
s
s

N
o
n
e
Ca
r
b
o
n

d
i
s
u
l
f
i
d
e

5
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Ch
r
o
m
i
u
m

1
0
0
%
R
<
B
k
g

<

B
k
g
R
<
B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g
Co
b
a
l
t

7
9
%
P

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Co
p
p
e
r

8
5
%
R
Po
s
s

P
o
s
s
R
Po
s
s

P
o
s
s

R

P
o
s
s

N
o
n
e

R

N
o
n
e

N
o
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R

N
o
n
e

N
o
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R

N
o
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

N
o
n
e

N
o
n
e
Ir
o
n

1
0
0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Le
a
d

8
3
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
Po
s
s

R

P
o
s
s

N
o
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
Po
s
s

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
Po
s
s
Ma
g
n
e
s
i
u
m

1
0
0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Ma
n
g
a
n
e
s
e

1
0
0
%
R
<
B
k
g

<

B
k
g

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Me
r
c
u
r
y

2
7
%
R
<
B
k
g

<

B
k
g
R
<
B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Mo
l
y
b
d
e
n
u
m

9
1
%
R
Po
s
s

P
o
s
s

U

-
-

-
-

R

N
o
n
e

N
o
n
e

R

N
o
n
e

N
o
n
e

R

N
o
n
e

N
o
n
e

P

-
-

-
-

R

P
o
s
s

P
o
s
s

R

N
o
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Ni
c
k
e
l

1
0
0
%
R
<
B
k
g

<

B
k
g
R
<
B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Ni
t
r
a
t
e

9
2
%
U

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Pe
r
c
h
l
o
r
a
t
e

5
0
%
P-
-
-
-
R
No
n
e

N
o
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R
Pr
o
b
a
b
l
e
No
n
e

P

-
-

-
-

P

-
-

-
-

R

P
o
s
s

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Ph
o
s
p
h
o
r
u
s

1
0
0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g

R

<

B
k
g

<

B
k
g
Se
l
e
n
i
u
m

0
%
R
U

U

P

-
-

-
-

R

U

U

P

-
-

-
-

R

U

U

P

-
-

-
-

R

U

U

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Si
l
v
e
r

8
%
R
U

N
o
n
e

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

N
o
n
e

N
o
n
e

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
St
r
o
n
t
i
u
m

1
0
0
%
U

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Th
a
l
l
i
u
m

5
4
%
R
<
B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Va
n
a
d
i
u
m

1
0
0
%
R
<
B
k
g

<

B
k
g

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

<

B
k
g

<

B
k
g

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Zi
n
c

1
0
0
%
R

P
r
o
b
a
b
l
e

P
r
o
b
a
b
l
e

R
Po
s
s

P
o
s
s

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

N
o
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

R

N
o
n
e

N
o
n
e

R

N
o
n
e

N
o
n
e

R

P
o
s
s

N
o
n
e
HI

-

I
n
o
r
g
a
n
i
c
s
R
NA
NA
R
NA
NA
R
Pro
babl
e
Pos
s
R
Pro
babl
e
Non
e
R
Pro
babl
e
Pos
s
R
Pro
babl
e
Non
e
R
Pro
babl
e
Pro
babl
e
R
Pos
s
Non
e
R
Pro
babl
e
Non
e
R
Pro
babl
e
Pos
s
R
Pro
babl
e
Pos
s
R
Pro
babl
e
Pos
s
2-
M
e
t
h
y
l
n
a
p
h
t
h
a
l
e
n
e

1
4
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

R

P
o
s
s

N
o
n
e

R

P
o
s
s

N
o
n
e

R

P
o
s
s

N
o
n
e

R

P
o
s
s

N
o
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R

N
o
n
e

N
o
n
e

P

-
-

-
-

R

P
o
s
s

N
o
n
e

R

P
o
s
s

N
o
n
e

P

-
-

-
-
Ac
e
n
a
p
h
t
h
e
n
e

0
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Ace
n
a
p
h
t
h
y
l
e
n
e

0
%
R
Non
e
Non
e
R
Non
e
Non
e
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
An
t
h
r
a
c
e
n
e

7
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Be
n
z
o
(
a
)
a
n
t
h
r
a
c
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Be
n
z
o
(
a
)
p
y
r
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Be
n
z
o
(
b
)
f
l
u
o
r
a
n
t
h
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Be
n
z
o
(
g
,
h
,
i
)
p
e
r
y
l
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

R

U

N
o
n
e

R

U

N
o
n
e

R

U

N
o
n
e

R

U

N
o
n
e

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Be
n
z
o
(
k
)
f
l
u
o
r
a
n
t
h
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Ch
r
y
s
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Di
b
e
n
z
o
(
a
,
h
)
a
n
t
h
r
a
c
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Fl
u
o
r
a
n
t
h
e
n
e

4
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Fl
u
o
r
e
n
e

1
4
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

R
Pr
o
b
a
b
l
e
No
n
e

R

P
o
s
s

N
o
n
e

R

P
o
s
s

N
o
n
e

R

N
o
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
In
d
e
n
o
(
1
,
2
,
3
-
c
,
d
)
p
y
r
e
n
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Na
p
h
t
h
a
l
e
n
e

2
5
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

R

N
o
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

N
o
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Ph
e
n
a
n
t
h
r
e
n
e

1
8
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Py
r
e
n
e

0
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
HI

-

P
A
H
s
R
NA
NA
R
NA
NA
R
Pro
babl
e
Non
e
R
Pos
s
Non
e
R
Pro
babl
e
Non
e
R
Pos
s
Non
e
R
Pro
babl
e
Non
e
R
Non
e
Non
e
R
Non
e
Non
e
R
Pos
s
Non
e
R
Pos
s
Non
e
P
--

-
-
TP
H

1
0
0
%
R

P
r
o
b
a
b
l
e
No
n
e
R

P
r
o
b
a
b
l
e
No
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

P
o
s
s

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
HI

-

P
e
t
r
o
l
e
u
m
R
NA
NA
R
NA
NA
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
R
Non
e
Non
e
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
2,
4
,
5
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

0
%
R
Non
e
Non
e
R
Non
e
Non
e
P
--

-
-
P
--

-
-
R
U
Non
e
P
--

-
-
R
U
U
R
Non
e
Non
e
P
--

-
-
R
U
Non
e
R
U
Non
e
P
--

-
-
2,
4
,
6
-
T
r
i
c
h
l
o
r
o
p
h
e
n
o
l

0
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
2,
4
-
D
i
c
h
l
o
r
o
p
h
e
n
o
l

0
%
R
Non
e
Non
e
R
Non
e
Non
e
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
R
U
U
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
2,
4
-
D
i
m
e
t
h
y
l
p
h
e
n
o
l

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
2-
C
h
l
o
r
o
n
a
p
h
t
h
a
l
e
n
e

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
2-
M
e
t
h
y
l
p
h
e
n
o
l

0
%
U

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
3,
3
-
D
i
c
h
l
o
r
o
b
e
n
z
i
d
i
n
e

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
4-
C
h
l
o
r
o
-
3
-
m
e
t
h
y
l
p
h
e
n
o
l

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
4-
C
h
l
o
r
o
a
n
i
l
i
n
e

0
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
4-
M
e
t
h
y
l
p
h
e
n
o
l

0
%
U

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Be
n
z
o
i
c

a
c
i
d

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
Be
n
z
y
l
a
l
c
o
h
o
l

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
bi
s
(
2
-
E
t
h
y
l
h
e
x
y
l
)
p
h
t
h
a
l
a
t
e

1
8
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

P
o
s
s

N
o
n
e

P

-
-

-
-

P

-
-

-
-
Bu
t
y
l

b
e
n
z
y
l
p
h
t
h
a
l
a
t
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

R

U

U

R

U

N
o
n
e
Di
b
e
n
z
o
f
u
r
a
n

1
4
%
U-
-
-
-
R
No
n
e

N
o
n
e

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Di
e
t
h
y
l
p
h
t
h
a
l
a
t
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

R

U

U

R

U

N
o
n
e
Di
m
e
t
h
y
l
p
h
t
h
a
l
a
t
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

R

U

U

R

U

N
o
n
e

R

U

N
o
n
e
Di
-
n
-
b
u
t
y
l
p
h
t
h
a
l
a
t
e

0
%
P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

R

U

U

R

U

N
o
n
e
Di
-
n
-
o
c
t
y
l
p
h
t
h
a
l
a
t
e

0
%
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

R

U

U

R

U

U

R

U

N
o
n
e
He
x
a
c
h
l
o
r
o
b
e
n
z
e
n
e

0
%
R
No
n
e

N
o
n
e

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

R

U

N
o
n
e

P

-
-

-
-
He
x
a
c
h
l
o
r
o
b
u
t
a
d
i
e
n
e

4
%
P

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
He
x
a
c
h
l
o
r
o
c
y
c
l
o
p
e
n
t
a
d
i
e
n
e

0
%
R
No
n
e

N
o
n
e

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

R

U

N
o
n
e

P

-
-

-
-
He
x
a
c
h
l
o
r
o
e
t
h
a
n
e

0
%
U

-
-

-
-

U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

P

-
-

-
-

P

-
-

-
-

R

U

N
o
n
e

R

U

N
o
n
e

P

-
-

-
-
Is
o
p
h
o
r
o
n
e

0
%
U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
n-
N
i
t
r
o
s
o
-
d
i
-
n
-
p
r
o
p
y
l
a
m
i
n
e

0
%
U-
-
-
-
R
No
n
e

N
o
n
e

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
n-
N
i
t
r
o
s
o
d
i
p
h
e
n
y
l
a
m
i
n
e

0
%
U-
-
-
-
R
No
n
e

N
o
n
e

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-

U

-
-

-
-
Pe
n
t
a
c
h
l
o
r
o
p
h
e
n
o
l

0
%
R
No
n
e

N
o
n
e
R
No
n
e

N
o
n
e

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

R

U

U

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
HI

-

S
V
O
C
s
P
NA
NA
R
NA
NA
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
R
Pos
s
Non
e
P
--

-
-
P
--

-
-
1,
1
,
1
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

5
%
U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
1,
1
,
1
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

5
%
U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
1,
1
,
2
,
2
-
T
e
t
r
a
c
h
l
o
r
o
e
t
h
a
n
e

5
%
U
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
P
--

-
-
1,
1
,
2
-
T
r
i
c
h
l
o
r
o
e
t
h
a
n
e

5
%
U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

5
%
U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
1,
1
-
D
i
c
h
l
o
r
o
e
t
h
e
n
e

5
%
U

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-

P

-
-

-
-
1,
2
,
3
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b
e
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-

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-

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-
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f
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m

5
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U

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P

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-

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P

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-

-
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m
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t
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P

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-

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-

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-

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-

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-

P

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s
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c
h
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e
t
h
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e

5
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U

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-

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-

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-

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s
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c
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p
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5
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U

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b
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m
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h
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5
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U

-
-

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-

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-

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-

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b
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%
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-
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5
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h
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b
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-

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-
-

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-

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-

P

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p
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X
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e

5
%
P

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-

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-

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-

P

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-

-
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P

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-

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t
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c
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l
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5
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-

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-

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P

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-

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-

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X
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1
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P

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-

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-

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-

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To
l
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3
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P

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-

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-

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p
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p
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5
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-
-

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(
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)

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AssessmentEndpoint2-soilinvertebrates
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InsectivorousBirdFeedingGuild-loggerheadshrike
AssessmentEndpoint6-
OmnivorousBirdFeedingGuild-westernmeadowlark
AssessmentEndpoint5-
HerbivorousBirdFeedingGuild-sagesparrow
AssessmentEndpoint3-
HerbivorousMammalFeedingGuild-Ord'skangaroorat,
Townsend'sgroundsquirrel,black-tailedjackrabbit,pronghorn
AssessmentEndpoint4-
CarnivorousMammalFeedingGuild-coyote
D/
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\\Slcdb\gis\PROJECTS\HAFB\UTTR\TTU\Map_Documents\Risk_Assessments\FIG1_TTU_ERA_SITE_MAP.mxd; 10-25-05; mnl
TTU SITE MAP
FIGURE 3
ATTACHMENT 10A - THERMAL TREATMENT UNIT ECOLOGICAL RISK ASSESSMENT
¡
¡
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¡
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!
!
!
!
!
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!
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!
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!!
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!
!!!!
!
Box
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County
Road
SS-01S
SS-02S
SS-03S
SS-04S (D)
SS-05S
SS-06S (BG)
D R Y
W A S H
T T U B o u n d a r y
SS-11
TTU-2
TTU-1
Landfill 5
NR-537
NR-536
NR-535
NR-534
NR-533
NR-532
NR-531
NR-530
NR-529
NR-528
NR-527
NR-526
NR-239
NR-238
NR-237
NR-236
NR-235 NR-234
NR-232
NR-231
NR-230
NR-229
NR-227
NR-233
NR-228
NR-226
SS-3
SS-4
SS-15
SS-14
SS-12 SS-13
SS-10
SS-20
SS-19
SS-18
SS-17
SS-5
SS-6
SS-9
SS-7SS-8
SS-2
SS-16
MW-F
MW-G
MW-HMW-I
MW-J1
0 500 1,000
Feet
LEGEND
!1989 SAMPLES (Estimated)
!1991 SAMPLES (Estimated)
!2002 SAMPLES (Surveyed)
!2004 SAMPLES (Surveyed)
¡MONITORING WELL
Appendix A
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-1
A p p en d i x A : Des c r i p t i o n s o f St u d i es Us ed t o
Cal c u l at e NOA EL s an d L OA EL s
Compound: Acenaphthene
Form: Not applicable
Reference: EPA, 2001
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Exposure Duration: 90 days (t 90 days = chronic)
Endpoint: Hepatoxicity
Exposure Route: Oral gavage
Dosage: Three dose levels: 175, 350 and 700 mg/kg/d;
Calculations: Not applicable
Comments: Liver weight changes accompanied by microscopic alteration (cellular
hypertrophy) were noted in both mid- and high-does animals and seemed to be does-
dependent. Additionally, high-dose males and mid- and high-does females showed
significant increases in cholesterol levels. The LOAEL is 350 mg/kg/d based on
hepatoxicity; the NOAEL is 175 mg/kg/day.
Final NOAEL: 175 mg/kg/d
Final LOAEL: 350 mg/kg/d
Compound: Acetone
Form: not applicable
Reference: EPA, 1986c
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Food Consumption: 0.028 kg/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: 90 days (<1 yr and not during a critical lifestage=subchronic).
Endpoint: Liver and kidney damage
Exposure Route: oral intubation
Dosage: three dose levels:
100, 500, and 2500 mg/kg/d;
NOAEL = 100 mg/kg/d
LOAEL = 500 mg/kg/d
Calculations: not applicable
Comments: Significant tubular degeneration of the kidneys and increases in kidney
weights were observed at the 500 and 2500 mg/kg/d dose levels; liver weights were
increased at the 2500 mg/kg/d level. Because no significant differences were observed at
the 100 mg/kg/d dose level and the study considered exposure for 90 days and did not
include critical lifestages (reproduction), this dose was considered to be a subchronic
NOAEL. The 500 mg/kg/d dose was considered to be a subchronic LOAEL. Chronic
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-2 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
NOAEL and LOAEL values were estimated by multiplying the subchronic NOAEL and
LOAEL by a subchronic to chronic uncertainty factor of 0.1.
Final NOAEL: 10 mg/kg/d
Final LOAEL: 50 mg/kg/d
Compound: Acetone
Form:Not applicable
Reference: Hill and Camardese, 1986
Test Species: Japanese Quail
Body Weight: 0.60kg (from study)
Food Consumption: 11.8 g (from study)
Exposure Duration: acute – single dose followed by 14 day observation
Endpoint: mortality, overt signs of toxicity
Exposure Route: oral gavage
Dosage: doses ranged from 10000 to 40000 mg/kg
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
AcetonemgNOAEL 3.39360.08.1120000:¸¸¹
·¨¨©
§
Acute NOAEL: 393 mg/kg/d
Comments: No mortality observed at any dose level. LC50 of >40000mg/kg is
reported. No overt signs of toxicity at concentrations of 40000 ppm. Because no signs
of toxicity were observed at 40000 ppm, this dose was considered to be an acute
NOAEL. A chronic NOAEL was estimated by multiplying the subchronic LOAEL by
a subchronic to chronic uncertainty factor of 0.1.
Final NOAEL: 39.3 mg/kg/d
Final LOAEL: 393 mg/kg
Compound: Aluminum
Form:AlCl2
Reference: Ondreicka et al., 1966
Test Species: Mouse
Exposure Duration: 3 generations (>1 yr and during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in water
Dosage: one dose level: 19.3 mg al/kg/d = LOAEL
Calculations: not applicable
Comments: While there were no effects on the number of litters or number
of offspring per litter, growth of generation 2 and 3 was significantly reduced.
Therefore, this dose was considered to be a chronic LOAEL. A chronic NOAEL was
estimated by multiplying the chronic LOAEL by a LOAEL-NOAEL uncertainty
factor of 0.1.
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-3
Final NOAEL: 1.93 mg/kg/d
Final LOAEL: 19.3 mg/kg/d
Compound: Aluminum
Form:Al2(SO4)3
Reference: Carriere et al., 1986
Test Species: ringed dove
0.155 kg body weight (Terres, 1980)
Food consumption: 0.017 kg/d (calculated using allometric
equation from Nagy, 1987)
Exposure Duration: 4 months (>10 week and during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: one dose level: 1000 ppm Al = NOAEL
Calculations:
dkgmgBWkgg
kg
day
foodg
foodkg
AlmgNOAEL //7.109155.0/1000
1171000: ¸¸
¹
·uu¨¨
©
§
Comments: Because no significant differences were observed at the 1000
ppm dose and the study considered exposure over 4 months, including critical
lifestages (reproduction), this dose was considered to be a chronic NOAEL.
Final NOAEL: 109.7mg/kg/d
Compound: Anthracene
Form:Not applicable
Reference: IRIS, 2001
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Exposure Duration: 90 days (t 90 days = chronic)
Endpoint: Survival and pathology
Exposure Route: Oral gavage
Dosage: Three dose levels: 250, 500, and 1,000 mg/kg/d;
Calculations: Not applicable
Comments: Mortality, clinical signs, body weights, food consumption,
ophthalmology findings, hematology and clinical chemistry results, organ weights,
organ-to-body weight ratios, gross pathology, and histopathology were evaluated. No
treatment-related effects were observed at the highest dose level.
Final NOAEL: 1,000 mg/kg/d
Compound: Antimony
Form: NA
Reference: EPA, 2003 (EcoSSL)
Test Species: NA
Exposure Duration: NA
Endpoint: Growth and reproduction
Exposure Route: NA
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-4 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Dosage: NA
Calculations: NA
Comments: A total of 11 papers with 31 toxicity test results were included in the
derivation of this EcoSSL. A geometric mean of the NOAEL values for growth and
reproduction was calculated at 13.3 mg antimony/kg bw/day. However, this value is higher
than the lowest bounded LOAEL for effects on reproduction, growth, or survival. Therefore,
the TRV was considered equal to the highest bounded NOAEL below the lowest bounded
LOAEL and is equal to 0.059 mg antimony/kg bw/day.
Final NOAEL: 0.059 mg/kg/d
Compound: Aromatic Hydrocarbon (AH) Mixture
Form:Aromatics – ethylbenzene, 1,2,3,4-tetrahydronaphthalene,
dimethylnaphthalene, 2,3,3-trimethylindolenine,
acenaphthylene, acenaphthene, phenanthrene, 2-
methylbenzothiazole, dibenzothiophene, and 2,6-
dimethylquinoline
Reference: Patton and Dieter, 1980
Test Species: Mallard
Body weight: 1.23 kg (mean from control group graph in
study)
Food consumption: 100 g/d (Heinz et al., 1989)
Exposure Duration: 7 month (>10 wk = chronic)
Endpoint: growth
Exposure Route: oral diet
Dosage: three dose groups (1% mixture in diet)
10000 ppm paraffin mixture only,
9600 ppm paraffin and 400 ppm AH, and
6000 ppm paraffin and 4000 ppm AH
Calculations:
dkgmgBWkgg
kg
day
foodg
foodkg
MixAHmgNOAEL //2.32523.1/1000
11004000: ¸¸
¹
·uu¨¨
©
§
Comments: Because no adverse effects were reported for paraffin and aromatic
hydrocarbon mixtures and because no adverse effects were reported for the paraffin only
dose, a dose of 4000 ppm was considered to be a chronic NOAEL for the aromatic
hydrocarbon mixture.
Final NOAEL: 325.2 mg/kg/d
Compound: Arsenic
Form: Arsenate (H3AsO4)
Reference: Nemec et al., 1998
Test Species: rabbit
Exposure Duration: days 6-18 of gestation (critical life stage-chronic)
Endpoint: reproduction
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-5
Exposure Route: oral gavage
Dosage: 4 concentrations as arsenate (0,0.19, 0.75, and 3 mg/kg/day)
(H3AsO4is 52.78% As by weight)
Calculations: NA
Comments: Reproductive and maternal effects were observed only at the
highest dose. This resulted in mortality for 7 of 20 doses; no maternal mortality was
observed at any other doses. Number of fetuses/litter decreased and fetal
reabsorbtions increased at the highest dose, but the differences were not statistically
significant. Because the study considered exposure during a critical lifestage, the 1.58
mg/kg dose was considered to be a chronic LOAEL.
Final NOAEL: 0.396 mg/kg/d
Final NOAEL: 1.58 mg/kg/d
Compound: Arsenic
Form: Sodium arsenate
Reference: Stanley et al., 1994
Test Species: mallard
Body weight: 1 kg (Heinz et al., 1989)
Food Consumption: 0.1 kg/d (Heinz et al., 1989)
Exposure Duration: 4 wks prior to breeding, through nesting, incubation, and
hatch, to 14 d post hatch (> 10 week and during critical
lifestage=chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: 4 dose levels (As concentrations measured in food)
0.26, 22, 93, and 403 mg/kg
Calculations:
dkgmgBWkgg
kgxday
foodgxfoodkg
Asmg //026.01/1000
110026.0 ¸¸
¹
ᬬ
©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Asmg //2.21/1000
110022 ¸¸¹
·
¨¨©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Asmg //3.91/1000
110093 ¸¸¹
·
¨¨©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Asmg //3.401/1000
1100403 ¸¸
¹
·¨¨©
§
Comments: Although As did not increase duckling mortality, As at 40.3 mg/kg/d
significantly reduced duckling production. No reduction duckling production or other
adverse effects were observed at the other dose levels. Because the study considered
exposure over 10 weeks and through reproduction, the 40.3 mg/kg/d dose was considered
to be a chronic LOAEL.
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-6 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Final NOAEL: 9.3 mg/kg/d
Final LOAEL: 40.3 mg/kg/d
Compound: Barium
Form: Barium Chloride
Reference: NTP, 1994
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Water Consumption: 0.022 L/d (from study)
Study Duration: 105 weeks (> 1 year = chronic)
Endpoint: nephrotoxicity
Exposure Route: Oral in water
Dosage:Three dose levels: 500, 1,250, and 2,500 ppm Ba (as barium
chloride);
Authors calculated exposures
Males – 15, 30, and 60 mg/kg/d
Females – 15, 45, and 75 mg/kg/d
Calculations: Not applicable
Comments: Although no kidney-related lesions were observed in any treatment,
kidney weights were significantly increased in females at the 2,500 ppm level. The
2,500 ppm dose level was thus judged to represent a chronic LOAEL.
Final NOAEL: 45 mg/kg/d
Final LOAEL: 75 mg/kg/d
Compound: Barium
Form: Barium Hydroxide
Reference: Johnson et al., 1960
Test Species: 1-day old chicks
Body weight: 0.121 kg (mean for males and females at 14 d;
EPA, 1988a)
Food Consumption: 0.0126 kg/d (calculated using allometric
equation from EPA, 1988a)
Study Duration: 4 weeks (< 10 weeks = subchronic)
Endpoint: Mortality
Exposure Route: Oral in diet
Dosage:Eight dose levels: 250, 500, 1,000, 2,000, 4,000, 8,000, 16,000, and
32,000 ppm Ba (as barium hydroxide)
NOAEL = 2,000 ppm
Calculations:
dkgmgBWkgg
kgxday
foodgxfoodkg
Bamg //26.208121.0/000,1
16.12000,2 ¸¸
¹
·
¨¨
©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Bamg //53.416121.0/000,1
16.12000,4 ¨¨
©
§
¸¸
¹
·
Comments: To estimate daily Ba intake throughout the 4 week study period, food
consumption of 2-week-old chicks was calculated. While this value will over- and
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-7
underestimate food consumption by younger and older chicks, it was assumed to
approximate food consumption throughout the entire 4 week study. While Barium
exposures up to 2,000 ppm produced no mortality, chicks in the 4,000 to 32,000 ppm
groups experienced 5% to 100% mortality. Because 2,000 ppm was the highest
nonlethal dose, this dose was considered to be a subchronic NOAEL. The 4,000 ppm
dose was considered to be a subchronic LOAEL. Chronic NOAELs and LOAELs were
estimated by multiplying the subchronic NOAELs and LOAELs by a subchronic to
chronic uncertainty factor of 0.1.
Final NOAEL: 20.8 mg/kg/d
Final LOAEL: 41.7 mg/kg/d
Compound: Benzene
Form: Not applicable
Reference: Wolf et al., 1956
Test Species: Rat
Body weight: 0.175 to 0.250 kg (from study)
Exposure Duration: 187 days (t 90 days = chronic)
Endpoint: Survival and pathology
Exposure Route: Oral gavage
Dosage: Four dose levels: 1, 10 50, and 100 mg/kg/d
Calculations: Not applicable
Comments: Mortality was not reported at any dose level. Benzene at 1 mg/kg/d had
no effect, while leucopenia and erythrocytopenia was observed at 10 mg/kg/d and
higher dose levels. Therefore, 1 and 10 mg/kg/d were considered the NOAEL and
LOAEL, respectively. Dose was adjusted for gavage schedule (5 days/week) for a
NOAEL of 0.7 mg/kg/d and a LOAEL of 7 mg/kg/d.
Final NOAEL: 0.7 mg/kg/d
Final LOAEL: 7 mg/kg/d
Compound: Benzo(a)pyrene (BaP)
Form: Not applicable
Reference: Mackenzie and Angevine, 1981
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Exposure Duration: Days 7-16 of gestation (during critical lifestage = chronic)
Endpoint: Reproduction
Exposure Route: Oral intubation
Dosage: Three dose levels: 10, 40, and 160 mg/kg/d; LOAEL
Calculations: Not applicable
Comments: BaP exposure at 160 mg/kg/d significantly reduced pregnancy rates and
percentage of viable litters. Pup weights were significantly reduced by all three dose
levels. Total sterility was observed in 97% of offspring in the 40 and 160 mg/kg/d
groups and fertility was impaired among offspring in the 10 mg/kg/d group. While
the BaP exposures evaluated in this study were of a short duration, they occurred
during a critical lifestage. Therefore, the 10 mg/kg/d dose was considered to be a
chronic LOAEL. A chronic NOAEL was estimated by multiplying the chronic LOAEL
by a LOAEL-NOAEL uncertainty factor of 0.1.
Final NOAEL: 1 mg/kg/d
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-8 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Final LOAEL: 10 mg/kg/d
Compound: Bis(2-ethylhexyl) Phthalate (BEHP)
Form:Not applicable
Reference: Peakall, 1974
Test Species: Ringed Dove
Body weight: 0.155 kg (Terres, 1980)
Food consumption: 0.0127 kg/d (calculated using allometric
equation from Nagy, 1987)
Exposure Duration: 4 weeks (during critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral diet
Dosage: one dose level:
NOAEL = 10 ppm
Calculations:
dkgmgBWkgg
kg
day
foodg
foodkg
BEHPmgNOAEL //11.1155.0/1000
127.1710: ¸¸
¹
·uu¨¨
©
§
Comments: No significant reproductive effects were observed among doves on diets
containing 10 ppm Bis(2-ethylhexyl)Phthalate, and the study considered exposure over 4
weeks and during a critical lifestage. Therefore, the 10 ppm dose was considered to be a
chronic NOAEL.
Final NOAEL: 1.1 mg/kg/d
Compound: Bis(2-ethylhexyl)Phthalate (BEHP)
Form: not applicable
Reference: Lamb et al., 1987
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Food Consumption: 0.0055 kg/d
(calculated using allometric equation from EPA, 1988a)
Study Duration: 105 d (during critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: three dose levels:
0.01%, 0.1% and 0.3% of diet;
NOAEL = 0.01% = 100 mg/kg
LOAEL = 0.1% = 1000 mg/kg
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
BEHPmgNOAEL 33.1803.05.5100:¸¸¹
·¨¨©
§
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-9
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
BEHPmgLOAEL 3.18303.05.51000:¸¸¹
·¨¨©
§
Comments: While significant reproductive effects were observed among mice on diets
containing 0.1% and 0.3% Bis(2-ethylhexyl)Phthalate, no adverse effects were observed
among the 0.01% dose group. Because the study considered exposure during critical
lifestage, the 0.01% dose was considered to be a chronic NOAEL. The 0.1% dose was
considered to be a chronic LOAEL.
Final NOAEL: 18.3 mg/kg/d
Final LOAEL: 183 mg/kg/d
Coompound: Cadmium
Form: NA
Reference: EPA, 2003 (EcoSSL)
Test Species: NA
Exposure Duration: NA
Endpoint: Growth and reproduction
Exposure Route: NA
Dosage: NA
Calculations: NA
Comments: A literature search was completed and 145 papers with
mammalian toxicity data met the search criteria and were used to calculate the EcoSSL. A
geometric mean of the NOAEL values for reproduction and growth was calculated at 1.86
mg /kg bw/day. However, this value is higher than the lowest bounded LOAEL for
reproduction, growth, or mortality results. Therefore, the EcoSSL is equal to the highest
bounded NOAEL below the lowest bounded LOAEL for reproduction, growth, or survival,
and is equal to 0.770 mg cadmium/kg bw/day.
Final NOAEL: 0.77 mg/kg/d
Compound: Cadmium
Form: Cd SO4
Reference: Leach et al., 1979
Test Species: white leghorn chickens
Body weight: 1.55 kg (from EPA, 1988)
Food Consumption: 0.077 kg/d (from study)
Study Duration: 1 year and during a critical lifestage =chronic
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: four dose level:
0.22, 3.22, 12.22, and 48.22 mg/kg Cd
Calculations:
mg/kg/d0.011=BWkg1.55/day
foodkg0.077xfoodkg
Cdmg0.22 ¸¸¹
·¨¨©
§
mg/kg/d0.16=BWkg1.55/day
foodkg0.077xfoodkg
Cdmg3.22 ¸¸¹
·¨¨©
§
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-10 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
mg/kg/d0.61=BWkg1.55/day
foodkg0.077xfoodkg
Cdmg12.22 ¸¸¹
·¨¨©
§
mg/kg/d2.4=BWkg1.55/day
foodkg0.077xfoodkg
Cdmg48.22 ¸¸¹
·¨¨©
§
Comments: Although egg weight and egg shell thickness was not affected by any diet,
egg production was significantly reduced by among hens consuming diets containing 12
and 48 mg/kg Cd. Because the study considered exposure over 1 year, the 3.22 mg/kg Cd
diet was considered to be a chronic NOAEL and the 12.22 mg/kg diet was considered to be
a chronic LOAEL.
Final NOAEL: 0.16 mg/kg/d
Final LOAEL: 0.61 mg/kg/d
Compound: Carbon Tetrachloride
Form: not applicable
Reference: Alumot et al., 1976a
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Food Consumption: 0.028 kg/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: 2 yr (>1 yr and during a critical lifestage = chronic).
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: two dose levels:
80 and 200 ppm;
No effects observed at either dose level.
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
CClmgNOAEL 1635.0284200:¸¸¹
·¨¨©
§
Comments: Because no significant differences were observed at either dose level and
the study considered exposure throughout 2 years including critical lifestages
(reproduction), the maximum dose was considered to be a chronic NOAEL.
Final NOAEL: 16 mg/kg/d
Compound: Chloroform
Form: not applicable
Reference: Palmer et al., 1979
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Study Duration: 13 wk (<1 yr and not during a critical lifestage = subchronic).
Endpoint: liver, kidney, gonad condition
Exposure Route: oral intubation
Dosage: four dose levels:
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-11
15, 30, 150, and 410 mg/kg/d; NOAEL = 150 mg/kg/d
Calculations: not applicable
Comments: Gonadal atrophy was observed among male and female rats receiving
410 mg/kg/d; therefore 150 mg/kg/d was considered to be a
subchronic NOAEL. The 410 mg/kg/d dose was considered to be a
subchronic LOAEL. To estimate the chronic NOAEL and LOAEL, the
subchronic values was multiplied by a subchronic-chronic uncertainty
factor of 0.1.
Final NOAEL: 15 mg/kg/d
Final LOAEL: 41 mg/kg/d
Compound: Chromium
Form: Cr+6 as K2Cr2O4
Reference: MacKenzie et al., 1958
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Water Consumption: 0.046 L/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: 1 yr
Endpoint: body weight and food consumption
Exposure Route: oral in water
Dosage: six dose levels:
0.45, 2.2, 4.5, 7.7, 11.2, and 25 ppm Cr+6 in water
No effects observed at any dose level
Calculations:
mg/kg/d=BWkg/day
waterLxwaterL
CrmgNOAEL 28.335.0046.025:¸¸
¹
·
¨¨
©
§
Comments: Because no significant differences were observed at any dose level
studied and the study considered exposure over 1 year, the maximum
dose was considered to be a chronic NOAEL.
Final NOAEL: 3.28 mg/kg/d
Compound: Chromium
Form: Cr+6
Reference: Steven et al., 1976 (cited in Eisler, 1986)
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Water Consumption: 0.046 L/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: 3 months (<1 yr = subchronic)
Endpoint: mortality
Exposure Route: oral in water
Dosage: two dose levels:
134 and 1000 ppm Cr+6 in water; 1000 ppm = LOAEL
Calculations:
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-12 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
mg/kg/d=BWkg/day
waterLx waterL
mgCrLOAEL 4.13135.0046.01000:¸¸¹
·¨¨©
§
Comments: Because the 1000 ppm dose was identified as the toxicity threshold,
this dose was considered to be a subchronic LOAEL. A chronic
LOAEL was estimated by multiplying the subchronic LOAEL by a
subchronic-chronic uncertainty factor of 0.1.
Final LOAEL: 13.14 mg/kg/d
Compound: Chromium
Form: Cr+3 as CrK(SO4)2
Reference: Haseltine et al. , 1985
Test Species: Black duck
Body weight: 1.25 kg (meanmale+female; Dunning, 1993)
Food Consumption: Congeneric Mallard ducks, weighing 1 kg
consume 100 g food/d (Heinz et al.1989). Therefore, it was assumed
that a 1.25 kg black duck would consume 125 g food/d.
Study Duration: 10 mo. (>10 weeks and during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: two dose levels:
10 and 50 ppm Cr+3 in diet; NOAEL = 10 ppm
NOAEL = dkgmgBWkgg
kgxday
foodgxfoodkg
Crmg //125.1/1000
1125103
¸¸
¹
·
¨¨
©
§
LOAEL = dkgmgBWkgg
kgxday
foodgxfoodkg
Crmg //525.1/1000
1125503
¸¸
¹
·
¨¨
©
§
Comments: While duckling survival was reduced at the 50 ppm dose level, no
significant differences were observed at the 10 ppm Cr+3 dose level.
Because the study considered exposure throughout a critical lifestage
(reproduction), the dose 50 ppm dose was considered to be a chronic
LOAEL and the dose 10 ppm dose was considered to be a chronic
NOAEL.
Final NOAEL: 1 mg/kg/d
Final LOAEL: 5 mg/kg/d
Compound: Cobalt
Form: CoCl2 - Cobalt (II) chloride
Reference: Paternain et al., 1988
Test Species: Rat
240-280 g (260 g average body weight in this study)
Study Duration: Days 6-15 gestation (during critical lifestage = chronic)
Endpoint: Reproduction and development
Exposure Route: oral gavage
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-13
Dosage: 3 doses 25, 50, 100 mg/kg (CoCL2); 45.4 % Co.
Calculations: NA
Comments: Significant reduction in weight gain and food consumption in
addition to negative blood chemistry changes in mothers dosed 100
mg/kg/d. No significant teratogenic effects were observed; however,
increased incidence of stunted fetuses/litter occurred at 50 and 100
mg/kg/d doses. An uncertainty factor of 0.1 was applied to the
chronic LOAEL to determine a chronic NOEAL.
Final NOAEL: 1.35 mg/kg/d
Final LOAEL: 11.35 mg/kg/d
Compound: Copper
Form: Copper Sulfate
Reference: Aulerich et al., 1982
Test Species: Mink
Body weight: 1.0 kg (EPA, 1993e)
Food Consumption: 0.137 kg/d (Bleavins and Aulerich, 1981)
Study Duration: 357 d (during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: four dose levels:
25, 50, 100, and 200 ppm Cu supplemental + 60.5 ppm Cu
in base feed; NOAEL = 85.5 ppm Cu (supplement + base)
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
CumgNOAEL 71.110.11375.85:¸¸¹
·¨¨©
§
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
CumgLOAEL 14.150.11375.110:¸¸¹
·¨¨©
§
Comments: Consumption of 50, 100, and 200 ppm supplemental Cu increased the
percentage mortality of mink kits. Kit survivorship among the 25 ppm
supplemental Cu group was actual greater than the controls. Because
this study was approximately one year in duration and considered
exposure during reproduction, the 25 ppm supplemental Cu (85.5
ppm total Cu) dose was considered to be a chronic NOAEL and the 50
ppm supplemental Cu (110.5 ppm total Cu) dose was considered to
be a chronic NOAEL
Final NOAEL: 11.7 mg/kg/d
Final LOAEL: 15.14 mg/kg/d
Compound: Copper
Form: Copper oxide
Reference: Mehring et al., 1960
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-14 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Test Species: 1 day old chicks
Body weight: 0.534 kg (mean male+female at 5 weeks; EPA, 1988)
food consumption: 0.044 kg/d (calculated using allometric
equation from EPA, 1988)
Exposure Duration: 10 weeks (10 weeks = chronic).
Endpoint: growth, mortality
Exposure Route: oral in diet
Dosage: 12 dose levels:
26, 36.8, 52.0, 73.5, 104.0, 147.1, 208.0, 294.1, 403, 570, 749, and
1180 ppm total Cu; NOAEL = 570 ppm total Cu
Calculations:
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //14.2534.0/1000
14426 ¸¸
¹
ᬬ
©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //03.3534.0/1000
1448.36 ¸¸
¹
ᬬ
©
§
mg/kg/d4.28=BWkg0.534/g1000
kg1xday
foodg44xfoodkg
Cumg52 ¸¸¹
·¨¨©
§
mg/kg/d6.06=BWkg0.534/g1000
kg1xday
foodg44xfoodkg
Cumg73.5 ¸¸¹
·¨¨©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //12.12534.0/1000
1441.147 ¸¸¹
·
¨¨©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //14.17534.0/1000
144208 ¸¸¹
·
¨¨©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //23.24534.0/1000
1441.294 ¸¸
¹
·¨¨©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //21.33534.0/1000
144403 ¸¸
¹
ᬬ
©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //97.46534.0/1000
144570 ¸¸¹
·
¨¨©
§
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-15
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //7.61534.0/1000
144749 ¸¸¹
·¨¨©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
Cumg //22.97534.0/1000
1441180 ¸¸¹
·
¨¨©
§
Comments: While consumption of Cu up to 570 ppm had no effect of growth of chicks,
749 ppm Cu in the diet reduced growth by over 30% and produced 15% mortality. Because
this study was 10 weeks in duration, the 570 and 749 ppm Cu doses were considered to be a
chronic NOAEL and LOAEL, respectively. To estimate daily Cu intake throughout the
10 week study period, food consumption of 5-week-old chicks was calculated. While this
value will over- and underestimate food consumption by younger and older chicks, it was
assumed to approximate food consumption throughout the entire 10 week study.
Final NOAEL: 47 mg/kg/d
Final LOAEL: 61.7 mg/kg/d
Compound: o-Cresol (2-methylphenol)
Form: Not applicable
Reference: Hornshaw et al., 1986
Test Species: Mink
Body weight: 0.958 kg (mean of control females from study)
Food Consumption: 204 g/d (mean of all test groups in study
because no differences among groups).
Study Duration: 6 months (during a critical lifestage = chronic)
Endpoint: Reproduction
Exposure Route: Oral in diet
Dosage: Three dose levels: 100, 400, and 1,600 ppm
Calculations:
dkgmgBWkgg
kg
day
foodg
foodkg
cresolomgNOAEL //340958.0/000,1
1204600,1: ¸¸
¹
·uu¨¨
©
§
Comments: No adverse effects were observed at any dose level. Because this study
considered exposure during reproduction, the maximum dose was considered to be a
chronic NOAEL.
Final NOAEL: 340 mg/kg/d
Compound: 1,2-Dichloroethane
Form: Not applicable
Reference: Alumot et al., 1976b
Test Species: Chicken
Body weight: 1.6 kg (meanmale+female from study)
Food Consumption: 0.11 kg/d (calculated using allometric equation
from EPA, 1988)
Study Duration: 2 yr (>10 weeks and during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: two dose levels:
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-16 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
250 and 500 ppm; NOAEL = 250 ppm
dkgmgBWkgg
kgxday
foodgxfoodkg
haneDichloroetmgNOAEL //2.176.1/1000
11102,1250 ¸¸
¹
·
¨¨
©
§
dkgmgBWkgg
kgxday
foodgxfoodkg
haneDichloroetmgLOAEL //4.346.1/1000
11102,1500 ¸¸
¹
·
¨¨
©
§
Comments: While egg production was reduced at the 500 ppm dose level, no significant
differences were observed at the 250 ppm dose level. Because the study considered exposure
throughout 2 years including critical lifestages (reproduction), these doses were considered
to be chronic NOAELs and LOAELs.
Final NOAEL: 17.2 mg/kg/d
Final LOAEL: 34.4 mg/kg/d
Compound: 1,2,-Dichloroethane
Form: not applicable
Reference: Lane et al., 1982
Test Species: Mouse
Body weight: 0.035 kg (from study)
Water Consumption: 6 mL/d (from study)
Study Duration: 2 generations (>1 yr and during a critical lifestage = chronic).
Endpoint: reproduction
Exposure Route: oral in water
Dosage: three dose levels:
5, 15, and 50 mg/kg/d
No effects observed at any dose level.
Calculations: not applicable
Comments: Because no significant differences were observed at any dose level and the
study considered exposure throughout 2 generations including critical lifestages
(reproduction), the maximum dose was considered to be a chronic NOAEL.
Final NOAEL: 50 mg/kg/d.
Compound: 1,1-Dichloroethylene
Form: not applicable
Reference: Quast et al., 1983
Test Species: dog (beagle)
Body weight: 10 kg (EPA, 1988a)
Study Duration: 97 d (<1 yr and not during a critical lifestage = subchronic).
Endpoint: mortality, body weight, blood chemistry, liver histology
Exposure Route: daily oral capsules
Dosage: three dose levels:
6.25, 12.5, and 25 mg/kg/d; NOAEL = 25 mg/kg/d
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-17
Calculations: not applicable
Comments: No adverse effects were observed among any of the treatments, therefore
the maximum dose, 25 mg/kg/d was considered a subchronic NOAEL. A chronic NOAEL
was estimated by multiplying the subchronic NOAEL by a subchronic-chronic uncertainty
factor of 0.1.
Final NOAEL: 2.5 mg/kg/d
Compound: 1,2-Dichloroethylene
Form: not applicable
Reference: Bannes et al., 1985
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Study Duration: 90 d (<1 yr and not during a critical lifestage = subchronic).
Endpoint: body and organ weights, blood chemistry, hepatic function
Exposure Route: oral in water
Dosage: three dose levels:
16.8, 175, and 387 mg/kg/d (Males)
22.6, 224, and 452 mg/kg/d (Females)
NOAEL = 452 mg/kg/d
Calculations: not applicable
Comments: Exposure to 387 mg/kg/d 1,2-ichloroethylene reduced glutathione
levels in males and all dose levels reduced aniline hydroxylase
activity in females. No other treatment effects were observed. Because
the relationship of enzyme levels to potential population effects is
unknown and no other effects were observed, the maximum dose, 452
mg/kg/d was considered a subchronic NOAEL. To estimate the
chronic NOAEL, the subchronic NOAEL was multiplied by a
subchronic-chronic uncertainty factor of 0.1.
Final NOAEL: 45.2 mg/kg/d
Compound: Diethylphthalate (DEP)
Form: not applicable
Reference: Lamb et al., 1987
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Food Consumption: 0.0055 kg/d
(calculated using allometric equation from EPA, 1988a)
Study Duration: 105 d (during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: three dose levels:
0.25%, 1.25% and 2.5% of diet;
NOAEL = 2.5% = 25000 mg/kg
Calculations:
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-18 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
mgmgNOAEL 458303.05.525000:¸¸¹
·¨¨©
§
Comments: No significant reproductive effects were observed among mice in any
of the treatment groups. Because the study considered exposure
during a critical lifestage, the maximum dose was considered to be a
chronic NOAEL.
Final NOAEL: 4583 mg/kg/d
Compound: Di-n-butyl phthalate (DBP)
Form: not applicable
Reference: Lamb et al., 1987
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Food Consumption: 0.0055 kg/d
(calculated using allometric equation from EPA, 1988a)
Study Duration: 105 d (during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: three dose levels:
0.03%, 0.3% and 1% of diet;
NOAEL = 0.3% = 3000 mg/kg
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
DBPmgNOAEL 55003.05.53000:¸¸¹
·¨¨©
§
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
DBPmgLOAEL 183303.05.510000:¸¸¹
·¨¨©
§
Comments: While significant reproductive effects (reduced litters/pair, live
pups/litter, etc.) were observed among mice on diet containing 1%
DBP, no adverse effects were observed among either the 0.03% or
0.3% dose groups. Because the study considered exposure during a
critical lifestage, these doses were considered to be chronic NOAELs
and LOAELs.
Final NOAEL: 550 mg/kg/d
Final LOAEL: 1833 mg/kg/d
Compound: Di-n-butyl Phthalate (DBP)
Form:Not applicable
Reference: Peakall, 1974
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-19
Test Species: Ringed Dove
Body weight: 0.155 kg (Terres, 1980)
Food consumption: 0.0127 kg/d (calculated using allometric
equation from Nagy, 1987)
Exposure Duration: 4 weeks (during critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral diet
Dosage: one dose level:
LOAEL = 10 ppm
Calculations:
dkgmgBWkgg
kg
day
foodg
foodkg
DBPmgLOAEL //11.1155.0/1000
127.1710: ¸¸
¹
·uu¨¨
©
§
Comments: Eggshell thickness and water permeability of the shell was reduced
among doves on diets containing 10 ppm DBP. Because the study considered exposure
during a critical lifestage, the 10 ppm dose was considered to be a chronic LOAEL. A chronic
NOAEL was estimated by multiplying the chronic LOAEL by a LOAEL-NOAEL uncertainty
factor of 0.1.
Final NOAEL: 0.11 mg/kg/d
Final LOAEL: 1.1 mg/kg/d
Compound: Ethylbenzene
Form: Not applicable
Reference: Wolf et al., 1956
Test Species: Rat
Body weight: 0.175 to 0.250 kg (from study)
Exposure Duration: 182 days (t 90 days = chronic)
Endpoint: Survival and pathology
Exposure Route: Oral gavage
Dosage: Four dose levels: 13.6, 136, 408, and 680 mg/kg/d
Calculations: Not applicable
Comments: Mortality was not reported at any dose level. Ethylbenzene at 136
mg/kg/d had no effect, while histopathological changes in the liver and kidney
were observed at 408 mg/kg/d and 680 mg/kg/d. Therefore, 136 mg/kg/d and 408
mg/kg/d were considered the NOAEL and LOAEL, respectively. Dose was adjusted
for gavage schedule (5 days/week) for a NOAEL of 97.1 mg/kg/d and a LOAEL of
291 mg/kg/d.
Final NOAEL: 291 mg/kg/d
Final LOAEL: 97.1 mg/kg/d
Compound: Fluoranthene
Form:Not applicable
Reference: IRIS, 2001
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-20 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Exposure Duration: 13 weeks (t 90 days = chronic)
Endpoint: Nephropathy
Exposure Route: Oral gavage
Dosage: Three dose levels: 125, 250, and 500 mg/kg/d;
Calculations: Not applicable
Comments: All treated mice exhibited nephropathy, increased salivation, and
increased liver enzyme levels in a dose-dependent manner. Mice exposed to 250 and
500 mg/kg/d had statistically increased SGPT values and increased absolute and
relative liver weights. Compound-related microscopic liver lesions (indicated by
pigmentation) were observed in 65 and 87.5% of the mid-and high-dose mice
respectively.
Final NOAEL: 125 mg/kg/d
Final LOAEL: 250 mg/kg/d
Compound: Fluorene
Form:Not applicable
Reference: IRIS, 2001
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Exposure Duration: 13 weeks (t 90 days = chronic)
Endpoint: Hematoxicity
Exposure Route: Oral gavage
Dosage: Three dose levels: 125, 250, and 500 mg/kg/d;
Calculations: Not applicable
Comments: A significant decrease in red blood cell count and packed cell volume
were observed in females treated with 250 mg/kg/d and in males and females
treated at 500 mg/kg/d.
Final NOAEL: 125 mg/kg/d
Final LOAEL: 250 mg/kg/d
Compound: Hexachlorobenzene (BHC mixed isomers)
Form: not applicable
Reference: Grant et al., 1977
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Food Consumption: 0.028 kg/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: 4 generations (>1 yr and during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: seven dose levels:
10, 20, 40, 80, 160, 320, and 640 ppm; NOAEL = 20 ppm
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
BHCmgNOAEL 6.135.02820:¸¸¹
·¨¨©
§
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-21
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
BHCmgLOAEL 2.335.02840:¸¸¹
·¨¨©
§
Comments: Consumption of 320 ppm and 640 ppm BHC in the diet increased
maternal mortality, 80 - 640 ppm BHC reduced litter sizes, and 40 -
320 ppm BHC reduced birth weights. Because no significant effects
were observed in groups consuming 10 or 20 ppm BHC in their diet
and the study considered exposure throughout four generations
including critical lifestages (reproduction), the 20 ppm dose was
considered to be a chronic NOAEL. The lowest dose to produce an
adverse effect (40 ppm) was considered a chronic LOAEL.
Final NOAEL: 1.6 mg/kg/d
Final LOAEL: 3.2 mg/kg/d
Compound: JP-8 Jet Fuel
Form: Not applicable
Reference: Cooper and Mattie, 1996
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Study Duration: Gestational days 6-15 (during a critical lifestage = chronic)
Endpoint: Reproduction
Exposure Route: Oral gavage
Dosage: Four dose levels: 500, 1,000, 1,500, 2,000 mg JP-8 jet fuel/kg/d
Calculations: Not applicable
Comments: Maternal and fetal weight gain were significantly reduced in rats dosed
by oral gavage at the rate of 1500 mg/kg/day. Additionally, a dose-response
increase in mortality was also reported. Because no significant differences were
observed at the two lower dose levels and the study considered exposure
throughout a critical lifestage (reproduction), the 1,000 mg/kg/day dose was
considered to be a chronic NOAEL and the 1,500 mg/kg/day dose was considered
to be a chronic LOAEL
Final NOAEL: 1000 mg/kg/d
Final LOAEL: 1500 mg/kg/d
Compound: Lead
Form: Lead acetate
Reference: Edens and Garlich, 1983
Test Species: Japanese Quail
Body weight: 0.15 kg (from study)
Food Consumption: 0.031 kg/d (from study)
Exposure Duration: 5 weeks (during a critical lifestage = chronic).
Endpoint: Reproduction
Exposure Route: Oral in diet
Dosage: Four dose levels: 0, 1, 10, and 100 ppm Pb; NOAEL = 1 ppm Pb
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-22 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Exposures also reported as metabolic mass-based doses: 0.12,
1.11, and 9.69 mg Pb/BW0.75/d
Doses in mg/kg/d calculated by multiplying each metabolic
mass-based dose by ratio of dose-level-specific body mass (kg;
from study) to dose-level-specific metabolic mass (kg0.75)
resulting in the following doses: 0.19, 1.78, and 15.65 mg/kg/d
Comments: While egg production was significantly reduced among birds
consuming the 10 and 100 ppm Pb, egg production was not affected by the 1 ppm Pb
dose. Because the study considered exposure throughout a critical lifestage
(reproduction), these values were considered to be chronic LOAELs and NOAELs.
Final NOAEL: 0.19 mg/kg/d
Final LOAEL: 1.78 mg/kg/d
Compound: Manganese
Form: Manganese Oxide (Mn3O4)
Reference: Laskey et al., 1982
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Food Consumption: 0.028 kg/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: through gestation for 224 d
(during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: three dose levels:
350, 1050, and 3500 ppm supplemented Mn + 50 ppm Mn in base diet;
NOAEL = 1100 ppm
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
MnmgNOAEL 8835.0281100:¸¸¹
·¨¨©
§
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
MnmgLOAEL 28435.0283550:¸¸¹
·¨¨©
§
Comments: While the pregnancy percentage and fertility among rats consuming 3550
ppm Mn in their diet was significantly reduced, all other reproductive
parameters (e.g., litter size, ovulations, resorptions, preimplantation
death, fetal weights) were not affected. No effects were observed at lower
Mn exposure levels. Therefore the 1100 ppm Mn dose was considered to
be a chronic NOAEL and the 3550 ppm Mn dose was considered to be a
chronic LOAEL.
Final NOAEL: 88 mg/kg/d
Final LOAEL: 284 mg/kg/d
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-23
Compound: Manganese
Form: Manganese oxide (Mn3O4)
Reference: Laskey and Edens, 1985
Test Species: Japanese Quail (maless only, starting at 1 day old)
Body weight: 0.072 kg (for 3 wk-old male quail; Shellenberger, 1978)
Study Duration: 75 d (>10 weeks = chronic)
Endpoint: growth, aggressive behavior
Exposure Route: oral in diet
Dosage: one dose level:
5000 ppm supplemented Mn + 56 ppm Mn in base diet = NOAEL
Calculations: NA
Comments: While no reduction in growth was observed, aggressive behavior was 25%
to 50% reduced relative to controls. Daily Mn consumption was reported to range from
575 mg/kg/day for adults at the end of the study and 977 mg/kg/d for 20 d-old birds.
Because the study was >10 weeks in duration, the 977 mg/kg/d dose was considered to be a
chronic NOAEL based on a growth endpoint and a chronic LOAEL based on a behavior
endpoint. A chronic behavior NOAEL was estimated by applying an LOAEL-NOAEL UF of
0.1
Final NOAELgrowth: 977 mg/kg/d
Final NOAELbehavior: 98 mg/kg/d
Final LOAELbehavior: 977 mg/kg/d
Compound: Mercury
Form: Methyl Mercury Chloride (CH3HgCl; 79.89% Hg)
Reference: Verschuuren et al., 1976
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Food Consumption: 0.028 kg/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: 3 generations (>1 yr and during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: three dose levels:
0.1, 0.5, and 2.5 ppm Methyl Mercury Chloride;
NOAEL = 0.5 ppm Methyl Mercury Chloride
0.7989 ´ 0.5 mg/kg = 0.399 mg Hg /kg
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
HgmgNOAEL 032.035.028399.0:¸¸¹
·¨¨©
§
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
HgmgLOAEL 16.035.02899725.1:¸¸¹
·¨¨©
§
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-24 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Comments: While exposure to 2.5 ppm methyl mercury chloride reduced pup viability,
adverse effects were not observed at lower doses. Because significant effects were not
observed at the 0.5 ppm Methyl Mercury Chloride dose level, this dose was considered to be
a chronic NOAEL. The 2.5 ppm Methyl Mercury Chloride dose level was considered to be a
chronic LOAEL.
Final NOAEL: 0.032 mg/kg/d
Final LOAEL: 0.16 mg/kg/d
Compound: Mercury
Form: methyl mercury chloride/dicyandiamide
Reference: Heinz (1976) and Heinz and Hoffman (1998)
Test Species: mallard
Body weight: 1 kg (Heinz et al., 1987)
Food Consumption: 0.128 kg/d (from Heinz, 1979)
Exposure Duration: 2 generations (lowest doses), 2.5 months (highest dose)
(during a critical lifestage = chronic).
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: four dose levels:
0, 0.53, 2.88, and 9.2 ppm Hg
Calculations:
dkgmgBWkgday
foodkg
foodkg
Hgmg //068.01/128.053.0 ¸¸¹
·u¨¨
©
§
dkgmgBWkgday
foodkg
foodkg
Hgmg //37.01/128.088.2 ¸¸¹
·u¨¨
©
§
dkgmgBWkgday
foodkg
foodkg
Hgmg //18.11/128.02.9 ¸¸¹
·u¨¨
©
§
Comments: Although duckling survival at 7 days was significantly reduced at the two
highest dose levels, no significant difference was observed at the 0.068 mg/kg/d dose.
Because exposure occurred during reproduction, the 0.37 mg/kg/d dose was considered to
be a chronic LOAEL.
Final NOAEL: 0.068 mg/kg/d
Final LOAEL: 0.37 mg/kg/d
Compound: Methylene Chloride
Form: not applicable
Reference: NCA, 1982
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Study Duration: 2 yrs (>1 yr=chronic)
Endpoint: liver histology
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-25
Exposure Route: oral in water
Dosage: four dose levels:
5.85, 50, 125, and 250 mg/kg/d; NOAEL = 5.85 mg/kg/d
Calculations: not applicable
Comments: While Methylene Chloride at 50 mg/kg/d or greater produced
histological changes in the liver, no effects were observed at the 5.85
mg/kg/d dose level. Because the study was 2 yrs in duration, the 5.85
mg/kg/d dose was considered to be a chronic NOAEL. The 50
mg/kg/d dose was considered to be a chronic LOAEL.
Final NOAEL: 5.85 mg/kg/d
Final LOAEL: 50 mg/kg/d
Compound: 4-Methyl 2-Pentanone (Methyl Isobutyl Ketone)
Form: not applicable
Reference: Microbiological Associates, 1986 (obtained from Health Effects Assessment
Summary Tables (HEAST; EPA, 1993f)
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Study Duration: 13 weeks
(<1 yr and not during a critical lifestage=subchronic)
Endpoint: Liver and kidney function
Exposure Route: oral gavage
Dosage: one dose level stated in HEAST summary:
250 mg/kg/d = NOAEL
Calculations: not applicable
Comments: Because the study was less than 1 year in duration and not considered
exposure during a critical life stage, the 250 mg/kg/d dose was
considered to be a subchronic NOAEL. A chronic NOAEL was
estimated by multiplying the subchronic NOAEL by a subchronic-
chronic uncertainty factor of 0.1
Final NOAEL: 25 mg/kg/d
Compound: Molybdenum
Form: Molybdate (MoO4)
Reference: Schroeder and Mitchner, 1971
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Food Consumption: 0.0055 kg/d
Water Consumption: 0.0075 L/d
(calculated using allometric equation from EPA, 1988a)
Study Duration: 3 generations (> 1 yr and during critical lifestage=chronic)
Endpoint: reproduction
Exposure Route: oral in water
Dosage: one dose level:
10 mg Mo/L + 0.45 mg/kg in diet = LOAEL
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-26 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
MomgNOAEL 5.203.05.710:¸¸¹
·¨¨©
§
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
MomgLOAEL 0825.003.05.745.0:¸¸¹
·¨¨©
§
Total Exposure = 2.5 mg/kg/d + 0.0825 mg/kg/d =2.5825 mg/kg/d
Comments: Because mice exposed to Mo displayed reduced reproductive success with a
high incidence of runts, this dose was considered to be a chronic LOAEL. A chronic NOAEL
was estimated by multiplying the chronic LOAEL by a LOAEL-NOAEL uncertainty factor
of 0.1.
Final NOAEL: 0.26 mg/kg/d
Final LOAEL: 2.6 mg/kg/d
Compound: Naphthalene
Form: Not applicable
Reference: Wildlife International, 1985
Test Species: Bobwhite Quail
Body weight: 198.4 g (mean of control group from study)
Exposure Duration: Acute – single dose followed by 14-day observation
Endpoint: Mortality
Exposure Route: Oral gavage
Dosage: Six dose levels: 0, 292, 486, 810, 1,350, and 2,250 mg/kg
Calculations: Not applicable
Comments: Overt signs of toxicity were observed at 486 mg/kg dose and above.
LD50 for naphthalene in bobwhite was determined to be 2,690 mg/kg
(95% CI=1,571-57,063 mg/kg). A chronic NOAEL and LOAEL were estimated
by applying uncertainty factors of 0.01 and 0.1, respectively.
Final LD50: 2690 mg/kg
Final NOAEL: 26.9 mg/kg/d
Final LOAEL: 269 mg/kg/d
Compound: Naphthalene
Form: Not applicable
Reference: Navarro et al., 1991
Test Species: Rat
Body weight: 0.24 kg (range, 0.21-0.27 kg) (mean of females in
study)
Exposure Duration: Days 6-15 of gestation (during critical lifestage = chronic )
Endpoint: Reproduction
Exposure Route: Oral gavage
Dosage: Three dose levels: 50, 150, and 450 mg/kg/d
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-27
Calculations: Not applicable
Comments: Dams treated with 150 and 450 mg/kg/d experienced a respective
31 and 53% reduction in weight gain compared to control dams. Maternal body
weight gain continued to be reduced post-treatment (day 15 through sacrifice on
day 20). No effects in weight gain were observed in rats dosed with 50 mg/kg/d.
No fetal effects were observed. Because maternal body weight gain was reduced and
these effects were observed during a critical life-stage, 150 mg/kg/d was considered
to be the chronic LOAEL. No adverse effects were observed at 50 mg/kg/d,
therefore this was considered to be a chronic NOAEL.
Final NOAEL: 50 mg/kg/d
Final LOAEL: 150 mg/kg/d
Compound: No. 2 fuel oil
Reference: Szaro et al., 1981
Test Species: Mallard Duck
Body Weight: 1 kg (from Heinz et al., 1987)
Food Consumption: 100 g/d (from Heinz et al., 1987)
Study Duration: 18 wk (18 wk during a critical lifestage = chronic)
Endpoint: Mortality and growth
Exposure Route: Oral in diet
Dosage: Two dose levels: 0.5 and 5.0% (5,000 and 50,000 mg/kg) No. 2
fuel oil in food
Calculations:
dkgmgBWkgg
kg
day
foodg
foodKg
OilFuelNomgNOAEL //5001/1000
11002.000,5: ¸¸
¹
·uu¨¨
©
§
dkgmgBWkgg
kg
day
foodg
foodKg
OilFuelNomgLOAEL //000,51/000,1
11002.000,50: ¸¸
¹
·uu¨¨
©
§
Comments: Growth was depressed in mallards receiving a diet containing 5% No. 2
fuel oil, and no mortality was related to oil ingestion. Other effects at the 5% dose
included increased liver weights, decreased spleen weights, shorter running distances,
and hyperactivity compared to control and 0.5% dosed birds. Because no significant
differences were observed at the lower dose level and the study considered exposure
throughout a critical lifestage (growth), the 0.5% dose was considered to be a chronic
NOAEL and the 5% dose was considered to be a chronic LOAEL.
Final NOAEL: 500 mg/kg/d
Final LOAEL: 5000 mg/kg/d
Compound: Nickel
Form: Nickel Sulfate Hexahydrate
Reference: Ambrose et al., 1976
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Food Consumption: 0.028 kg/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: 3 generations (>1 yr and during a critical lifestage = chronic)
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-28 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: three dose levels:
250, 500, and 1000 ppm Ni
NOAEL = 500 ppm
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
NimgNOAEL 4035.028500:¸¸¹
·¨¨©
§
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
NimgLOAEL 8035.028100:¸¸¹
·¨¨©
§
Comments: While 1000 ppm Ni in the diet reduced offspring body weights, no adverse
effects were observed in the other dose levels. Because this study considers exposures over
multiple generations, the 500 ppm dose was considered to be a chronic NOAEL and the
1000 ppm dose was considered to be a chronic LOAEL..
Final NOAEL: 40 mg/kg/d
Final LOAEL: 80 mg/kg/d
Compound: Nickel
Form: Nickel Sulfate
Reference: Cain and Pafford, 1981
Test Species: Mallard Duckling
Body weight: 0.782 kg (meancontrol male+female at 28 and 60 days;
from study)
Food Consumption: Adult Mallard ducks, weighing 1 kg
consume 100 g food/d (Heinz et al., 1989). Therefore, it was
assumed that a 0.782 kg mallard duckling would consume 78.2
g food/d.
Study Duration: 90 d (>10 week = chronic)
Endpoint: mortality, growth, behavior
Exposure Route: oral in diet
Dosage: three dose levels:
176, 774, and 1069 ppm Ni;
NOAEL = 176 ppm
Calculations:
dkgmgBWkgg
kg
day
foodg
foodkg
NimgNOAEL //6.17782.0/1000
12.78176: ¸¸
¹
·uu¨¨
©
§
dkgmgBWkgg
kg
day
foodg
foodkg
NimgLOAEL //4.77782.0/1000
12.78774: ¸¸
¹
·uu¨¨
©
§
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-29
Comments: While consumption of up to 774 ppm Ni in diet resulted in a significant
increase in tremors and joint edema, 176 ppm did not. Because the study considered
exposure over 90 days, the 176 ppm dose was considered to be a chronic NOAEL and the
774 ppm dose was considered to be a chronic LOAEL. To estimate daily Ni intake
throughout the 90 day study period, food consumption of 45-day-old ducklings was
calculated. While this value will over- and underestimate food consumption by younger
and older ducklings, it was assumed to approximate food consumption throughout the
entire 90-day study.
Final NOAEL: 17.6 mg/kg/d
Final LOAEL: 77.4 mg/kg/d
Compound: Nitrate
Form: Potassium Nitrate
Reference: Sleight and Atallah, 1968
Test Species: Guinea pig
Body weight: 0.86 kg (EPA, 1988a)
Study Duration: 143-204 days (during a critical lifestage=chronic)
Endpoint: reproduction
Exposure Route: oral in water
Dosage: four dose levels:
12, 102, 507, and 1130 mg nitrate-Nitrogen kg/d;
NOAEL = 507 mg/kg/d
Calculations: not applicable
Comments: While Nitrate at the 1130 mg/kg/d dose level reduced the number of
live births, no adverse effects were observed at the other dose levels.
Because the study considered exposure during reproduction, the 507
mg/kg/d dose was considered to be a chronic NOAEL and the 1130
mg/kg/d dose was considered to be a chronic LOAEL. .
Final NOAEL: 507 mg/kg/d
Final LOAEL: 1130 mg/kg/d
Compound: Perchlorate
Form: NH4ClO4
Reference: McNabb et al. 2003
Test Species: Bobwhite Quail
Exposure Duration: 2-8 weeks during sensitive period (3-4 days posthatch)
Endpoint: Thyroid hormone (T4) content
Exposure Route: drinking water
Dosage: 50 ug/L to 250 mg/L
Calculations: not applicable
Comments:. Quail exposure to ammonium perchlorate (AP) in this study indicated
trends but not significant differences in T4 content of the thyroid from controls at 50
ug/L over 2 weeks (NOAEL), and significant differences in several indices occurred
at 500 ug/L (LOAEL) over 2 weeks. Drinking rates were not measured but
estimated daily doses were determined as 3.85 ug/kg/d at the NOAEL and at 38.5
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-30 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
mg/kg/day at the LOAEL. Since these reported values are expressed as NH4ClO4,
the perchlorate ion dose was calculated based on a 84.6% composition of AP.
Final NOAEL: 3.26 ug/kg/d
Final LOAEL: 32.6 ug/kg/d
Compound: 2,4,6-Trinitrotoluene (TNT)
Form: Not Applicable
Reference: Johnson et al. 2000
Test Species: Northern Bobwhite (Colimus virginianus)
Exposure Duration: 90 days
Endpoint: mortality, blood hematological effects, and immunity
Exposure Route: oral dose in food
Dosage: 160 mg/kg and 3300 mg/kg
Calculations: Not Applicable
Comments:. This evaluation of TNT toxicity for all avian and mammal studies
based the reported NOAEL and LOAELs on a single study (Gogal et al. in Draft).
These reported chronic values are applied.
Final NOAEL: 0.07 mg/kg/d
Final LOAEL: 1.8 mg/kg/d
Compound: 2,4,6-Trinitrotoluene (TNT)
Form: Not Applicable
Reference: Johnson et al. 2000
Test Species: Dog (beagle)
Exposure Duration: 13 week to 6 month
Endpoint: increased liver weight, physiology, decreased body weight.
Exposure Route: Not Applicable
Dosage: Not Applicable
Calculations: Not Applicable
Comments:. This evaluation of TNT toxicity reported NOAEL and LOAELs from
nine investigations. The lowest NOAEL and LOAEL values reported were adopted
as wildlife screening values.
Final NOAEL: 2 mg/kg/d
Final LOAEL: 8 mg/kg/d
Compound: Pentachlorophenol (PCP)
Form: not applicable
Reference: Schwetz et al., 1978
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Food Consumption: 0.028 kg/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: 62 d prior to mating, 15 d during mating, and through gestation and
lactation (during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: two dose levels:
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-31
3 and 30 ppm; NOAEL = 3 ppm
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
PCPmgNOAEL 2435.0283:¸¸¹
·¨¨©
§
mg/kg/d=BWkg/mg1000
kg1xday
foodgxfoodkg
NimgLOAEL 40.235.02830:¸¸¹
·¨¨©
§
Comments: While survival and growth were significantly reduced (<20% of controls)
among rats consuming the 30 ppm PCP diet, no adverse effects were observed among rats
on the 3 ppm diet. Because the study considered exposure during reproduction, the 3 ppm
dose was considered to be a chronic NOAEL and the 30 ppm dose was considered a chronic
LOAEL.
Final NOAEL: 0.24 mg/kg/d
Final LOAEL: 2.4 mg/kg/d
Compound: Pentachlorophenol (PCP)
Form: Not applicable
Reference: Nebeker et al., 1994
Test Species: Mallard ducklings (0.15 Kg BW)
Exposure Duration: 11 days (at critical lifestage = chronic)
Endpoint: Growth and Bioaccumulation
Exposure Route: Oral in diet (0.06 g/day)
Dosage: 25, 54.2, 105, 233.2, 423.2, and 961 ug/g
Calculations: Mean PCP in feed was reported for body weight LOAEL and
NOAEL test concentrations. These concentrations were used to calculate final
LOAEL and NOAEL values after the application of a sub-chronic to chronic
uncertainty factor (0.1)
dkgmgBWkgg
kg
day
foodg
foodkg
PCPmgNOAEL //28.16915.0/1000
106.02.423: ¸¸
¹
·uu¨¨
©
§
dkgmgBWkgg
kg
day
foodg
foodkg
PCPimgLOAEL //4.38415.0/1000
106.0961: ¸¸
¹
·uu¨¨
©
§
Comments:
Final LOAEL: 38.4 mg/kg/d
Final NOAEL: 16.9 mg/kg/d
Compound: Phenol
Form: Not applicable
Reference: Bishop et al., 1997
Test Species: Mouse
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-32 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Exposure Duration: 347 days (during critical lifestage = chronic)
Endpoint: Reproduction
Exposure Route: Intraperitoneal
Dosage: One dose level: 350 mg/kg (1 i.p. injection prior to each of
17 breeding cycles)
Calculations: Normalized 17 doses of 350 mg/kg over 347 days
17.1 mg/kg/d
Comments: No effects on reproductive performance were observed. Because
injections were given at critical lifestage periods, a dose of 17.1 mg/kg/d was
considered to be the chronic NOAEL.
Final NOAEL: 17.1 mg/kg/d
Compound: Phosphorus
Form: P4
Reference: Sparling et al., 1997
Test Species: Mallards
Exposure Duration: 24 hour lethality, 7 day sublethal
Endpoint: mortality, organ function
Exposure Route: fed pelletized P4
Dosage: 4-5 adult birds dosed with 2, 4, 5.2, 6.1, 7.1, 8.0, and 9.0 mg/kg
Calculations: Not Applicable
Comments: A chronic LOAEL was estimated from the reported acute
sublethal liver necrosis (2.6 mg/kg) by multiplying by an acute to chronic
uncertainty factor (0.1). The lowest reported NOAEL resulted from acute lethality
tests dosed at 3.7 mg/kg. An acute to chronic uncertainty factor (0.1) and a lethal to
sublethal uncertainty factor (0.1) were applied to determine a chronic NOAEL.
Final LOAEL: 0.26 mg/kg/d
Final NOAEL: 0.037mg/kg/d
Compound: Pyrene
Form:Not applicable
Reference: IRIS, 2001
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Exposure Duration: 13 weeks (t 90 days = chronic)
Endpoint: Nephropathy
Exposure Route: Oral gavage
Dosage: Three dose levels: 75, 125, and 250 mg/kg/d;
Calculations: Not applicable
Comments: Nephropathy, characterized by multiple foci of renal tubular
regeneration, often accompanied by interstitial lymphocytic infiltrates and/or foci of
interstitial fibrosis, were present in higher numbers in female mice in the two higher
dose groups. Relative and absolute kidney weights were also reduced in the two
higher dosage groups.
Final NOAEL: 75 mg/kg/d
Final LOAEL: 125 mg/kg/d
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-33
Compound: Selenium
Form: Potassium Selanate (SeO4)
Reference: Rosenfeld and Beath, 1954
Test Species: rat
Body weight: 0.35 kg (EPA, 1988a)
Water Consumption: 0.046 L/d
(calculated using allometric equation from EPA, 1988a)
Study Duration: 1 year, through 2 generations (1 yr and during critical
lifestage=chronic)
Endpoint: reproduction
Exposure Route: oral in water
Dosage: three dose levels:
1.5, 2.5, and 7.5 mg Se/L
2.5 mg/L = LOAEL
Calculations:
mg/kg/d=BWkg/mL
Lxday
watermLxwaterL
SemgNOAEL 20.035.01000
1465.1:¸¸
¹
·
¨¨
©
§
mg/kg/d=BWkg/mL
Lxday
watermLxwaterL
SemgNOAEL 33.035.01000
1465.2:¸¸
¹
·
¨¨
©
§
Comments: While no adverse effects on reproduction were observed among rats
exposed to 1.5 mg Se/L in drinking water, the number of second-generation young was
reduced by 50% among females in the 2.5 mg/L group. In the 7.5 mg/L group, fertility,
juvenile growth, and survival were all reduced. Because the study considered exposure over
multiple generations, the 1.5 and 2.5 mg/L doses were considered to be chronic NOAELs
and LOAELs, respectively.
Final NOAEL: 0.20 mg/kg/d
Final LOAEL: 0.33 mg/kg/d
Compound: Selenium
Form: Selanomethionine
Reference: Heinz et al., 1989
Test Species: Mallard
Body Weight: 1 kg (from study)
Food Consumption: 100 g/d (from study)
Study Duration: 100 days (>10 wks and during critical lifestage=chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: five dose levels:
1, 2, 4, 8, and 16 ppm Se; 4 ppm = NOAEL
Calculations:
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-34 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC

dkgmgBWkgg
kgxday
foodgxfoodkg
Semg
dkgmgBWkgg
kgxday
foodgxfoodkg
Semg
//8.01/1000
11008
//4.01/1000
11004
¸¸
¹
ᬬ
©
§
¸¸¹
·
¨¨©
§
Comments: Consumption of 8 or 16 ppm Se in the diet as Selanomethionine resulted
in a reduced duckling survival as compared to the 1, 2, or 4 ppm Se exposures. Because 4
ppm Se in the diet was the highest dose level that produced no adverse effects and the study
considered exposure through reproduction, this dose was considered to be a chronic
NOAEL. The 8 ppm Se dose was considered to be a chronic LOAEL
Final NOAEL: 0.4 mg/kg/d
Final LOAEL: 0.8 mg/kg/d
Compound: Strontium (stable)
Form: Strontium Chloride (55% Sr)
Reference: Skoryna, 1981
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Study Duration: 3 yrs (>1 yr = chronic)
Endpoint: Body weight and bone changes
Exposure Route: oral in water
Dosage: three dose levels:
70, 147, and 263 mg Sr kg/d;
NOAEL = 263 mg/kg/d
Calculations: not applicable
Comments: No adverse effects were observed for any Sr dosage level. Therefore,
because the study considered exposure over three years, the maximum dose was considered
to be a chronic NOAEL.
Final NOAEL: 263 mg/kg/d
Compound: Thallium
Form: Thallium Sulfate
Reference: Formigli et al., 1986
Test Species: Rat
Body weight: 0.365 kg (from study)
Study Duration: 60 days
(<1 yr and not during a critical lifestage = subchronic)
Endpoint: reproduction (male testicular function)
Exposure Route: oral in water
Dosage: one dose level: 10 ppm Tl = LOAEL
Calculations: mean daily intake (from study) = 270 p Tl/rat
= 0.74 mg/kg/d
Comments: Because rats exposed to 10 ppm Tl in the diet displayed reduced sperm
motility and the study considered exposures only for 60 d , this dose was considered to be a
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-35
subchronic LOAEL. A chronic NOAEL was estimated by multiplying the subchronic
LOAEL by a subchronic-chronic uncertainty factor of 0.1 and a LOAEL-NOAEL uncertainty
factor of 0.1.
Final NOAEL: 0.0074 mg/kg/d
Final LOAEL: 0.074 mg/kg/d
Compound: Thallium
Form: Tl2SO4
Reference: Bean and Hudson, 1976
Test Species: Golden eagles (3 immatures ranging from 2.8-4.6 kg)
Exposure Duration: single dose
Endpoint: lethality
Exposure Route: oral
Dosage: 60 and 120 mg/kg
Calculations: Not Applicable
Comments: Uncertainty factors for lethal to sublethal effects (0.1) and from
acute to chronic effects (0.1) were applied to the reported acute NOEL (60 mg/kg)
and acute lethal LOEL (120 mg/kg).
Final NOAEL: 0.6 mg/kg/d
Final LOAEL: 1.2 mg/kg/d
Compound: Toluene
Form: Not applicable
Reference: Gospe et al., 1994
Test Species: Rat
Body weight: 0.2 kg (mean from study)
Exposure Duration: Days 6-19 of gestation (during a critical lifestage = chronic)
Endpoint: Reproduction and growth
Exposure Route: Oral gavage
Dosage: 520 mg/kg/d
Calculations: Not applicable
Comments: Female rats dosed at 520 mg/kg/d during gestation experienced a 24%
reduction in body weight gain, as well as reductions in placental weight. Fetal
weights were reduced 9.4%. Fetal organ weights were less in the exposed group, with
significant reductions on the weights of fetal liver and kidney. Toluene exposure did
not produce any major fetal malformations and there were no significant
neuropathologic findings. Because the study was conducted during a critical
life-stage, 520 mg/kg/d was considered to be a chronic LOAEL. A chronic NOAEL
was estimated by multiplying the chronic LOAEL by an uncertainty factor of 0.1.
Final NOAEL: 52 mg/kg/d
Final LOAEL: 520 mg/kg/d
Compound: 1,1,1-Trichloroethane
Form: not applicable
Reference: Lane et al., 1982
Test Species: Mouse
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-36 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Body weight: 0.035 kg (from study)
Water Consumption: 6 mL/d (from study)
Study Duration: 2 generations (>1 yr and during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in water
Dosage: three dose levels:
100, 300, and 1000 mg/kg/d
No effects observed at any dose level.
Calculations: not applicable
Comments: Because no significant differences were observed at any dose level and
the study considered exposure throughout 2 generations including
critical lifestages (reproduction), the maximum dose was considered to
be a chronic NOAEL.
Final NOAEL: 1000 mg/kg/d.
Compound: 1,1,2,2-Tetrachloroethylene
Form: not applicable
Reference: Buben and O'Flaherty, 1985
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Study Duration: 6 weeks
(<1 yr and not during a critical lifestage = subchronic)
Endpoint: Hepatotoxicity
Exposure Route: oral gavage
Dosage: seven dose levels (administered daily 5 days/week for 6 weeks):
20, 100, 200, 500, 1000, 1500, and 2000 mg/kg/d;
NOAEL = 20 mg/kg/d
Calculations: not applicable
Comments: Because mice were exposed for 5 days/week, 7 day/week exposure were
estimated by multiplying doses by 0.7 (5 days/7 days). Hepatotoxicity was observed at doses
of 100 mg/kg/d or greater. Therefore, the 20 mg/kg/d dose was considered to be a
subchronic NOAEL and the 100 mg/kg/d dose was considered to be a subchronic LOAEL.
A chronic NOAEL was estimated by multiplying the subchronic NOAEL by a subchronic-
chronic uncertainty factor of 0.1
Final NOAEL: 1.4 mg/kg/d
Final LOAEL: 7 mg/kg/d
Compound: Trichloroethylene (TCE)
Form: not applicable
Reference: Buben and O'Flaherty, 1985
Test Species: Mouse
Body weight: 0.03 kg (EPA, 1988a)
Study Duration: 6 weeks
(<1 yr and not during a critical lifestage = subchronic)
Endpoint: Hepatotoxicity
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-37
Exposure Route: oral gavage
Dosage: seven dose levels (administered daily 5 days/week for 6 weeks):
100, 200, 400, 800, 1600, 2400, and 3200 mg/kg/d;
LOAEL = 100 mg/kg/d
Calculations: not applicable
Comments: Because mice were exposed for 5 days/week, 7 day/week exposures
were estimated by multiplying doses by 0.7 (5 days/7 days).
Hepatotoxicity was observed at doses of 100 mg/kg/d or greater.
Therefore, the 100 mg/kg/d dose was considered to be a subchronic
LOAEL. A chronic NOAEL was estimated by multiplying the
subchronic NOAEL by a subchronic-chronic uncertainty factor of 0.1
and a LOAEL-NOAEL uncertainty factor of 0.1.
Final NOAEL: 0.7 mg/kg/d
Final LOAEL: 7 mg/kg/d
Compound: Vanadium
Form: Sodium Metavanadate (NaVO3; 41.78% V)
Reference: Domingo et al., 1986
Test Species: Rat
Body weight (from study): 0.26 kg
Study Duration: 60 d prior to gestation, plus through gestation, delivery and lactation
(during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral intubation
Dosage: three dose levels:
5, 10, and 20 mg NaVO3 /kg/d; LOAEL=5 mg/kg/d
Calculations: LOAEL dosage of elemental V is:
0.4178 x 5 mg NaVO3 /kg/d or 2.1 mg V/kg/d
Comments: Significant differences in reproductive parameters (e.g., no. dead
young/litter, size and weight of offspring, etc.) were observed at all dose levels. Therefore,
the lowest dose was considered to be a chronic LOAEL. To estimate the chronic NOAEL, the
chronic LOAEL was multiplied by a LOAEL-NOAEL uncertainty factor of 0.1.
Final NOAEL: 0.21 mg V/kg/d
Final LOAEL: 2.1 mg V/kg/d
Compound: Vinyl Chloride
Form: not applicable
Reference: Feron et al., 1981
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Study Duration: lifetime (~144 wks)
Endpoint: longevity, mortality
Exposure Route: oral in diet
Dosage: three dose levels:
1.7, 5.0, and 14.1 mg /kg/d; LOAEL= 1.7 mg/kg/d or
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-38 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Calculations: not applicable
Comments: Significantly reduced survivorship was observed at all dose levels,
therefore the 1.7 mg/kg/d dose level was considered to be a chronic LOAEL. To estimate
the chronic NOAEL, the LOAEL was multiplied by a LOAEL-NOAEL uncertainty factor of
0.1.
Final NOAEL: 0.17 mg/kg/d
Final LOAEL: 1.7 mg/kg/d
Compound: Xylenes
Form:Xylene Mixture (60.2% m-xylene, 13.6% p-xylene, 17.0%
ethylbenzene, and 9.1% o-xylene)
Reference: IRIS, 2002
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Exposure Duration: 103 weeks (t 90 days = chronic)
Endpoint: Behavior, growth, and mortality
Exposure Route: Oral gavage
Dosage: Two dose levels: 250 and 500 mg/kg/d;
Calculations: Not applicable
Comments: There was a dose-related increase in mortality in male rats, and the
increase significantly greater in the high-dose group compared with controls.
Although increased mortality was observed at 250 mg/kg/day, the increase was not
significant. Although many of the early deaths were caused by gavage error, the
possibility that the rats were resisting gavage dosing because of behavioral effects of
xylenes was not ruled out. Dose was adjusted for gavage schedule (5 days/week) for
a NOAEL of 179 mg/kg/d (from 250 mg/kg/d) and a LOAEL of 357 mg/kg/d
(from 500 mg/kg/d).
Final NOAEL: 179 mg/kg/d
Final LOAEL: 357 mg/kg/d
Compound: Xylenes
Form:mixed isomers
Reference: Hill and Camardese, 1986
Test Species: Japanese Quail
Body Weight: 0.60 kg (from study)
Food Consumption: 12.2 g (from study)
Exposure Duration: acute – single dose followed by 14 day observation
Endpoint: mortality, overt signs of toxicity
Exposure Route: oral gavage
Dosage: doses ranged from 5000 to 20000 mg/kg
Calculations:
mg/kg/d=BWkg/mg1000
kg1xday
foodg12xfoodkg
Xylenesmg 7.10160.02.5000 ¸¸¹
·¨¨©
§
APPENDIX A: APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC A-39
Comments: No mortality observed at any dose level. LC50 of >20000mg/kg is
reported. No overt signs of toxicity at concentrations of 5000 ppm. Because no signs
of toxicity were observed at 5000 ppm, this dose was considered to be an acute
NOAEL. A 0.1 acute to chronic uncertainty factor was applied to estimate a chronic
NOAEL.
Acute NOAEL: 101.7 mg/kg/d
Chronic NOAEL: 10.2 mg/kg/d
Compound: Zinc
Form: Zinc Oxide
Reference: Schlicker and Cox, 1968
Test Species: Rat
Body weight: 0.35 kg (EPA, 1988a)
Food Consumption: 0.028 kg/d (calculated using allometric equation
from EPA, 1988a)
Study Duration: days 1 -16 of gestation (during a critical lifestage = chronic)
Endpoint: reproduction
Exposure Route: oral in diet
Dosage: two dose levels:
2000, and 4000 ppm Zn; NOAEL = 2000 ppm
Calculations:
mg/kg/d=BWkg/g
kgxday
foodgxfoodkg
ZnmgNOAEL 16035.01000
1282000:¸¸
¹
·
¨¨
©
§
mg/kg/d=BWkg/g
kgxday
foodgxfoodkg
ZnmgLOAEL 32035.01000
1284000:¸¸
¹
·
¨¨
©
§
Comments: Rats exposed to 4000 ppm Zn in the diet displayed increased rates of fetal
resorption and reduced fetal growth rates. Because no effects were observed at the 2000
ppm Zn dose rate and the exposure occurred during gestation (a critical lifestage), this dose
was considered a chronic NOAEL. The 4000 ppm Zn dose was considered to be a chronic
LOAEL.
Final NOAEL: 160 mg/kg/d
Final LOAEL: 320 mg/kg/d
Compound: Zinc
Form: Zinc Sulfate
Reference: Stahl et al., 1990
Test Species: White Leghorn Hens
Body Weight: 1.935 kg (228 ppm dose; from study)
1.766 kg (2028 ppm dose; from study)
Food Consumption: 123 g/d (228 ppm dose; from study)
0.114 (2028 ppm dose; from study)
Exposure Duration: 44 weeks (>10 wks and during critical lifestage=chronic)
Endpoint: reproduction
Exposure Route: oral in diet
APPENDIX A: DESCRIPTIONS OF STUDIES USED TO CALCULATE NOAELS AND LOAELS
A-40 SLC JMS ES112005010SLC\HILLAFB_APPENDIXA-TOXICITYSTUDIES_OCT05 (2)_101405.DOC
Dosage: four dose levels:
0, 20, 200, and 2000 ppm supplemental Zn plus 28 ppm Zn in
diet
Calculations:
mg/kg/d=BWkg1.9/mg1000
kg1xday
foodg12xfoodkg
Znmg 84.100528¸¸¹
·¨¨©
§
mg/kg/d3.11=BWkg1.963/mg1000
kg1xday
foodg127xfoodkg
Znmg48 ¸¸¹
·¨¨©
§
mg/kg/d14.49=BWkg1.935/mg1000
kg1xday
foodg123xfoodkg
Znmg228 ¸¸¹
·¨¨©
§
mg/kg/d130.9=BWkg1.766/mg1000
kg1xday
foodg114xfoodkg
Znmg2028 ¸¸¹
·¨¨©
§
Comments: While no adverse effects were observed among hens consuming 48 and 228
ppm Zn, egg hatchability was <20% of controls among hens consuming 2028 ppm zinc.
Because the study was greater than 10 weeks in duration and considered exposure during
reproduction, the 228 ppm dose was considered a chronic NOAEL and the 2028 ppm dose
was considered a chronic LOAEL..
Final NOAEL: 14.5 mg/kg/d
Final LOAEL: 131 mg/kg/d

Appendix B
SLC JMS ES112005010SLC\HILLAFB_APPENDIX-B TEXT_OCT05 (2)_101405.DOC B-1
Appendi B. Background Soils Anal sis
Four sets of background data were available for the Thermal Treatment Unit (TTU). Three
sets (1997, 1998, and 2000 data) were reported by URS (2001), and another set that included
two additional background locations to the west of the TTU were sampled in 2004 and are
reported here. These background data represent two soil formations that exist in the Utah
Training and Test Range (UTTR)-North area (which includes the TTU): the combined
amtoft, skumpah, and timpie-tooele soil formations and the playa-salt air soil formation.
The full background data set including sampling location is presented in Table B-1.
The U.S. Environmental Protection Agency(EPA) provides methods for background
comparisons in Guidance for Comparing Background and Chemical Concentrations in Soil
for CERCLA Sites (USEPA, 2002). In accordance with this guidance, TTU background
concentrations of inorganic contaminants of potential ecological concern (COPECs) were
statistically compared to on-site concentrations using the non-parametric Wilcoxon Rank
Sum (WRS) test. Analyses were performed using the SAS software (SAS Institute, 1999).
Results of the WRS tests for the TTU are presented in Table B-2. Additionally, box plots
illustrating distributions of the background and on-site data are presented in Figures B-1 to
B-13. Figure B-1 is a guide describing how data distributions are displayed in box plots.
Interpretation of the results of this comparison followed EPA (2002) recommendations.
Namely, if the null hypothesis was accepted (i.e., there was no significant [p > 0.05]
difference between background and on-site data), then it was concluded that the analyte
was not elevated relative to background and it was dropped from further consideration as a
COPEC for all receptors. COPECs with background concentrations that were significantly
greater than site concentrations also were dropped from further consideration. Those
COPECs with significantly greater site concentrations compared to background
concentrations were retained for further evaluation.
Briefly, 23 COPECs had both on-site and background data available. On-site concentrations
of eight COPECs (aluminum, beryllium, chromium, iron, manganese, mercury, nickel, and
thallium) did not differ from background concentrations. Background concentrations were
statistically greater than on-site concentrations for seven COPECs (arsenic, barium, cobalt,
magnesium, phosphorus, strontium, and vanadium). These 15 COPECs were excluded
from further evaluation. The remaining eight COPECs (antimony, cadmium, copper, lead,
molybdenum, selenium, silver, and zinc) had greater on-site concentrations compared to
background, and were carried forward for further evaluation in the refined screening
assessment.
References:
SAS Institute 1999. SAS/STAT User’s Guide, Version 8. SAS Institute, Cary, North Carolina.
United States Environmental Protection Agency (EPA). 2002. Guidance for Comparing
Background and Chemical Concentrations in Soil for CERCLA Sites. EPA 540-R-01-003, OSWER
9285.7-41, Office of Emergency and Remedial Response, EPA, Washington, D.C. September.
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Aluminum AMTOF-01-1298-01 Background Habitat mg/kg = 12300 1998
Aluminum AMTOF-02-1298-01 Background Habitat mg/kg = 10500 1998
Aluminum AMTOF-03-1298-01 Background Habitat mg/kg = 13600 1998
Aluminum AMTOF-04-1298-01 Background Habitat mg/kg = 15400 1998
Aluminum AMTOF-05-1298-01 Background Habitat mg/kg = 10600 1998
Aluminum AMTOF-06-1298-01 Background Habitat mg/kg = 12800 1998
Aluminum NR-238 Background Habitat mg/Kg = 14800 2002
Aluminum NR-239 Background Habitat mg/Kg = 10800 2002
Aluminum NR-500-0800-01 Background Habitat mg/kg = 12600 2000
Aluminum NR-501-0800-01 Background Habitat mg/kg = 9160 2000
Aluminum NR-502-0800-01 Background Habitat mg/kg = 13700 2000
Aluminum NR-503-0800-01 Background Habitat mg/kg = 13300 2000
Aluminum NR-504-0800-01 Background Habitat mg/kg = 12200 2000
Aluminum NR-505-0800-01 Background Habitat mg/kg = 14100 2000
Aluminum NR-506-0800-01 Background Habitat mg/kg = 12200 2000
Aluminum NR-507-0800-01 Background Habitat mg/kg = 11600 2000
Aluminum NR-508-0800-01 Background Habitat mg/kg = 11100 2000
Aluminum NR-509-0800-01 Background Habitat mg/kg = 10500 2000
Aluminum NR-510-0800-01 Background Habitat mg/kg = 7800 2000
Aluminum NR-511-0800-01 Background Habitat mg/kg = 11500 2000
Aluminum NR-512-0800-01 Background Habitat mg/kg = 15600 2000
Aluminum NR-513-0800-01 Background Habitat mg/kg = 12800 2000
Aluminum NR-514-0800-01 Background Habitat mg/kg = 12700 2000
Aluminum NR-515-0800-01 Background Habitat mg/kg = 2820 2000
Aluminum NR-516-0800-01 Background Habitat mg/kg = 13700 2000
Aluminum NR-517-0800-01 Background Habitat mg/kg = 7490 2000
Aluminum NR-518-0800-01 Background Habitat mg/kg = 2080 2000
Aluminum NR-519-0800-01 Background Habitat mg/kg = 6810 2000
Aluminum NR-520-0800-01 Background Habitat mg/kg = 7070 2000
Aluminum NR-521-0800-01 Background Habitat mg/kg = 5050 2000
Aluminum NR-522-0800-01 Background Habitat mg/kg = 11700 2000
Aluminum NR-523-0800-01 Background Habitat mg/kg = 9750 2000
Aluminum NR-524-0800-01 Background Habitat mg/kg = 7980 2000
Aluminum NR-525-0800-01 Background Habitat mg/kg = 6340 2000
Aluminum NR-536 Background Habitat mg/Kg B 15000 2004
Aluminum NR-537 Background Habitat mg/Kg B 17200 2004
Aluminum UTNCBU-01-OCT97-01 Background Habitat mg/kg = 12100 1997
Aluminum UTNCBU-02-OCT97-01 Background Habitat mg/kg = 11400 1997
Aluminum UTNCBU-03-1298-01 Background Habitat mg/kg = 15800 1998
Aluminum UTNCBU-04-1298-01 Background Habitat mg/kg = 15400 1998
Aluminum UTNCBU-05-1298-01 Background Habitat mg/kg = 11700 1998
Aluminum UTNCBU-06-1298-01 Background Habitat mg/kg = 11500 1998
Aluminum UTNEB-03-1298-01 Background Habitat mg/kg = 12700 1998
Aluminum UTNEB-04-1298-01 Background Habitat mg/kg = 17700 1998
Aluminum UTNEB-05-1298-01 Background Habitat mg/kg = 14100 1998
Aluminum UTNEB-06-1298-01 Background Habitat mg/kg = 12000 1998
Aluminum UTNERB-01-OCT97-01 Background Habitat mg/kg = 21100 1997
Aluminum UTNERB-02-OCT97-01 Background Habitat mg/kg = 18900 1997
Aluminum UTNOCB-01-OCT97-01 Background Habitat mg/kg = 14100 1997
Aluminum UTNOCB-02-OCT97-01 Background Habitat mg/kg = 13400 1997
Aluminum UTNOCBG-03-1298-01 Background Habitat mg/kg = 11100 1998
Aluminum UTNOCBG-04-1298-01 Background Habitat mg/kg = 10000 1998
Aluminum UTNOCBG-05-1298-01 Background Habitat mg/kg = 10800 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 1 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Aluminum UTNOCBG-06-1298-01 Background Habitat mg/kg = 15300 1998
Aluminum NR-226 OnSite Habitat mg/Kg = 5390 2002
Aluminum NR-227 OnSite Habitat mg/Kg = 8350 2002
Aluminum NR-228 OnSite OB/OD mg/Kg = 10400 2002
Aluminum NR-229 OnSite Habitat mg/Kg = 14700 2002
Aluminum NR-230 OnSite Habitat mg/Kg = 13000 2002
Aluminum NR-231 OnSite OB/OD mg/Kg = 12800 2002
Aluminum NR-232 OnSite Habitat mg/Kg = 16800 2002
Aluminum NR-233 OnSite Habitat mg/Kg = 10500 2002
Aluminum NR-234 OnSite Habitat mg/Kg = 13200 2002
Aluminum NR-235 OnSite Habitat mg/Kg = 13600 2002
Aluminum NR-236 OnSite Habitat mg/Kg = 10700 2002
Aluminum NR-237 OnSite Habitat mg/Kg = 11100 2002
Aluminum NR-526 OnSite Habitat mg/Kg B 9050 2004
Aluminum NR-527 OnSite Habitat mg/Kg B 13500 2004
Aluminum NR-528 OnSite Habitat mg/Kg B 7720 2004
Aluminum NR-529 OnSite Habitat mg/Kg B 11800 2004
Aluminum NR-530 OnSite Habitat mg/Kg B 9540 2004
Aluminum NR-531 OnSite OB/OD mg/Kg B 10800 2004
Aluminum NR-532 OnSite OB/OD mg/Kg B 8600 2004
Aluminum NR-533 OnSite OB/OD mg/Kg B 10300 2004
Aluminum NR-534 OnSite OB/OD mg/Kg B 9290 2004
Aluminum NR-535 OnSite OB/OD mg/Kg B 10300 2004
Aluminum SS1 OnSite OB/OD mg/Kg = 11000 1991
Aluminum SS10 OnSite OB/OD mg/Kg = 14000 1991
Aluminum SS11 OnSite OB/OD mg/Kg = 17000 1991
Aluminum SS12 OnSite OB/OD mg/Kg = 20000 1991
Aluminum SS13 OnSite OB/OD mg/Kg = 17000 1991
Aluminum SS14 OnSite OB/OD mg/Kg = 20000 1991
Aluminum SS15 OnSite OB/OD mg/Kg = 18000 1991
Aluminum SS16 OnSite Habitat mg/Kg = 14000 1991
Aluminum SS17 OnSite Habitat mg/Kg = 14000 1991
Aluminum SS18 OnSite Habitat mg/Kg = 17000 1991
Aluminum SS19 OnSite Habitat mg/Kg = 12000 1991
Aluminum SS2 OnSite OB/OD mg/Kg = 7900 1991
Aluminum SS20 OnSite Habitat mg/Kg = 15000 1991
Aluminum SS3 OnSite OB/OD mg/Kg = 20000 1991
Aluminum SS4 OnSite OB/OD mg/Kg = 9600 1991
Aluminum SS5 OnSite OB/OD mg/Kg = 11000 1991
Aluminum SS6 OnSite OB/OD mg/Kg = 16000 1991
Aluminum SS7 OnSite OB/OD mg/Kg = 13000 1991
Aluminum SS8 OnSite OB/OD mg/Kg = 13000 1991
Aluminum SS9 OnSite OB/OD mg/Kg = 54000 1991
Aluminum TTU-SS01S OnSite OB/OD mg/Kg = 7980 1989
Aluminum TTU-SS02S OnSite OB/OD mg/Kg = 9280 1989
Aluminum TTU-SS03S OnSite OB/OD mg/Kg = 9950 1989
Aluminum TTU-SS04S(D) OnSite OB/OD mg/Kg = 8630 1989
Aluminum TTU-SS05S OnSite OB/OD mg/Kg = 9340 1989
Aluminum TTU-SS06S(BG) OnSite Habitat mg/Kg = 14600 1989
Antimony AMTOF-01-1298-01 Background Habitat mg/kg = 1.07 1998
Antimony AMTOF-02-1298-01 Background Habitat mg/kg = 1.23 1998
Antimony AMTOF-03-1298-01 Background Habitat mg/kg = 1.47 1998
Antimony AMTOF-04-1298-01 Background Habitat mg/kg = 1.82 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 2 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Antimony AMTOF-05-1298-01 Background Habitat mg/kg = 1.19 1998
Antimony AMTOF-06-1298-01 Background Habitat mg/kg = 1.48 1998
Antimony NR-238 Background Habitat mg/Kg = 2.1 2002
Antimony NR-239 Background Habitat mg/Kg = 3.1 2002
Antimony NR-500-0800-01 Background Habitat mg/kg U 0.135 0.27 2000
Antimony NR-501-0800-01 Background Habitat mg/kg U 0.745 1.49 2000
Antimony NR-502-0800-01 Background Habitat mg/kg U 0.88 1.76 2000
Antimony NR-503-0800-01 Background Habitat mg/kg U 0.715 1.43 2000
Antimony NR-504-0800-01 Background Habitat mg/kg U 0.765 1.53 2000
Antimony NR-505-0800-01 Background Habitat mg/kg U 0.85 1.7 2000
Antimony NR-506-0800-01 Background Habitat mg/kg U 0.68 1.36 2000
Antimony NR-507-0800-01 Background Habitat mg/kg U 0.00705 0.0141 2000
Antimony NR-508-0800-01 Background Habitat mg/kg U 0.715 1.43 2000
Antimony NR-509-0800-01 Background Habitat mg/kg U 0.17 0.34 2000
Antimony NR-510-0800-01 Background Habitat mg/kg U 0.88 1.76 2000
Antimony NR-511-0800-01 Background Habitat mg/kg U 0.1925 0.385 2000
Antimony NR-512-0800-01 Background Habitat mg/kg U 0.056 0.112 2000
Antimony NR-513-0800-01 Background Habitat mg/kg U 0.615 1.23 2000
Antimony NR-514-0800-01 Background Habitat mg/kg U 0.103 0.206 2000
Antimony NR-515-0800-01 Background Habitat mg/kg U 0.895 1.79 2000
Antimony NR-516-0800-01 Background Habitat mg/kg U 0.2255 0.451 2000
Antimony NR-517-0800-01 Background Habitat mg/kg U 0.16 0.32 2000
Antimony NR-518-0800-01 Background Habitat mg/kg U 0.498 0.996 2000
Antimony NR-519-0800-01 Background Habitat mg/kg U 0.051 0.102 2000
Antimony NR-520-0800-01 Background Habitat mg/kg J 2.54 2000
Antimony NR-521-0800-01 Background Habitat mg/kg U 0.74 1.48 2000
Antimony NR-522-0800-01 Background Habitat mg/kg U 0.2785 0.557 2000
Antimony NR-523-0800-01 Background Habitat mg/kg U 0.1325 0.265 2000
Antimony NR-524-0800-01 Background Habitat mg/kg U 0.99 1.98 2000
Antimony NR-525-0800-01 Background Habitat mg/kg U 1.07 2.14 2000
Antimony NR-536 Background Habitat mg/Kg J 0.21 2004
Antimony NR-537 Background Habitat mg/Kg J 0.2 2004
Antimony UTNCBU-01-OCT97-01 Background Habitat mg/kg B 0.644 1997
Antimony UTNCBU-02-OCT97-01 Background Habitat mg/kg B 0.499 1997
Antimony UTNCBU-03-1298-01 Background Habitat mg/kg J 0.148 1998
Antimony UTNCBU-04-1298-01 Background Habitat mg/kg = 0.376 1998
Antimony UTNCBU-05-1298-01 Background Habitat mg/kg J 0.229 1998
Antimony UTNCBU-06-1298-01 Background Habitat mg/kg L 0.341 1998
Antimony UTNEB-03-1298-01 Background Habitat mg/kg = 0.422 1998
Antimony UTNEB-04-1298-01 Background Habitat mg/kg J 0.122 1998
Antimony UTNEB-05-1298-01 Background Habitat mg/kg = 0.4 1998
Antimony UTNEB-06-1298-01 Background Habitat mg/kg = 0.362 1998
Antimony UTNERB-01-OCT97-01 Background Habitat mg/kg B 0.85 1997
Antimony UTNERB-02-OCT97-01 Background Habitat mg/kg B 0.843 1997
Antimony UTNOCB-01-OCT97-01 Background Habitat mg/kg B 0.766 1997
Antimony UTNOCB-02-OCT97-01 Background Habitat mg/kg B 0.559 1997
Antimony UTNOCBG-03-1298-01 Background Habitat mg/kg L 1.39 1998
Antimony UTNOCBG-04-1298-01 Background Habitat mg/kg = 1.25 1998
Antimony UTNOCBG-05-1298-01 Background Habitat mg/kg = 1.55 1998
Antimony UTNOCBG-06-1298-01 Background Habitat mg/kg = 1.66 1998
Antimony NR-226 OnSite Habitat mg/Kg = 1.9 2002
Antimony NR-227 OnSite Habitat mg/Kg = 2.3 2002
Antimony NR-228 OnSite OB/OD mg/Kg = 2.2 2002
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 3 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Antimony NR-229 OnSite Habitat mg/Kg = 2.2 2002
Antimony NR-230 OnSite Habitat mg/Kg = 3.3 2002
Antimony NR-231 OnSite OB/OD mg/Kg = 2.8 2002
Antimony NR-232 OnSite Habitat mg/Kg = 2.5 2002
Antimony NR-233 OnSite Habitat mg/Kg U 0.8 1.6 2002
Antimony NR-234 OnSite Habitat mg/Kg = 2.4 2002
Antimony NR-235 OnSite Habitat mg/Kg = 2.5 2002
Antimony NR-236 OnSite Habitat mg/Kg = 3.8 2002
Antimony NR-237 OnSite Habitat mg/Kg = 3.2 2002
Antimony NR-526 OnSite Habitat mg/Kg J 0.21 2004
Antimony NR-527 OnSite Habitat mg/Kg J 0.16 2004
Antimony NR-528 OnSite Habitat mg/Kg J 0.17 2004
Antimony NR-529 OnSite Habitat mg/Kg J 0.19 2004
Antimony NR-530 OnSite Habitat mg/Kg J 0.13 2004
Antimony NR-531 OnSite OB/OD mg/Kg = 166.93 2004
Antimony NR-532 OnSite OB/OD mg/Kg = 18.7 2004
Antimony NR-533 OnSite OB/OD mg/Kg J 0.12 2004
Antimony NR-534 OnSite OB/OD mg/Kg J 0.16 2004
Antimony NR-535 OnSite OB/OD mg/Kg J 0.13 2004
Antimony TTU-SS01S OnSite OB/OD mg/Kg U 0.85 1.7 1989
Antimony TTU-SS02S OnSite OB/OD mg/Kg = 6.4 1989
Antimony TTU-SS03S OnSite OB/OD mg/Kg U 0.85 1.7 1989
Antimony TTU-SS04S(D) OnSite OB/OD mg/Kg U 0.85 1.7 1989
Antimony TTU-SS05S OnSite OB/OD mg/Kg U 0.8 1.6 1989
Antimony TTU-SS06S(BG) OnSite Habitat mg/Kg U 0.85 1.7 1989
Arsenic AMTOF-01-1298-01 Background Habitat mg/kg = 5.79 1998
Arsenic AMTOF-02-1298-01 Background Habitat mg/kg = 6.83 1998
Arsenic AMTOF-03-1298-01 Background Habitat mg/kg = 5.66 1998
Arsenic AMTOF-04-1298-01 Background Habitat mg/kg = 5.74 1998
Arsenic AMTOF-05-1298-01 Background Habitat mg/kg = 7.14 1998
Arsenic AMTOF-06-1298-01 Background Habitat mg/kg = 5.81 1998
Arsenic NR-238 Background Habitat mg/Kg = 7.7 2002
Arsenic NR-239 Background Habitat mg/Kg = 8.2 2002
Arsenic NR-500-0800-01 Background Habitat mg/kg = 5.27 2000
Arsenic NR-501-0800-01 Background Habitat mg/kg = 9.54 2000
Arsenic NR-502-0800-01 Background Habitat mg/kg = 5.69 2000
Arsenic NR-503-0800-01 Background Habitat mg/kg = 5.03 2000
Arsenic NR-504-0800-01 Background Habitat mg/kg = 4.91 2000
Arsenic NR-505-0800-01 Background Habitat mg/kg = 5.57 2000
Arsenic NR-506-0800-01 Background Habitat mg/kg = 9.18 2000
Arsenic NR-507-0800-01 Background Habitat mg/kg = 5.26 2000
Arsenic NR-508-0800-01 Background Habitat mg/kg = 6.23 2000
Arsenic NR-509-0800-01 Background Habitat mg/kg = 8.45 2000
Arsenic NR-510-0800-01 Background Habitat mg/kg = 6.66 2000
Arsenic NR-511-0800-01 Background Habitat mg/kg = 5.75 2000
Arsenic NR-512-0800-01 Background Habitat mg/kg = 5.82 2000
Arsenic NR-513-0800-01 Background Habitat mg/kg = 4.34 2000
Arsenic NR-514-0800-01 Background Habitat mg/kg = 6.86 2000
Arsenic NR-515-0800-01 Background Habitat mg/kg = 8.48 2000
Arsenic NR-516-0800-01 Background Habitat mg/kg = 6.75 2000
Arsenic NR-517-0800-01 Background Habitat mg/kg = 15.4 2000
Arsenic NR-518-0800-01 Background Habitat mg/kg = 9.6 2000
Arsenic NR-519-0800-01 Background Habitat mg/kg = 5.81 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 4 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Arsenic NR-520-0800-01 Background Habitat mg/kg = 5.92 2000
Arsenic NR-521-0800-01 Background Habitat mg/kg = 6.99 2000
Arsenic NR-522-0800-01 Background Habitat mg/kg = 6.37 2000
Arsenic NR-523-0800-01 Background Habitat mg/kg = 2.25 2000
Arsenic NR-524-0800-01 Background Habitat mg/kg = 5.7 2000
Arsenic NR-525-0800-01 Background Habitat mg/kg = 4.22 2000
Arsenic NR-536 Background Habitat mg/Kg J 5 2004
Arsenic NR-537 Background Habitat mg/Kg J 6.6 2004
Arsenic UTNCBU-01-OCT97-01 Background Habitat mg/kg = 6.88 1997
Arsenic UTNCBU-02-OCT97-01 Background Habitat mg/kg = 6.52 1997
Arsenic UTNCBU-03-1298-01 Background Habitat mg/kg = 6.69 1998
Arsenic UTNCBU-04-1298-01 Background Habitat mg/kg = 6.51 1998
Arsenic UTNCBU-05-1298-01 Background Habitat mg/kg = 5.46 1998
Arsenic UTNCBU-06-1298-01 Background Habitat mg/kg = 5.46 1998
Arsenic UTNEB-03-1298-01 Background Habitat mg/kg = 5.35 1998
Arsenic UTNEB-04-1298-01 Background Habitat mg/kg = 7.16 1998
Arsenic UTNEB-05-1298-01 Background Habitat mg/kg = 6.08 1998
Arsenic UTNEB-06-1298-01 Background Habitat mg/kg = 5.92 1998
Arsenic UTNERB-01-OCT97-01 Background Habitat mg/kg = 12.1 1997
Arsenic UTNERB-02-OCT97-01 Background Habitat mg/kg = 12 1997
Arsenic UTNOCB-01-OCT97-01 Background Habitat mg/kg = 8.03 1997
Arsenic UTNOCB-02-OCT97-01 Background Habitat mg/kg = 6.58 1997
Arsenic UTNOCBG-03-1298-01 Background Habitat mg/kg = 5 1998
Arsenic UTNOCBG-04-1298-01 Background Habitat mg/kg = 5.11 1998
Arsenic UTNOCBG-05-1298-01 Background Habitat mg/kg = 5.04 1998
Arsenic UTNOCBG-06-1298-01 Background Habitat mg/kg = 5.44 1998
Arsenic NR-226 OnSite Habitat mg/Kg = 4.9 2002
Arsenic NR-227 OnSite Habitat mg/Kg = 5.2 2002
Arsenic NR-228 OnSite OB/OD mg/Kg = 9.8 2002
Arsenic NR-229 OnSite Habitat mg/Kg = 8.5 2002
Arsenic NR-230 OnSite Habitat mg/Kg = 7.4 2002
Arsenic NR-231 OnSite OB/OD mg/Kg = 7.9 2002
Arsenic NR-232 OnSite Habitat mg/Kg = 41.3 2002
Arsenic NR-233 OnSite Habitat mg/Kg = 1.9 2002
Arsenic NR-234 OnSite Habitat mg/Kg = 7.5 2002
Arsenic NR-235 OnSite Habitat mg/Kg = 7.5 2002
Arsenic NR-236 OnSite Habitat mg/Kg = 7.3 2002
Arsenic NR-237 OnSite Habitat mg/Kg = 8.4 2002
Arsenic NR-526 OnSite Habitat mg/Kg J 4.7 2004
Arsenic NR-527 OnSite Habitat mg/Kg J 5.1 2004
Arsenic NR-528 OnSite Habitat mg/Kg J 4.2 2004
Arsenic NR-529 OnSite Habitat mg/Kg J 4.7 2004
Arsenic NR-530 OnSite Habitat mg/Kg J 4.6 2004
Arsenic NR-531 OnSite OB/OD mg/Kg J 5.7 2004
Arsenic NR-532 OnSite OB/OD mg/Kg J 5.5 2004
Arsenic NR-533 OnSite OB/OD mg/Kg J 5 2004
Arsenic NR-534 OnSite OB/OD mg/Kg J 4.8 2004
Arsenic NR-535 OnSite OB/OD mg/Kg J 5.4 2004
Arsenic SS1 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS10 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS11 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS12 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS13 OnSite OB/OD mg/Kg U 5 10 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 5 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Arsenic SS14 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS15 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS16 OnSite Habitat mg/Kg U 5 10 1991
Arsenic SS17 OnSite Habitat mg/Kg U 5 10 1991
Arsenic SS18 OnSite Habitat mg/Kg U 5 10 1991
Arsenic SS19 OnSite Habitat mg/Kg U 5 10 1991
Arsenic SS2 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS20 OnSite Habitat mg/Kg U 5 10 1991
Arsenic SS3 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS4 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS5 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS6 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS7 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS8 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic SS9 OnSite OB/OD mg/Kg U 5 10 1991
Arsenic TTU-SS01S OnSite OB/OD mg/Kg = 5.7 1989
Arsenic TTU-SS02S OnSite OB/OD mg/Kg = 7 1989
Arsenic TTU-SS03S OnSite OB/OD mg/Kg = 9.6 1989
Arsenic TTU-SS04S(D) OnSite OB/OD mg/Kg = 7 1989
Arsenic TTU-SS05S OnSite OB/OD mg/Kg = 7.4 1989
Arsenic TTU-SS06S(BG) OnSite Habitat mg/Kg = 5.9 1989
Barium AMTOF-01-1298-01 Background Habitat mg/kg = 213 1998
Barium AMTOF-02-1298-01 Background Habitat mg/kg = 148 1998
Barium AMTOF-03-1298-01 Background Habitat mg/kg = 215 1998
Barium AMTOF-04-1298-01 Background Habitat mg/kg = 233 1998
Barium AMTOF-05-1298-01 Background Habitat mg/kg = 227 1998
Barium AMTOF-06-1298-01 Background Habitat mg/kg = 215 1998
Barium NR-238 Background Habitat mg/Kg = 212 2002
Barium NR-239 Background Habitat mg/Kg = 225 2002
Barium NR-500-0800-01 Background Habitat mg/kg = 240 2000
Barium NR-501-0800-01 Background Habitat mg/kg = 266 2000
Barium NR-502-0800-01 Background Habitat mg/kg = 239 2000
Barium NR-503-0800-01 Background Habitat mg/kg = 257 2000
Barium NR-504-0800-01 Background Habitat mg/kg = 242 2000
Barium NR-505-0800-01 Background Habitat mg/kg = 266 2000
Barium NR-506-0800-01 Background Habitat mg/kg = 275 2000
Barium NR-507-0800-01 Background Habitat mg/kg = 184 2000
Barium NR-508-0800-01 Background Habitat mg/kg = 218 2000
Barium NR-509-0800-01 Background Habitat mg/kg = 344 2000
Barium NR-510-0800-01 Background Habitat mg/kg = 158 2000
Barium NR-511-0800-01 Background Habitat mg/kg = 180 2000
Barium NR-512-0800-01 Background Habitat mg/kg = 187 2000
Barium NR-513-0800-01 Background Habitat mg/kg = 205 2000
Barium NR-514-0800-01 Background Habitat mg/kg = 223 2000
Barium NR-515-0800-01 Background Habitat mg/kg = 194 2000
Barium NR-516-0800-01 Background Habitat mg/kg = 339 2000
Barium NR-517-0800-01 Background Habitat mg/kg = 246 2000
Barium NR-518-0800-01 Background Habitat mg/kg = 270 2000
Barium NR-519-0800-01 Background Habitat mg/kg = 370 2000
Barium NR-520-0800-01 Background Habitat mg/kg = 313 2000
Barium NR-521-0800-01 Background Habitat mg/kg = 334 2000
Barium NR-522-0800-01 Background Habitat mg/kg = 336 2000
Barium NR-523-0800-01 Background Habitat mg/kg = 341 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 6 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Barium NR-524-0800-01 Background Habitat mg/kg = 344 2000
Barium NR-525-0800-01 Background Habitat mg/kg = 309 2000
Barium NR-536 Background Habitat mg/Kg = 275 2004
Barium NR-537 Background Habitat mg/Kg = 244 2004
Barium UTNCBU-01-OCT97-01 Background Habitat mg/kg = 217 1997
Barium UTNCBU-02-OCT97-01 Background Habitat mg/kg = 288 1997
Barium UTNCBU-03-1298-01 Background Habitat mg/kg = 227 1998
Barium UTNCBU-04-1298-01 Background Habitat mg/kg = 221 1998
Barium UTNCBU-05-1298-01 Background Habitat mg/kg = 196 1998
Barium UTNCBU-06-1298-01 Background Habitat mg/kg = 208 1998
Barium UTNEB-03-1298-01 Background Habitat mg/kg = 426 1998
Barium UTNEB-04-1298-01 Background Habitat mg/kg = 255 1998
Barium UTNEB-05-1298-01 Background Habitat mg/kg = 263 1998
Barium UTNEB-06-1298-01 Background Habitat mg/kg = 270 1998
Barium UTNERB-01-OCT97-01 Background Habitat mg/kg = 270 1997
Barium UTNERB-02-OCT97-01 Background Habitat mg/kg = 316 1997
Barium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 266 1997
Barium UTNOCB-02-OCT97-01 Background Habitat mg/kg = 237 1997
Barium UTNOCBG-03-1298-01 Background Habitat mg/kg = 274 1998
Barium UTNOCBG-04-1298-01 Background Habitat mg/kg = 283 1998
Barium UTNOCBG-05-1298-01 Background Habitat mg/kg = 277 1998
Barium UTNOCBG-06-1298-01 Background Habitat mg/kg = 332 1998
Barium NR-226 OnSite Habitat mg/Kg = 152 2002
Barium NR-227 OnSite Habitat mg/Kg = 187 2002
Barium NR-228 OnSite OB/OD mg/Kg = 180 2002
Barium NR-229 OnSite Habitat mg/Kg = 205 2002
Barium NR-230 OnSite Habitat mg/Kg = 247 2002
Barium NR-231 OnSite OB/OD mg/Kg = 212 2002
Barium NR-232 OnSite Habitat mg/Kg = 215 2002
Barium NR-233 OnSite Habitat mg/Kg = 204 2002
Barium NR-234 OnSite Habitat mg/Kg = 218 2002
Barium NR-235 OnSite Habitat mg/Kg = 222 2002
Barium NR-236 OnSite Habitat mg/Kg = 206 2002
Barium NR-237 OnSite Habitat mg/Kg = 192 2002
Barium NR-526 OnSite Habitat mg/Kg = 218 2004
Barium NR-527 OnSite Habitat mg/Kg = 228 2004
Barium NR-528 OnSite Habitat mg/Kg = 191 2004
Barium NR-529 OnSite Habitat mg/Kg = 336 2004
Barium NR-530 OnSite Habitat mg/Kg = 220 2004
Barium NR-531 OnSite OB/OD mg/Kg = 196 2004
Barium NR-532 OnSite OB/OD mg/Kg = 187 2004
Barium NR-533 OnSite OB/OD mg/Kg = 211 2004
Barium NR-534 OnSite OB/OD mg/Kg = 194 2004
Barium NR-535 OnSite OB/OD mg/Kg = 187 2004
Barium SS1 OnSite OB/OD mg/Kg = 140 1991
Barium SS10 OnSite OB/OD mg/Kg = 190 1991
Barium SS11 OnSite OB/OD mg/Kg = 240 1991
Barium SS12 OnSite OB/OD mg/Kg = 200 1991
Barium SS13 OnSite OB/OD mg/Kg = 640 1991
Barium SS14 OnSite OB/OD mg/Kg = 190 1991
Barium SS15 OnSite OB/OD mg/Kg = 200 1991
Barium SS16 OnSite Habitat mg/Kg = 230 1991
Barium SS17 OnSite Habitat mg/Kg = 210 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 7 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Barium SS18 OnSite Habitat mg/Kg = 220 1991
Barium SS19 OnSite Habitat mg/Kg = 180 1991
Barium SS2 OnSite OB/OD mg/Kg = 110 1991
Barium SS20 OnSite Habitat mg/Kg = 190 1991
Barium SS3 OnSite OB/OD mg/Kg = 160 1991
Barium SS4 OnSite OB/OD mg/Kg = 170 1991
Barium SS5 OnSite OB/OD mg/Kg = 240 1991
Barium SS6 OnSite OB/OD mg/Kg = 220 1991
Barium SS7 OnSite OB/OD mg/Kg = 200 1991
Barium SS8 OnSite OB/OD mg/Kg = 200 1991
Barium SS9 OnSite OB/OD mg/Kg = 210 1991
Barium TTU-SS01S OnSite OB/OD mg/Kg = 153 1989
Barium TTU-SS02S OnSite OB/OD mg/Kg = 162 1989
Barium TTU-SS03S OnSite OB/OD mg/Kg = 161 1989
Barium TTU-SS04S(D) OnSite OB/OD mg/Kg = 136 1989
Barium TTU-SS05S OnSite OB/OD mg/Kg = 159 1989
Barium TTU-SS06S(BG) OnSite Habitat mg/Kg = 181 1989
Beryllium AMTOF-01-1298-01 Background Habitat mg/kg = 0.209 1998
Beryllium AMTOF-02-1298-01 Background Habitat mg/kg = 0.204 1998
Beryllium AMTOF-03-1298-01 Background Habitat mg/kg = 0.16 1998
Beryllium AMTOF-04-1298-01 Background Habitat mg/kg = 0.206 1998
Beryllium AMTOF-05-1298-01 Background Habitat mg/kg = 0.204 1998
Beryllium AMTOF-06-1298-01 Background Habitat mg/kg = 0.19 1998
Beryllium NR-238 Background Habitat mg/Kg = 0.65 2002
Beryllium NR-239 Background Habitat mg/Kg = 0.55 2002
Beryllium NR-500-0800-01 Background Habitat mg/kg = 0.562 2000
Beryllium NR-501-0800-01 Background Habitat mg/kg = 0.432 2000
Beryllium NR-502-0800-01 Background Habitat mg/kg = 0.606 2000
Beryllium NR-503-0800-01 Background Habitat mg/kg = 0.576 2000
Beryllium NR-504-0800-01 Background Habitat mg/kg = 0.525 2000
Beryllium NR-505-0800-01 Background Habitat mg/kg = 0.603 2000
Beryllium NR-506-0800-01 Background Habitat mg/kg = 0.565 2000
Beryllium NR-507-0800-01 Background Habitat mg/kg = 0.505 2000
Beryllium NR-508-0800-01 Background Habitat mg/kg = 0.502 2000
Beryllium NR-509-0800-01 Background Habitat mg/kg = 0.526 2000
Beryllium NR-510-0800-01 Background Habitat mg/kg = 0.393 2000
Beryllium NR-511-0800-01 Background Habitat mg/kg = 0.525 2000
Beryllium NR-512-0800-01 Background Habitat mg/kg = 0.689 2000
Beryllium NR-513-0800-01 Background Habitat mg/kg = 0.576 2000
Beryllium NR-514-0800-01 Background Habitat mg/kg = 0.537 2000
Beryllium NR-515-0800-01 Background Habitat mg/kg = 0.209 2000
Beryllium NR-516-0800-01 Background Habitat mg/kg = 0.732 2000
Beryllium NR-517-0800-01 Background Habitat mg/kg = 0.361 2000
Beryllium NR-518-0800-01 Background Habitat mg/kg = 0.179 2000
Beryllium NR-519-0800-01 Background Habitat mg/kg = 0.396 2000
Beryllium NR-520-0800-01 Background Habitat mg/kg = 0.368 2000
Beryllium NR-521-0800-01 Background Habitat mg/kg = 0.305 2000
Beryllium NR-522-0800-01 Background Habitat mg/kg = 0.568 2000
Beryllium NR-523-0800-01 Background Habitat mg/kg = 0.465 2000
Beryllium NR-524-0800-01 Background Habitat mg/kg = 0.46 2000
Beryllium NR-525-0800-01 Background Habitat mg/kg = 0.399 2000
Beryllium NR-536 Background Habitat mg/Kg J 0.79 2004
Beryllium NR-537 Background Habitat mg/Kg J 0.89 2004
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 8 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Beryllium UTNCBU-01-OCT97-01 Background Habitat mg/kg = 0.639 1997
Beryllium UTNCBU-02-OCT97-01 Background Habitat mg/kg = 0.582 1997
Beryllium UTNCBU-03-1298-01 Background Habitat mg/kg U 0.0067 0.0134 1998
Beryllium UTNCBU-04-1298-01 Background Habitat mg/kg U 0.0068 0.0136 1998
Beryllium UTNCBU-05-1298-01 Background Habitat mg/kg U 0.0058 0.0116 1998
Beryllium UTNCBU-06-1298-01 Background Habitat mg/kg U 0.00755 0.0151 1998
Beryllium UTNEB-03-1298-01 Background Habitat mg/kg U 0.0056 0.0112 1998
Beryllium UTNEB-04-1298-01 Background Habitat mg/kg U 0.00645 0.0129 1998
Beryllium UTNEB-05-1298-01 Background Habitat mg/kg U 0.00535 0.0107 1998
Beryllium UTNEB-06-1298-01 Background Habitat mg/kg U 0.00735 0.0147 1998
Beryllium UTNERB-01-OCT97-01 Background Habitat mg/kg = 1.05 1997
Beryllium UTNERB-02-OCT97-01 Background Habitat mg/kg = 0.885 1997
Beryllium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 0.761 1997
Beryllium UTNOCB-02-OCT97-01 Background Habitat mg/kg = 0.773 1997
Beryllium UTNOCBG-03-1298-01 Background Habitat mg/kg = 0.16 1998
Beryllium UTNOCBG-04-1298-01 Background Habitat mg/kg = 0.22 1998
Beryllium UTNOCBG-05-1298-01 Background Habitat mg/kg J 0.0839 1998
Beryllium UTNOCBG-06-1298-01 Background Habitat mg/kg = 0.248 1998
Beryllium NR-226 OnSite Habitat mg/Kg = 0.3 2002
Beryllium NR-227 OnSite Habitat mg/Kg = 0.44 2002
Beryllium NR-228 OnSite OB/OD mg/Kg = 0.58 2002
Beryllium NR-229 OnSite Habitat mg/Kg = 0.71 2002
Beryllium NR-230 OnSite Habitat mg/Kg = 0.61 2002
Beryllium NR-231 OnSite OB/OD mg/Kg = 0.65 2002
Beryllium NR-232 OnSite Habitat mg/Kg = 0.7 2002
Beryllium NR-233 OnSite Habitat mg/Kg = 0.46 2002
Beryllium NR-234 OnSite Habitat mg/Kg = 0.68 2002
Beryllium NR-235 OnSite Habitat mg/Kg = 0.61 2002
Beryllium NR-236 OnSite Habitat mg/Kg = 0.57 2002
Beryllium NR-237 OnSite Habitat mg/Kg = 0.52 2002
Beryllium NR-526 OnSite Habitat mg/Kg J 0.45 2004
Beryllium NR-527 OnSite Habitat mg/Kg J 0.72 2004
Beryllium NR-528 OnSite Habitat mg/Kg J 0.44 2004
Beryllium NR-529 OnSite Habitat mg/Kg J 0.57 2004
Beryllium NR-530 OnSite Habitat mg/Kg J 0.55 2004
Beryllium NR-531 OnSite OB/OD mg/Kg J 0.28 2004
Beryllium NR-532 OnSite OB/OD mg/Kg J 0.28 2004
Beryllium NR-533 OnSite OB/OD mg/Kg J 0.55 2004
Beryllium NR-534 OnSite OB/OD mg/Kg J 0.47 2004
Beryllium NR-535 OnSite OB/OD mg/Kg J 0.48 2004
Beryllium SS1 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS10 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS11 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS12 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS13 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS14 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS15 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS16 OnSite Habitat mg/Kg U 0.5 1 1991
Beryllium SS17 OnSite Habitat mg/Kg U 0.5 1 1991
Beryllium SS18 OnSite Habitat mg/Kg U 0.5 1 1991
Beryllium SS19 OnSite Habitat mg/Kg U 0.5 1 1991
Beryllium SS2 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS20 OnSite Habitat mg/Kg U 0.5 1 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 9 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Beryllium SS3 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS4 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS5 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS6 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS7 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS8 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium SS9 OnSite OB/OD mg/Kg U 0.5 1 1991
Beryllium TTU-SS01S OnSite OB/OD mg/Kg U 0.085 0.17 1989
Beryllium TTU-SS02S OnSite OB/OD mg/Kg U 0.075 0.15 1989
Beryllium TTU-SS03S OnSite OB/OD mg/Kg U 0.085 0.17 1989
Beryllium TTU-SS04S(D) OnSite OB/OD mg/Kg U 0.085 0.17 1989
Beryllium TTU-SS05S OnSite OB/OD mg/Kg U 0.08 0.16 1989
Beryllium TTU-SS06S(BG) OnSite Habitat mg/Kg = 0.3 1989
Bismuth AMTOF-01-1298-01 Background Habitat mg/kg U 0.1275 0.255 1998
Bismuth AMTOF-02-1298-01 Background Habitat mg/kg U 0.0955 0.191 1998
Bismuth AMTOF-03-1298-01 Background Habitat mg/kg J 0.0741 1998
Bismuth AMTOF-04-1298-01 Background Habitat mg/kg U 0.1225 0.245 1998
Bismuth AMTOF-05-1298-01 Background Habitat mg/kg U 0.1245 0.249 1998
Bismuth AMTOF-06-1298-01 Background Habitat mg/kg U 0.125 0.25 1998
Bismuth NR-500-0800-01 Background Habitat mg/kg J 0.436 2000
Bismuth NR-501-0800-01 Background Habitat mg/kg U 0.123 0.246 2000
Bismuth NR-502-0800-01 Background Habitat mg/kg J 0.481 2000
Bismuth NR-503-0800-01 Background Habitat mg/kg U 0.088 0.176 2000
Bismuth NR-504-0800-01 Background Habitat mg/kg U 0.116 0.232 2000
Bismuth NR-505-0800-01 Background Habitat mg/kg U 0.126 0.252 2000
Bismuth NR-506-0800-01 Background Habitat mg/kg U 0.089 0.178 2000
Bismuth NR-507-0800-01 Background Habitat mg/kg U 0.0975 0.195 2000
Bismuth NR-508-0800-01 Background Habitat mg/kg U 0.0324 0.0648 2000
Bismuth NR-509-0800-01 Background Habitat mg/kg U 0.106 0.212 2000
Bismuth NR-510-0800-01 Background Habitat mg/kg J 0.301 2000
Bismuth NR-511-0800-01 Background Habitat mg/kg J 0.329 2000
Bismuth NR-512-0800-01 Background Habitat mg/kg U 0.1055 0.211 2000
Bismuth NR-513-0800-01 Background Habitat mg/kg U 0.094 0.188 2000
Bismuth NR-514-0800-01 Background Habitat mg/kg U 0.1135 0.227 2000
Bismuth NR-515-0800-01 Background Habitat mg/kg U 0.022 0.044 2000
Bismuth NR-516-0800-01 Background Habitat mg/kg U 0.1255 0.251 2000
Bismuth NR-517-0800-01 Background Habitat mg/kg U 0.01945 0.0389 2000
Bismuth NR-518-0800-01 Background Habitat mg/kg U 0.0328 0.0656 2000
Bismuth NR-519-0800-01 Background Habitat mg/kg U 0.193 0.386 2000
Bismuth NR-520-0800-01 Background Habitat mg/kg U 0.03555 0.0711 2000
Bismuth NR-521-0800-01 Background Habitat mg/kg U 0.003625 0.00725 2000
Bismuth NR-522-0800-01 Background Habitat mg/kg U 0.0825 0.165 2000
Bismuth NR-523-0800-01 Background Habitat mg/kg U 0.124 0.248 2000
Bismuth NR-524-0800-01 Background Habitat mg/kg U 0.234 0.468 2000
Bismuth NR-525-0800-01 Background Habitat mg/kg U 0.2035 0.407 2000
Bismuth UTNCBU-01-OCT97-01 Background Habitat mg/kg U 0.0745 0.149 1997
Bismuth UTNCBU-02-OCT97-01 Background Habitat mg/kg U 0.2115 0.423 1997
Bismuth UTNCBU-03-1298-01 Background Habitat mg/kg U 0.218 0.436 1998
Bismuth UTNCBU-04-1298-01 Background Habitat mg/kg U 0.2385 0.477 1998
Bismuth UTNCBU-05-1298-01 Background Habitat mg/kg J 0.0411 1998
Bismuth UTNCBU-06-1298-01 Background Habitat mg/kg J 0.0757 1998
Bismuth UTNEB-03-1298-01 Background Habitat mg/kg J 0.206 1998
Bismuth UTNEB-04-1298-01 Background Habitat mg/kg U 0.259 0.518 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 10 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Bismuth UTNEB-05-1298-01 Background Habitat mg/kg U 0.212 0.424 1998
Bismuth UTNEB-06-1298-01 Background Habitat mg/kg U 0.2185 0.437 1998
Bismuth UTNERB-01-OCT97-01 Background Habitat mg/kg U 0.2545 0.509 1997
Bismuth UTNERB-02-OCT97-01 Background Habitat mg/kg U 0.258 0.516 1997
Bismuth UTNOCB-01-OCT97-01 Background Habitat mg/kg U 0.233 0.466 1997
Bismuth UTNOCB-02-OCT97-01 Background Habitat mg/kg U 0.196 0.392 1997
Bismuth UTNOCBG-03-1298-01 Background Habitat mg/kg U 0.237 0.474 1998
Bismuth UTNOCBG-04-1298-01 Background Habitat mg/kg U 0.227 0.454 1998
Bismuth UTNOCBG-05-1298-01 Background Habitat mg/kg U 0.2195 0.439 1998
Bismuth UTNOCBG-06-1298-01 Background Habitat mg/kg U 0.1635 0.327 1998
Boron AMTOF-01-1298-01 Background Habitat mg/kg = 32.1 1998
Boron AMTOF-02-1298-01 Background Habitat mg/kg = 23.1 1998
Boron AMTOF-03-1298-01 Background Habitat mg/kg = 33.6 1998
Boron AMTOF-04-1298-01 Background Habitat mg/kg = 39.5 1998
Boron AMTOF-05-1298-01 Background Habitat mg/kg = 28.6 1998
Boron AMTOF-06-1298-01 Background Habitat mg/kg = 32.4 1998
Boron NR-500-0800-01 Background Habitat mg/kg = 45.3 2000
Boron NR-501-0800-01 Background Habitat mg/kg = 73 2000
Boron NR-502-0800-01 Background Habitat mg/kg = 55.6 2000
Boron NR-503-0800-01 Background Habitat mg/kg = 67.3 2000
Boron NR-504-0800-01 Background Habitat mg/kg = 93.6 2000
Boron NR-505-0800-01 Background Habitat mg/kg = 124 2000
Boron NR-506-0800-01 Background Habitat mg/kg = 53.6 2000
Boron NR-507-0800-01 Background Habitat mg/kg = 24.7 2000
Boron NR-508-0800-01 Background Habitat mg/kg = 28.5 2000
Boron NR-509-0800-01 Background Habitat mg/kg = 29.3 2000
Boron NR-510-0800-01 Background Habitat mg/kg = 14.8 2000
Boron NR-511-0800-01 Background Habitat mg/kg = 25.1 2000
Boron NR-512-0800-01 Background Habitat mg/kg = 28.2 2000
Boron NR-513-0800-01 Background Habitat mg/kg = 31.7 2000
Boron NR-514-0800-01 Background Habitat mg/kg = 147 2000
Boron NR-515-0800-01 Background Habitat mg/kg = 170 2000
Boron NR-516-0800-01 Background Habitat mg/kg = 27.5 2000
Boron NR-517-0800-01 Background Habitat mg/kg = 619 2000
Boron NR-518-0800-01 Background Habitat mg/kg = 118 2000
Boron NR-519-0800-01 Background Habitat mg/kg = 55.7 2000
Boron NR-520-0800-01 Background Habitat mg/kg = 57.1 2000
Boron NR-521-0800-01 Background Habitat mg/kg = 55.5 2000
Boron NR-522-0800-01 Background Habitat mg/kg = 54.8 2000
Boron NR-523-0800-01 Background Habitat mg/kg = 23.1 2000
Boron NR-524-0800-01 Background Habitat mg/kg = 37.7 2000
Boron NR-525-0800-01 Background Habitat mg/kg = 27.1 2000
Boron UTNCBU-01-OCT97-01 Background Habitat mg/kg = 46.7 1997
Boron UTNCBU-02-OCT97-01 Background Habitat mg/kg = 41.5 1997
Boron UTNCBU-03-1298-01 Background Habitat mg/kg = 45.3 1998
Boron UTNCBU-04-1298-01 Background Habitat mg/kg = 47.7 1998
Boron UTNCBU-05-1298-01 Background Habitat mg/kg = 32.9 1998
Boron UTNCBU-06-1298-01 Background Habitat mg/kg = 28 1998
Boron UTNEB-03-1298-01 Background Habitat mg/kg = 32.4 1998
Boron UTNEB-04-1298-01 Background Habitat mg/kg = 54.3 1998
Boron UTNEB-05-1298-01 Background Habitat mg/kg = 53.3 1998
Boron UTNEB-06-1298-01 Background Habitat mg/kg = 34.6 1998
Boron UTNERB-01-OCT97-01 Background Habitat mg/kg = 169 1997
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 11 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Boron UTNERB-02-OCT97-01 Background Habitat mg/kg = 101 1997
Boron UTNOCB-01-OCT97-01 Background Habitat mg/kg = 71.6 1997
Boron UTNOCB-02-OCT97-01 Background Habitat mg/kg = 145 1997
Boron UTNOCBG-03-1298-01 Background Habitat mg/kg = 34.6 1998
Boron UTNOCBG-04-1298-01 Background Habitat mg/kg = 48.3 1998
Boron UTNOCBG-05-1298-01 Background Habitat mg/kg = 40.8 1998
Boron UTNOCBG-06-1298-01 Background Habitat mg/kg = 52 1998
Cadmium AMTOF-01-1298-01 Background Habitat mg/kg = 0.347 1998
Cadmium AMTOF-02-1298-01 Background Habitat mg/kg = 0.384 1998
Cadmium AMTOF-03-1298-01 Background Habitat mg/kg = 0.263 1998
Cadmium AMTOF-04-1298-01 Background Habitat mg/kg = 0.162 1998
Cadmium AMTOF-05-1298-01 Background Habitat mg/kg = 0.288 1998
Cadmium AMTOF-06-1298-01 Background Habitat mg/kg = 0.247 1998
Cadmium NR-238 Background Habitat mg/Kg = 0.71 2002
Cadmium NR-239 Background Habitat mg/Kg = 0.67 2002
Cadmium NR-500-0800-01 Background Habitat mg/kg U 0.01285 0.0257 2000
Cadmium NR-501-0800-01 Background Habitat mg/kg U 0.017 0.034 2000
Cadmium NR-502-0800-01 Background Habitat mg/kg U 0.012 0.024 2000
Cadmium NR-503-0800-01 Background Habitat mg/kg J 0.0336 2000
Cadmium NR-504-0800-01 Background Habitat mg/kg U 0.002915 0.00583 2000
Cadmium NR-505-0800-01 Background Habitat mg/kg U 0.0195 0.039 2000
Cadmium NR-506-0800-01 Background Habitat mg/kg J 0.0976 2000
Cadmium NR-507-0800-01 Background Habitat mg/kg J 0.107 2000
Cadmium NR-508-0800-01 Background Habitat mg/kg U 0.0117 0.0234 2000
Cadmium NR-509-0800-01 Background Habitat mg/kg J 0.0575 2000
Cadmium NR-510-0800-01 Background Habitat mg/kg J 0.148 2000
Cadmium NR-511-0800-01 Background Habitat mg/kg = 0.296 2000
Cadmium NR-512-0800-01 Background Habitat mg/kg J 0.0626 2000
Cadmium NR-513-0800-01 Background Habitat mg/kg J 0.134 2000
Cadmium NR-514-0800-01 Background Habitat mg/kg U 0.02015 0.0403 2000
Cadmium NR-515-0800-01 Background Habitat mg/kg U 0.02055 0.0411 2000
Cadmium NR-516-0800-01 Background Habitat mg/kg U 0.02585 0.0517 2000
Cadmium NR-517-0800-01 Background Habitat mg/kg U 0.01945 0.0389 2000
Cadmium NR-518-0800-01 Background Habitat mg/kg U 0.01835 0.0367 2000
Cadmium NR-519-0800-01 Background Habitat mg/kg U 0.02665 0.0533 2000
Cadmium NR-520-0800-01 Background Habitat mg/kg U 0.02715 0.0543 2000
Cadmium NR-521-0800-01 Background Habitat mg/kg U 0.02175 0.0435 2000
Cadmium NR-522-0800-01 Background Habitat mg/kg U 0.02205 0.0441 2000
Cadmium NR-523-0800-01 Background Habitat mg/kg U 0.02105 0.0421 2000
Cadmium NR-524-0800-01 Background Habitat mg/kg U 0.0323 0.0646 2000
Cadmium NR-525-0800-01 Background Habitat mg/kg U 0.0278 0.0556 2000
Cadmium NR-536 Background Habitat mg/Kg UB 0.095 0.19 2004
Cadmium NR-537 Background Habitat mg/Kg J 0.35 2004
Cadmium UTNCBU-01-OCT97-01 Background Habitat mg/kg = 0.26 1997
Cadmium UTNCBU-02-OCT97-01 Background Habitat mg/kg = 0.249 1997
Cadmium UTNCBU-03-1298-01 Background Habitat mg/kg = 0.466 1998
Cadmium UTNCBU-04-1298-01 Background Habitat mg/kg = 0.5 1998
Cadmium UTNCBU-05-1298-01 Background Habitat mg/kg = 0.311 1998
Cadmium UTNCBU-06-1298-01 Background Habitat mg/kg = 0.318 1998
Cadmium UTNEB-03-1298-01 Background Habitat mg/kg = 0.448 1998
Cadmium UTNEB-04-1298-01 Background Habitat mg/kg = 0.523 1998
Cadmium UTNEB-05-1298-01 Background Habitat mg/kg = 0.446 1998
Cadmium UTNEB-06-1298-01 Background Habitat mg/kg = 0.35 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 12 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Cadmium UTNERB-01-OCT97-01 Background Habitat mg/kg = 0.239 1997
Cadmium UTNERB-02-OCT97-01 Background Habitat mg/kg = 0.267 1997
Cadmium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 0.242 1997
Cadmium UTNOCB-02-OCT97-01 Background Habitat mg/kg = 0.427 1997
Cadmium UTNOCBG-03-1298-01 Background Habitat mg/kg = 0.269 1998
Cadmium UTNOCBG-04-1298-01 Background Habitat mg/kg = 0.218 1998
Cadmium UTNOCBG-05-1298-01 Background Habitat mg/kg = 0.217 1998
Cadmium UTNOCBG-06-1298-01 Background Habitat mg/kg = 0.376 1998
Cadmium NR-226 OnSite Habitat mg/Kg = 0.73 2002
Cadmium NR-227 OnSite Habitat mg/Kg = 0.6 2002
Cadmium NR-228 OnSite OB/OD mg/Kg = 0.78 2002
Cadmium NR-229 OnSite Habitat mg/Kg = 0.57 2002
Cadmium NR-230 OnSite Habitat mg/Kg = 0.92 2002
Cadmium NR-231 OnSite OB/OD mg/Kg = 0.83 2002
Cadmium NR-232 OnSite Habitat mg/Kg = 0.83 2002
Cadmium NR-233 OnSite Habitat mg/Kg = 0.34 2002
Cadmium NR-234 OnSite Habitat mg/Kg = 0.8 2002
Cadmium NR-235 OnSite Habitat mg/Kg = 0.83 2002
Cadmium NR-236 OnSite Habitat mg/Kg = 0.81 2002
Cadmium NR-237 OnSite Habitat mg/Kg = 0.59 2002
Cadmium NR-526 OnSite Habitat mg/Kg UB 0.1 0.2 2004
Cadmium NR-527 OnSite Habitat mg/Kg U 0.06 0.12 2004
Cadmium NR-528 OnSite Habitat mg/Kg J 0.38 2004
Cadmium NR-529 OnSite Habitat mg/Kg UB 0.09 0.18 2004
Cadmium NR-530 OnSite Habitat mg/Kg U 0.07 0.14 2004
Cadmium NR-531 OnSite OB/OD mg/Kg J 0.27 2004
Cadmium NR-532 OnSite OB/OD mg/Kg J 0.55 2004
Cadmium NR-533 OnSite OB/OD mg/Kg U 0.06 0.12 2004
Cadmium NR-534 OnSite OB/OD mg/Kg U 0.055 0.11 2004
Cadmium NR-535 OnSite OB/OD mg/Kg U 0.06 0.12 2004
Cadmium SS1 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS10 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS11 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS12 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS13 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS14 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS15 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS16 OnSite Habitat mg/Kg = 3 1991
Cadmium SS17 OnSite Habitat mg/Kg U 0.5 1 1991
Cadmium SS18 OnSite Habitat mg/Kg U 0.5 1 1991
Cadmium SS19 OnSite Habitat mg/Kg U 0.5 1 1991
Cadmium SS2 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS20 OnSite Habitat mg/Kg U 0.5 1 1991
Cadmium SS3 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS4 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS5 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS6 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS7 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS8 OnSite OB/OD mg/Kg U 0.5 1 1991
Cadmium SS9 OnSite OB/OD mg/Kg = 32 1991
Cadmium TTU-SS01S OnSite OB/OD mg/Kg U 0.42 0.84 1989
Cadmium TTU-SS02S OnSite OB/OD mg/Kg = 2.1 1989
Cadmium TTU-SS03S OnSite OB/OD mg/Kg = 0.98 1989
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 13 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Cadmium TTU-SS04S(D) OnSite OB/OD mg/Kg U 0.435 0.87 1989
Cadmium TTU-SS05S OnSite OB/OD mg/Kg = 0.83 1989
Cadmium TTU-SS06S(BG) OnSite Habitat mg/Kg = 0.9 1989
Chromium AMTOF-01-1298-01 Background Habitat mg/kg = 13.3 1998
Chromium AMTOF-02-1298-01 Background Habitat mg/kg = 17.2 1998
Chromium AMTOF-03-1298-01 Background Habitat mg/kg = 14.6 1998
Chromium AMTOF-04-1298-01 Background Habitat mg/kg = 15.7 1998
Chromium AMTOF-05-1298-01 Background Habitat mg/kg = 10.6 1998
Chromium AMTOF-06-1298-01 Background Habitat mg/kg = 13.4 1998
Chromium NR-238 Background Habitat mg/Kg = 14.3 2002
Chromium NR-239 Background Habitat mg/Kg = 9.6 2002
Chromium NR-500-0800-01 Background Habitat mg/kg = 12.9 2000
Chromium NR-501-0800-01 Background Habitat mg/kg = 9.24 2000
Chromium NR-502-0800-01 Background Habitat mg/kg = 14.5 2000
Chromium NR-503-0800-01 Background Habitat mg/kg = 13.6 2000
Chromium NR-504-0800-01 Background Habitat mg/kg = 12.1 2000
Chromium NR-505-0800-01 Background Habitat mg/kg = 14.3 2000
Chromium NR-506-0800-01 Background Habitat mg/kg = 13 2000
Chromium NR-507-0800-01 Background Habitat mg/kg = 13 2000
Chromium NR-508-0800-01 Background Habitat mg/kg = 11.9 2000
Chromium NR-509-0800-01 Background Habitat mg/kg = 14.1 2000
Chromium NR-510-0800-01 Background Habitat mg/kg = 9.21 2000
Chromium NR-511-0800-01 Background Habitat mg/kg = 14.6 2000
Chromium NR-512-0800-01 Background Habitat mg/kg = 16 2000
Chromium NR-513-0800-01 Background Habitat mg/kg = 14.8 2000
Chromium NR-514-0800-01 Background Habitat mg/kg = 14.6 2000
Chromium NR-515-0800-01 Background Habitat mg/kg = 3.09 2000
Chromium NR-516-0800-01 Background Habitat mg/kg = 15.1 2000
Chromium NR-517-0800-01 Background Habitat mg/kg = 7.05 2000
Chromium NR-518-0800-01 Background Habitat mg/kg = 2.32 2000
Chromium NR-519-0800-01 Background Habitat mg/kg = 7.5 2000
Chromium NR-520-0800-01 Background Habitat mg/kg = 7.59 2000
Chromium NR-521-0800-01 Background Habitat mg/kg = 5.26 2000
Chromium NR-522-0800-01 Background Habitat mg/kg = 13.3 2000
Chromium NR-523-0800-01 Background Habitat mg/kg = 13.1 2000
Chromium NR-524-0800-01 Background Habitat mg/kg = 8.98 2000
Chromium NR-525-0800-01 Background Habitat mg/kg = 6.97 2000
Chromium NR-536 Background Habitat mg/Kg = 12.5 2004
Chromium NR-537 Background Habitat mg/Kg = 14.2 2004
Chromium UTNCBU-01-OCT97-01 Background Habitat mg/kg = 11.8 1997
Chromium UTNCBU-02-OCT97-01 Background Habitat mg/kg = 11.5 1997
Chromium UTNCBU-03-1298-01 Background Habitat mg/kg = 16.1 1998
Chromium UTNCBU-04-1298-01 Background Habitat mg/kg = 16.1 1998
Chromium UTNCBU-05-1298-01 Background Habitat mg/kg = 12 1998
Chromium UTNCBU-06-1298-01 Background Habitat mg/kg = 12.2 1998
Chromium UTNEB-03-1298-01 Background Habitat mg/kg = 14.2 1998
Chromium UTNEB-04-1298-01 Background Habitat mg/kg = 18.4 1998
Chromium UTNEB-05-1298-01 Background Habitat mg/kg = 14.7 1998
Chromium UTNEB-06-1298-01 Background Habitat mg/kg = 13.4 1998
Chromium UTNERB-01-OCT97-01 Background Habitat mg/kg = 20.9 1997
Chromium UTNERB-02-OCT97-01 Background Habitat mg/kg = 19.2 1997
Chromium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 16.9 1997
Chromium UTNOCB-02-OCT97-01 Background Habitat mg/kg = 13.1 1997
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 14 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Chromium UTNOCBG-03-1298-01 Background Habitat mg/kg = 12 1998
Chromium UTNOCBG-04-1298-01 Background Habitat mg/kg = 10.8 1998
Chromium UTNOCBG-05-1298-01 Background Habitat mg/kg = 11.8 1998
Chromium UTNOCBG-06-1298-01 Background Habitat mg/kg = 16 1998
Chromium NR-226 OnSite Habitat mg/Kg = 7 2002
Chromium NR-227 OnSite Habitat mg/Kg = 8.1 2002
Chromium NR-228 OnSite OB/OD mg/Kg = 10.1 2002
Chromium NR-229 OnSite Habitat mg/Kg = 13.2 2002
Chromium NR-230 OnSite Habitat mg/Kg = 11.8 2002
Chromium NR-231 OnSite OB/OD mg/Kg = 11.8 2002
Chromium NR-232 OnSite Habitat mg/Kg = 15.9 2002
Chromium NR-233 OnSite Habitat mg/Kg = 9.8 2002
Chromium NR-234 OnSite Habitat mg/Kg = 12.5 2002
Chromium NR-235 OnSite Habitat mg/Kg = 12.9 2002
Chromium NR-236 OnSite Habitat mg/Kg = 10.1 2002
Chromium NR-237 OnSite Habitat mg/Kg = 10.6 2002
Chromium NR-526 OnSite Habitat mg/Kg = 7.6 2004
Chromium NR-527 OnSite Habitat mg/Kg = 10.7 2004
Chromium NR-528 OnSite Habitat mg/Kg = 6.5 2004
Chromium NR-529 OnSite Habitat mg/Kg = 10.3 2004
Chromium NR-530 OnSite Habitat mg/Kg = 7.5 2004
Chromium NR-531 OnSite OB/OD mg/Kg = 55.3 2004
Chromium NR-532 OnSite OB/OD mg/Kg = 18.3 2004
Chromium NR-533 OnSite OB/OD mg/Kg = 8.7 2004
Chromium NR-534 OnSite OB/OD mg/Kg = 8.4 2004
Chromium NR-535 OnSite OB/OD mg/Kg = 8.5 2004
Chromium SS1 OnSite OB/OD mg/Kg = 13 1991
Chromium SS10 OnSite OB/OD mg/Kg = 15 1991
Chromium SS11 OnSite OB/OD mg/Kg = 18 1991
Chromium SS12 OnSite OB/OD mg/Kg = 18 1991
Chromium SS13 OnSite OB/OD mg/Kg = 14 1991
Chromium SS14 OnSite OB/OD mg/Kg = 17 1991
Chromium SS15 OnSite OB/OD mg/Kg = 16 1991
Chromium SS16 OnSite Habitat mg/Kg = 15 1991
Chromium SS17 OnSite Habitat mg/Kg = 13 1991
Chromium SS18 OnSite Habitat mg/Kg = 16 1991
Chromium SS19 OnSite Habitat mg/Kg = 12 1991
Chromium SS2 OnSite OB/OD mg/Kg = 18 1991
Chromium SS20 OnSite Habitat mg/Kg = 14 1991
Chromium SS3 OnSite OB/OD mg/Kg = 30 1991
Chromium SS4 OnSite OB/OD mg/Kg = 17 1991
Chromium SS5 OnSite OB/OD mg/Kg = 25 1991
Chromium SS6 OnSite OB/OD mg/Kg = 18 1991
Chromium SS7 OnSite OB/OD mg/Kg = 22 1991
Chromium SS8 OnSite OB/OD mg/Kg = 15 1991
Chromium SS9 OnSite OB/OD mg/Kg = 14 1991
Chromium TTU-SS01S OnSite OB/OD mg/Kg = 9.7 1989
Chromium TTU-SS02S OnSite OB/OD mg/Kg = 23.6 1989
Chromium TTU-SS03S OnSite OB/OD mg/Kg = 10.8 1989
Chromium TTU-SS04S(D) OnSite OB/OD mg/Kg = 8.3 1989
Chromium TTU-SS05S OnSite OB/OD mg/Kg = 9 1989
Chromium TTU-SS06S(BG) OnSite Habitat mg/Kg = 12.6 1989
Cobalt AMTOF-01-1298-01 Background Habitat mg/kg = 3.83 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 15 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Cobalt AMTOF-02-1298-01 Background Habitat mg/kg = 3.57 1998
Cobalt AMTOF-03-1298-01 Background Habitat mg/kg = 4.01 1998
Cobalt AMTOF-04-1298-01 Background Habitat mg/kg = 4.18 1998
Cobalt AMTOF-05-1298-01 Background Habitat mg/kg = 5.22 1998
Cobalt AMTOF-06-1298-01 Background Habitat mg/kg = 3.75 1998
Cobalt NR-238 Background Habitat mg/Kg = 4.5 2002
Cobalt NR-239 Background Habitat mg/Kg = 3.6 2002
Cobalt NR-500-0800-01 Background Habitat mg/kg = 4.01 2000
Cobalt NR-501-0800-01 Background Habitat mg/kg = 2.58 2000
Cobalt NR-502-0800-01 Background Habitat mg/kg = 4.22 2000
Cobalt NR-503-0800-01 Background Habitat mg/kg = 4.02 2000
Cobalt NR-504-0800-01 Background Habitat mg/kg = 3.52 2000
Cobalt NR-505-0800-01 Background Habitat mg/kg = 4.2 2000
Cobalt NR-506-0800-01 Background Habitat mg/kg = 3.96 2000
Cobalt NR-507-0800-01 Background Habitat mg/kg = 3.23 2000
Cobalt NR-508-0800-01 Background Habitat mg/kg = 3.52 2000
Cobalt NR-509-0800-01 Background Habitat mg/kg = 4.54 2000
Cobalt NR-510-0800-01 Background Habitat mg/kg = 3.1 2000
Cobalt NR-511-0800-01 Background Habitat mg/kg = 3.67 2000
Cobalt NR-512-0800-01 Background Habitat mg/kg = 4.68 2000
Cobalt NR-513-0800-01 Background Habitat mg/kg = 4 2000
Cobalt NR-514-0800-01 Background Habitat mg/kg = 3.58 2000
Cobalt NR-515-0800-01 Background Habitat mg/kg J 0.837 2000
Cobalt NR-516-0800-01 Background Habitat mg/kg = 6.06 2000
Cobalt NR-517-0800-01 Background Habitat mg/kg = 1.86 2000
Cobalt NR-518-0800-01 Background Habitat mg/kg J 0.678 2000
Cobalt NR-519-0800-01 Background Habitat mg/kg = 2.07 2000
Cobalt NR-520-0800-01 Background Habitat mg/kg = 2.11 2000
Cobalt NR-521-0800-01 Background Habitat mg/kg = 1.6 2000
Cobalt NR-522-0800-01 Background Habitat mg/kg = 3.37 2000
Cobalt NR-523-0800-01 Background Habitat mg/kg = 2.36 2000
Cobalt NR-524-0800-01 Background Habitat mg/kg = 2.1 2000
Cobalt NR-525-0800-01 Background Habitat mg/kg = 1.88 2000
Cobalt NR-536 Background Habitat mg/Kg J 3.1 2004
Cobalt NR-537 Background Habitat mg/Kg = 5.2 2004
Cobalt UTNCBU-01-OCT97-01 Background Habitat mg/kg = 3.03 1997
Cobalt UTNCBU-02-OCT97-01 Background Habitat mg/kg = 2.78 1997
Cobalt UTNCBU-03-1298-01 Background Habitat mg/kg = 4.22 1998
Cobalt UTNCBU-04-1298-01 Background Habitat mg/kg = 4.08 1998
Cobalt UTNCBU-05-1298-01 Background Habitat mg/kg = 3.21 1998
Cobalt UTNCBU-06-1298-01 Background Habitat mg/kg = 3.22 1998
Cobalt UTNEB-03-1298-01 Background Habitat mg/kg = 3.7 1998
Cobalt UTNEB-04-1298-01 Background Habitat mg/kg = 4.76 1998
Cobalt UTNEB-05-1298-01 Background Habitat mg/kg = 3.44 1998
Cobalt UTNEB-06-1298-01 Background Habitat mg/kg = 3.36 1998
Cobalt UTNERB-01-OCT97-01 Background Habitat mg/kg = 5.02 1997
Cobalt UTNERB-02-OCT97-01 Background Habitat mg/kg = 4.17 1997
Cobalt UTNOCB-01-OCT97-01 Background Habitat mg/kg = 3.42 1997
Cobalt UTNOCB-02-OCT97-01 Background Habitat mg/kg = 3.79 1997
Cobalt UTNOCBG-03-1298-01 Background Habitat mg/kg = 3.74 1998
Cobalt UTNOCBG-04-1298-01 Background Habitat mg/kg = 3.93 1998
Cobalt UTNOCBG-05-1298-01 Background Habitat mg/kg = 3.61 1998
Cobalt UTNOCBG-06-1298-01 Background Habitat mg/kg = 4.65 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 16 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Cobalt NR-226 OnSite Habitat mg/Kg = 1.9 2002
Cobalt NR-227 OnSite Habitat mg/Kg = 3 2002
Cobalt NR-228 OnSite OB/OD mg/Kg = 3.9 2002
Cobalt NR-229 OnSite Habitat mg/Kg = 4.9 2002
Cobalt NR-230 OnSite Habitat mg/Kg = 3.6 2002
Cobalt NR-231 OnSite OB/OD mg/Kg = 4.4 2002
Cobalt NR-232 OnSite Habitat mg/Kg = 4.8 2002
Cobalt NR-233 OnSite Habitat mg/Kg = 2.6 2002
Cobalt NR-234 OnSite Habitat mg/Kg = 4.2 2002
Cobalt NR-235 OnSite Habitat mg/Kg = 3.7 2002
Cobalt NR-236 OnSite Habitat mg/Kg = 3.9 2002
Cobalt NR-237 OnSite Habitat mg/Kg = 3.9 2002
Cobalt NR-526 OnSite Habitat mg/Kg J 1.7 2004
Cobalt NR-527 OnSite Habitat mg/Kg J 3.4 2004
Cobalt NR-528 OnSite Habitat mg/Kg J 1.5 2004
Cobalt NR-529 OnSite Habitat mg/Kg J 1.5 2004
Cobalt NR-530 OnSite Habitat mg/Kg J 1 2004
Cobalt NR-531 OnSite OB/OD mg/Kg J 1.1 2004
Cobalt NR-532 OnSite OB/OD mg/Kg J 1.6 2004
Cobalt NR-533 OnSite OB/OD mg/Kg J 2.7 2004
Cobalt NR-534 OnSite OB/OD mg/Kg J 1.9 2004
Cobalt NR-535 OnSite OB/OD mg/Kg J 2.6 2004
Cobalt TTU-SS01S OnSite OB/OD mg/Kg U 2.35 4.7 1989
Cobalt TTU-SS02S OnSite OB/OD mg/Kg U 2.1 4.2 1989
Cobalt TTU-SS03S OnSite OB/OD mg/Kg U 2.4 4.8 1989
Cobalt TTU-SS04S(D) OnSite OB/OD mg/Kg U 2.45 4.9 1989
Cobalt TTU-SS05S OnSite OB/OD mg/Kg U 2.3 4.6 1989
Cobalt TTU-SS06S(BG) OnSite Habitat mg/Kg U 2.3 4.6 1989
Copper AMTOF-01-1298-01 Background Habitat mg/kg = 13 1998
Copper AMTOF-02-1298-01 Background Habitat mg/kg = 11.3 1998
Copper AMTOF-03-1298-01 Background Habitat mg/kg = 12.7 1998
Copper AMTOF-04-1298-01 Background Habitat mg/kg = 13.9 1998
Copper AMTOF-05-1298-01 Background Habitat mg/kg = 14 1998
Copper AMTOF-06-1298-01 Background Habitat mg/kg = 15.1 1998
Copper NR-238 Background Habitat mg/Kg = 17.1 2002
Copper NR-239 Background Habitat mg/Kg = 15.4 2002
Copper NR-500-0800-01 Background Habitat mg/kg = 12.8 2000
Copper NR-501-0800-01 Background Habitat mg/kg = 9.21 2000
Copper NR-502-0800-01 Background Habitat mg/kg = 13.4 2000
Copper NR-503-0800-01 Background Habitat mg/kg = 12.3 2000
Copper NR-504-0800-01 Background Habitat mg/kg = 10.7 2000
Copper NR-505-0800-01 Background Habitat mg/kg = 11.9 2000
Copper NR-506-0800-01 Background Habitat mg/kg = 12.2 2000
Copper NR-507-0800-01 Background Habitat mg/kg = 10.3 2000
Copper NR-508-0800-01 Background Habitat mg/kg = 10.6 2000
Copper NR-509-0800-01 Background Habitat mg/kg = 14.1 2000
Copper NR-510-0800-01 Background Habitat mg/kg = 10.6 2000
Copper NR-511-0800-01 Background Habitat mg/kg = 12.9 2000
Copper NR-512-0800-01 Background Habitat mg/kg = 14.9 2000
Copper NR-513-0800-01 Background Habitat mg/kg = 12.6 2000
Copper NR-514-0800-01 Background Habitat mg/kg = 11.7 2000
Copper NR-515-0800-01 Background Habitat mg/kg = 2.77 2000
Copper NR-516-0800-01 Background Habitat mg/kg = 19.3 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 17 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Copper NR-517-0800-01 Background Habitat mg/kg = 6.25 2000
Copper NR-518-0800-01 Background Habitat mg/kg = 2.49 2000
Copper NR-519-0800-01 Background Habitat mg/kg = 6.81 2000
Copper NR-520-0800-01 Background Habitat mg/kg = 9.26 2000
Copper NR-521-0800-01 Background Habitat mg/kg = 7.04 2000
Copper NR-522-0800-01 Background Habitat mg/kg = 15.9 2000
Copper NR-523-0800-01 Background Habitat mg/kg = 9.63 2000
Copper NR-524-0800-01 Background Habitat mg/kg = 12.4 2000
Copper NR-525-0800-01 Background Habitat mg/kg = 9.21 2000
Copper NR-536 Background Habitat mg/Kg B 19.2 2004
Copper NR-537 Background Habitat mg/Kg B 26.7 2004
Copper UTNCBU-01-OCT97-01 Background Habitat mg/kg = 10.2 1997
Copper UTNCBU-02-OCT97-01 Background Habitat mg/kg = 8.84 1997
Copper UTNCBU-03-1298-01 Background Habitat mg/kg = 14.6 1998
Copper UTNCBU-04-1298-01 Background Habitat mg/kg = 14.6 1998
Copper UTNCBU-05-1298-01 Background Habitat mg/kg = 10.4 1998
Copper UTNCBU-06-1298-01 Background Habitat mg/kg = 11.3 1998
Copper UTNEB-03-1298-01 Background Habitat mg/kg = 12.4 1998
Copper UTNEB-04-1298-01 Background Habitat mg/kg = 16.8 1998
Copper UTNEB-05-1298-01 Background Habitat mg/kg = 13.8 1998
Copper UTNEB-06-1298-01 Background Habitat mg/kg = 12.8 1998
Copper UTNERB-01-OCT97-01 Background Habitat mg/kg = 15.9 1997
Copper UTNERB-02-OCT97-01 Background Habitat mg/kg = 14 1997
Copper UTNOCB-01-OCT97-01 Background Habitat mg/kg = 12.9 1997
Copper UTNOCB-02-OCT97-01 Background Habitat mg/kg = 12.8 1997
Copper UTNOCBG-03-1298-01 Background Habitat mg/kg = 13.9 1998
Copper UTNOCBG-04-1298-01 Background Habitat mg/kg = 11.4 1998
Copper UTNOCBG-05-1298-01 Background Habitat mg/kg = 13.7 1998
Copper UTNOCBG-06-1298-01 Background Habitat mg/kg = 15.4 1998
Copper NR-226 OnSite Habitat mg/Kg = 9.4 2002
Copper NR-227 OnSite Habitat mg/Kg = 11.1 2002
Copper NR-228 OnSite OB/OD mg/Kg = 16.6 2002
Copper NR-229 OnSite Habitat mg/Kg = 15.4 2002
Copper NR-230 OnSite Habitat mg/Kg = 18.6 2002
Copper NR-231 OnSite OB/OD mg/Kg = 18.8 2002
Copper NR-232 OnSite Habitat mg/Kg = 20 2002
Copper NR-233 OnSite Habitat mg/Kg = 10.4 2002
Copper NR-234 OnSite Habitat mg/Kg = 20.7 2002
Copper NR-235 OnSite Habitat mg/Kg = 24.4 2002
Copper NR-236 OnSite Habitat mg/Kg = 20 2002
Copper NR-237 OnSite Habitat mg/Kg = 13.4 2002
Copper NR-526 OnSite Habitat mg/Kg J 61 2004
Copper NR-527 OnSite Habitat mg/Kg B 19.7 2004
Copper NR-528 OnSite Habitat mg/Kg B 13.2 2004
Copper NR-529 OnSite Habitat mg/Kg B 18.5 2004
Copper NR-530 OnSite Habitat mg/Kg B 9.4 2004
Copper NR-531 OnSite OB/OD mg/Kg B 77.6 2004
Copper NR-532 OnSite OB/OD mg/Kg B 16.8 2004
Copper NR-533 OnSite OB/OD mg/Kg B 10.9 2004
Copper NR-534 OnSite OB/OD mg/Kg B 9.6 2004
Copper NR-535 OnSite OB/OD mg/Kg B 10.2 2004
Copper SS1 OnSite OB/OD mg/Kg = 6 1991
Copper SS10 OnSite OB/OD mg/Kg = 52 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 18 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Copper SS11 OnSite OB/OD mg/Kg = 38 1991
Copper SS12 OnSite OB/OD mg/Kg = 79 1991
Copper SS13 OnSite OB/OD mg/Kg = 49 1991
Copper SS14 OnSite OB/OD mg/Kg = 25 1991
Copper SS15 OnSite OB/OD mg/Kg = 12 1991
Copper SS16 OnSite Habitat mg/Kg = 42 1991
Copper SS17 OnSite Habitat mg/Kg = 15 1991
Copper SS18 OnSite Habitat mg/Kg = 15 1991
Copper SS19 OnSite Habitat mg/Kg = 18 1991
Copper SS2 OnSite OB/OD mg/Kg U 0.5 1 1991
Copper SS20 OnSite Habitat mg/Kg = 19 1991
Copper SS3 OnSite OB/OD mg/Kg = 18000 1991
Copper SS4 OnSite OB/OD mg/Kg = 19 1991
Copper SS5 OnSite OB/OD mg/Kg = 410 1991
Copper SS6 OnSite OB/OD mg/Kg = 59 1991
Copper SS7 OnSite OB/OD mg/Kg = 950 1991
Copper SS8 OnSite OB/OD mg/Kg = 30 1991
Copper SS9 OnSite OB/OD mg/Kg = 140 1991
Copper TTU-SS01S OnSite OB/OD mg/Kg U 39 78 1989
Copper TTU-SS02S OnSite OB/OD mg/Kg U 47.35 94.7 1989
Copper TTU-SS03S OnSite OB/OD mg/Kg U 7.65 15.3 1989
Copper TTU-SS04S(D) OnSite OB/OD mg/Kg U 41.3 82.6 1989
Copper TTU-SS05S OnSite OB/OD mg/Kg U 41.85 83.7 1989
Copper TTU-SS06S(BG) OnSite Habitat mg/Kg U 7.05 14.1 1989
Iron AMTOF-01-1298-01 Background Habitat mg/kg = 11500 1998
Iron AMTOF-02-1298-01 Background Habitat mg/kg = 10300 1998
Iron AMTOF-03-1298-01 Background Habitat mg/kg = 12500 1998
Iron AMTOF-04-1298-01 Background Habitat mg/kg = 12900 1998
Iron AMTOF-05-1298-01 Background Habitat mg/kg = 10400 1998
Iron AMTOF-06-1298-01 Background Habitat mg/kg = 11500 1998
Iron NR-238 Background Habitat mg/Kg = 12300 2002
Iron NR-239 Background Habitat mg/Kg = 10000 2002
Iron NR-500-0800-01 Background Habitat mg/kg = 11200 2000
Iron NR-501-0800-01 Background Habitat mg/kg = 6630 2000
Iron NR-502-0800-01 Background Habitat mg/kg = 11600 2000
Iron NR-503-0800-01 Background Habitat mg/kg = 11000 2000
Iron NR-504-0800-01 Background Habitat mg/kg = 9880 2000
Iron NR-505-0800-01 Background Habitat mg/kg = 12800 2000
Iron NR-506-0800-01 Background Habitat mg/kg = 12100 2000
Iron NR-507-0800-01 Background Habitat mg/kg = 9730 2000
Iron NR-508-0800-01 Background Habitat mg/kg = 10500 2000
Iron NR-509-0800-01 Background Habitat mg/kg = 10600 2000
Iron NR-510-0800-01 Background Habitat mg/kg = 8150 2000
Iron NR-511-0800-01 Background Habitat mg/kg = 10300 2000
Iron NR-512-0800-01 Background Habitat mg/kg = 13500 2000
Iron NR-513-0800-01 Background Habitat mg/kg = 11600 2000
Iron NR-514-0800-01 Background Habitat mg/kg = 10000 2000
Iron NR-515-0800-01 Background Habitat mg/kg = 1900 2000
Iron NR-516-0800-01 Background Habitat mg/kg = 13700 2000
Iron NR-517-0800-01 Background Habitat mg/kg = 5320 2000
Iron NR-518-0800-01 Background Habitat mg/kg = 1390 2000
Iron NR-519-0800-01 Background Habitat mg/kg = 4950 2000
Iron NR-520-0800-01 Background Habitat mg/kg = 5430 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 19 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Iron NR-521-0800-01 Background Habitat mg/kg = 3370 2000
Iron NR-522-0800-01 Background Habitat mg/kg = 8550 2000
Iron NR-523-0800-01 Background Habitat mg/kg = 7070 2000
Iron NR-524-0800-01 Background Habitat mg/kg = 5640 2000
Iron NR-525-0800-01 Background Habitat mg/kg = 4610 2000
Iron NR-536 Background Habitat mg/Kg B 13800 2004
Iron NR-537 Background Habitat mg/Kg B 15900 2004
Iron UTNCBU-01-OCT97-01 Background Habitat mg/kg = 9530 1997
Iron UTNCBU-02-OCT97-01 Background Habitat mg/kg = 8730 1997
Iron UTNCBU-03-1298-01 Background Habitat mg/kg = 11700 1998
Iron UTNCBU-04-1298-01 Background Habitat mg/kg = 11400 1998
Iron UTNCBU-05-1298-01 Background Habitat mg/kg = 9030 1998
Iron UTNCBU-06-1298-01 Background Habitat mg/kg = 9000 1998
Iron UTNEB-03-1298-01 Background Habitat mg/kg = 9990 1998
Iron UTNEB-04-1298-01 Background Habitat mg/kg = 13900 1998
Iron UTNEB-05-1298-01 Background Habitat mg/kg = 10300 1998
Iron UTNEB-06-1298-01 Background Habitat mg/kg = 9340 1998
Iron UTNERB-01-OCT97-01 Background Habitat mg/kg = 16200 1997
Iron UTNERB-02-OCT97-01 Background Habitat mg/kg = 13400 1997
Iron UTNOCB-01-OCT97-01 Background Habitat mg/kg = 11800 1997
Iron UTNOCB-02-OCT97-01 Background Habitat mg/kg = 12400 1997
Iron UTNOCBG-03-1298-01 Background Habitat mg/kg = 10600 1998
Iron UTNOCBG-04-1298-01 Background Habitat mg/kg = 9970 1998
Iron UTNOCBG-05-1298-01 Background Habitat mg/kg = 10100 1998
Iron UTNOCBG-06-1298-01 Background Habitat mg/kg = 13100 1998
Iron NR-226 OnSite Habitat mg/Kg = 5450 2002
Iron NR-227 OnSite Habitat mg/Kg = 8210 2002
Iron NR-228 OnSite OB/OD mg/Kg = 9440 2002
Iron NR-229 OnSite Habitat mg/Kg = 12700 2002
Iron NR-230 OnSite Habitat mg/Kg = 11000 2002
Iron NR-231 OnSite OB/OD mg/Kg = 11400 2002
Iron NR-232 OnSite Habitat mg/Kg = 13400 2002
Iron NR-233 OnSite Habitat mg/Kg = 8410 2002
Iron NR-234 OnSite Habitat mg/Kg = 12100 2002
Iron NR-235 OnSite Habitat mg/Kg = 10800 2002
Iron NR-236 OnSite Habitat mg/Kg = 10100 2002
Iron NR-237 OnSite Habitat mg/Kg = 10300 2002
Iron NR-526 OnSite Habitat mg/Kg B 7100 2004
Iron NR-527 OnSite Habitat mg/Kg B 13000 2004
Iron NR-528 OnSite Habitat mg/Kg B 7550 2004
Iron NR-529 OnSite Habitat mg/Kg B 9890 2004
Iron NR-530 OnSite Habitat mg/Kg B 8430 2004
Iron NR-531 OnSite OB/OD mg/Kg B 6570 2004
Iron NR-532 OnSite OB/OD mg/Kg B 4510 2004
Iron NR-533 OnSite OB/OD mg/Kg B 9360 2004
Iron NR-534 OnSite OB/OD mg/Kg B 8170 2004
Iron NR-535 OnSite OB/OD mg/Kg B 9160 2004
Iron SS1 OnSite OB/OD mg/Kg = 9600 1991
Iron SS10 OnSite OB/OD mg/Kg = 12000 1991
Iron SS11 OnSite OB/OD mg/Kg = 14000 1991
Iron SS12 OnSite OB/OD mg/Kg = 14000 1991
Iron SS13 OnSite OB/OD mg/Kg = 12000 1991
Iron SS14 OnSite OB/OD mg/Kg = 15000 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 20 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Iron SS15 OnSite OB/OD mg/Kg = 14000 1991
Iron SS16 OnSite Habitat mg/Kg = 12000 1991
Iron SS17 OnSite Habitat mg/Kg = 13000 1991
Iron SS18 OnSite Habitat mg/Kg = 13000 1991
Iron SS19 OnSite Habitat mg/Kg = 10000 1991
Iron SS2 OnSite OB/OD mg/Kg = 6100 1991
Iron SS20 OnSite Habitat mg/Kg = 14000 1991
Iron SS3 OnSite OB/OD mg/Kg = 6900 1991
Iron SS4 OnSite OB/OD mg/Kg = 7800 1991
Iron SS5 OnSite OB/OD mg/Kg = 15000 1991
Iron SS6 OnSite OB/OD mg/Kg = 14000 1991
Iron SS7 OnSite OB/OD mg/Kg = 14000 1991
Iron SS8 OnSite OB/OD mg/Kg = 11000 1991
Iron SS9 OnSite OB/OD mg/Kg = 11000 1991
Lead AMTOF-01-1298-01 Background Habitat mg/kg = 13.2 1998
Lead AMTOF-02-1298-01 Background Habitat mg/kg = 8.56 1998
Lead AMTOF-03-1298-01 Background Habitat mg/kg = 11.2 1998
Lead AMTOF-04-1298-01 Background Habitat mg/kg = 10.5 1998
Lead AMTOF-05-1298-01 Background Habitat mg/kg = 13 1998
Lead AMTOF-06-1298-01 Background Habitat mg/kg = 12.8 1998
Lead NR-238 Background Habitat mg/Kg = 13.8 2002
Lead NR-239 Background Habitat mg/Kg = 15.9 2002
Lead NR-500-0800-01 Background Habitat mg/kg = 9.5 2000
Lead NR-501-0800-01 Background Habitat mg/kg = 7.76 2000
Lead NR-502-0800-01 Background Habitat mg/kg = 10.4 2000
Lead NR-503-0800-01 Background Habitat mg/kg = 10 2000
Lead NR-504-0800-01 Background Habitat mg/kg = 8.3 2000
Lead NR-505-0800-01 Background Habitat mg/kg = 9.52 2000
Lead NR-506-0800-01 Background Habitat mg/kg = 10.2 2000
Lead NR-507-0800-01 Background Habitat mg/kg = 8.21 2000
Lead NR-508-0800-01 Background Habitat mg/kg = 8.5 2000
Lead NR-509-0800-01 Background Habitat mg/kg = 11 2000
Lead NR-510-0800-01 Background Habitat mg/kg = 12 2000
Lead NR-511-0800-01 Background Habitat mg/kg = 14.1 2000
Lead NR-512-0800-01 Background Habitat mg/kg = 11.7 2000
Lead NR-513-0800-01 Background Habitat mg/kg = 10.1 2000
Lead NR-514-0800-01 Background Habitat mg/kg = 10.2 2000
Lead NR-515-0800-01 Background Habitat mg/kg = 5.42 2000
Lead NR-516-0800-01 Background Habitat mg/kg = 14 2000
Lead NR-517-0800-01 Background Habitat mg/kg = 2.95 2000
Lead NR-518-0800-01 Background Habitat mg/kg = 5.04 2000
Lead NR-519-0800-01 Background Habitat mg/kg = 6.8 2000
Lead NR-520-0800-01 Background Habitat mg/kg = 7.81 2000
Lead NR-521-0800-01 Background Habitat mg/kg = 5.71 2000
Lead NR-522-0800-01 Background Habitat mg/kg = 11.6 2000
Lead NR-523-0800-01 Background Habitat mg/kg = 5.44 2000
Lead NR-524-0800-01 Background Habitat mg/kg = 9 2000
Lead NR-525-0800-01 Background Habitat mg/kg = 7.33 2000
Lead NR-536 Background Habitat mg/Kg = 19.9 2004
Lead NR-537 Background Habitat mg/Kg = 30.5 2004
Lead UTNCBU-01-OCT97-01 Background Habitat mg/kg = 6.6 1997
Lead UTNCBU-02-OCT97-01 Background Habitat mg/kg = 5.99 1997
Lead UTNCBU-03-1298-01 Background Habitat mg/kg = 11 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 21 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Lead UTNCBU-04-1298-01 Background Habitat mg/kg = 11.2 1998
Lead UTNCBU-05-1298-01 Background Habitat mg/kg = 8.28 1998
Lead UTNCBU-06-1298-01 Background Habitat mg/kg = 10 1998
Lead UTNEB-03-1298-01 Background Habitat mg/kg = 10.8 1998
Lead UTNEB-04-1298-01 Background Habitat mg/kg = 12.8 1998
Lead UTNEB-05-1298-01 Background Habitat mg/kg = 8.55 1998
Lead UTNEB-06-1298-01 Background Habitat mg/kg = 11.9 1998
Lead UTNERB-01-OCT97-01 Background Habitat mg/kg = 8.55 1997
Lead UTNERB-02-OCT97-01 Background Habitat mg/kg = 7.19 1997
Lead UTNOCB-01-OCT97-01 Background Habitat mg/kg = 5.34 1997
Lead UTNOCB-02-OCT97-01 Background Habitat mg/kg = 6.66 1997
Lead UTNOCBG-03-1298-01 Background Habitat mg/kg = 13.8 1998
Lead UTNOCBG-04-1298-01 Background Habitat mg/kg = 11.5 1998
Lead UTNOCBG-05-1298-01 Background Habitat mg/kg = 15.9 1998
Lead UTNOCBG-06-1298-01 Background Habitat mg/kg = 10.6 1998
Lead NR-226 OnSite Habitat mg/Kg = 5.6 2002
Lead NR-227 OnSite Habitat mg/Kg = 9.1 2002
Lead NR-228 OnSite OB/OD mg/Kg = 12.5 2002
Lead NR-229 OnSite Habitat mg/Kg = 6.5 2002
Lead NR-230 OnSite Habitat mg/Kg = 20.5 2002
Lead NR-231 OnSite OB/OD mg/Kg = 9 2002
Lead NR-232 OnSite Habitat mg/Kg = 16.9 2002
Lead NR-233 OnSite Habitat mg/Kg = 4.5 2002
Lead NR-234 OnSite Habitat mg/Kg = 14.1 2002
Lead NR-235 OnSite Habitat mg/Kg = 16.3 2002
Lead NR-236 OnSite Habitat mg/Kg = 17.8 2002
Lead NR-237 OnSite Habitat mg/Kg = 10.5 2002
Lead NR-526 OnSite Habitat mg/Kg = 9.7 2004
Lead NR-527 OnSite Habitat mg/Kg = 17.5 2004
Lead NR-528 OnSite Habitat mg/Kg = 15.8 2004
Lead NR-529 OnSite Habitat mg/Kg = 11.8 2004
Lead NR-530 OnSite Habitat mg/Kg = 6 2004
Lead NR-531 OnSite OB/OD mg/Kg = 3.2 2004
Lead NR-532 OnSite OB/OD mg/Kg = 2.8 2004
Lead NR-533 OnSite OB/OD mg/Kg = 6.9 2004
Lead NR-534 OnSite OB/OD mg/Kg = 6.3 2004
Lead NR-535 OnSite OB/OD mg/Kg = 6.2 2004
Lead SS1 OnSite OB/OD mg/Kg = 12 1991
Lead SS10 OnSite OB/OD mg/Kg = 36 1991
Lead SS11 OnSite OB/OD mg/Kg = 30 1991
Lead SS12 OnSite OB/OD mg/Kg = 67 1991
Lead SS13 OnSite OB/OD mg/Kg = 300 1991
Lead SS14 OnSite OB/OD mg/Kg = 24 1991
Lead SS15 OnSite OB/OD mg/Kg = 19 1991
Lead SS16 OnSite Habitat mg/Kg = 34 1991
Lead SS17 OnSite Habitat mg/Kg = 36 1991
Lead SS18 OnSite Habitat mg/Kg = 29 1991
Lead SS19 OnSite Habitat mg/Kg = 28 1991
Lead SS2 OnSite OB/OD mg/Kg U 1 2 1991
Lead SS20 OnSite Habitat mg/Kg = 22 1991
Lead SS3 OnSite OB/OD mg/Kg = 34 1991
Lead SS4 OnSite OB/OD mg/Kg U 1 2 1991
Lead SS5 OnSite OB/OD mg/Kg = 48000 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 22 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Lead SS6 OnSite OB/OD mg/Kg = 80 1991
Lead SS7 OnSite OB/OD mg/Kg = 1500 1991
Lead SS8 OnSite OB/OD mg/Kg = 65 1991
Lead SS9 OnSite OB/OD mg/Kg = 140 1991
Lead TTU-SS01S OnSite OB/OD mg/Kg U 12.4 24.8 1989
Lead TTU-SS02S OnSite OB/OD mg/Kg U 405.5 811 1989
Lead TTU-SS03S OnSite OB/OD mg/Kg U 80 160 1989
Lead TTU-SS04S(D) OnSite OB/OD mg/Kg U 55.5 111 1989
Lead TTU-SS05S OnSite OB/OD mg/Kg U 9.25 18.5 1989
Lead TTU-SS06S(BG) OnSite Habitat mg/Kg U 8.05 16.1 1989
Magnesium AMTOF-01-1298-01 Background Habitat mg/kg = 22700 1998
Magnesium AMTOF-02-1298-01 Background Habitat mg/kg = 16900 1998
Magnesium AMTOF-03-1298-01 Background Habitat mg/kg = 24200 1998
Magnesium AMTOF-04-1298-01 Background Habitat mg/kg = 24200 1998
Magnesium AMTOF-05-1298-01 Background Habitat mg/kg = 18800 1998
Magnesium AMTOF-06-1298-01 Background Habitat mg/kg = 22500 1998
Magnesium NR-238 Background Habitat mg/Kg = 21700 2002
Magnesium NR-239 Background Habitat mg/Kg = 22100 2002
Magnesium NR-500-0800-01 Background Habitat mg/kg = 27600 2000
Magnesium NR-501-0800-01 Background Habitat mg/kg = 40400 2000
Magnesium NR-502-0800-01 Background Habitat mg/kg = 31600 2000
Magnesium NR-503-0800-01 Background Habitat mg/kg = 28200 2000
Magnesium NR-504-0800-01 Background Habitat mg/kg = 27800 2000
Magnesium NR-505-0800-01 Background Habitat mg/kg = 21800 2000
Magnesium NR-506-0800-01 Background Habitat mg/kg = 21100 2000
Magnesium NR-507-0800-01 Background Habitat mg/kg = 17500 2000
Magnesium NR-508-0800-01 Background Habitat mg/kg = 22300 2000
Magnesium NR-509-0800-01 Background Habitat mg/kg = 15500 2000
Magnesium NR-510-0800-01 Background Habitat mg/kg = 18600 2000
Magnesium NR-511-0800-01 Background Habitat mg/kg = 18800 2000
Magnesium NR-512-0800-01 Background Habitat mg/kg = 19700 2000
Magnesium NR-513-0800-01 Background Habitat mg/kg = 16400 2000
Magnesium NR-514-0800-01 Background Habitat mg/kg = 38000 2000
Magnesium NR-515-0800-01 Background Habitat mg/kg = 39700 2000
Magnesium NR-516-0800-01 Background Habitat mg/kg = 22600 2000
Magnesium NR-517-0800-01 Background Habitat mg/kg B 167000 2000
Magnesium NR-518-0800-01 Background Habitat mg/kg = 21100 2000
Magnesium NR-519-0800-01 Background Habitat mg/kg = 25000 2000
Magnesium NR-520-0800-01 Background Habitat mg/kg B 83800 2000
Magnesium NR-521-0800-01 Background Habitat mg/kg = 24200 2000
Magnesium NR-522-0800-01 Background Habitat mg/kg = 34300 2000
Magnesium NR-523-0800-01 Background Habitat mg/kg = 41700 2000
Magnesium NR-524-0800-01 Background Habitat mg/kg = 26400 2000
Magnesium NR-525-0800-01 Background Habitat mg/kg = 17900 2000
Magnesium NR-536 Background Habitat mg/Kg B 29000 2004
Magnesium NR-537 Background Habitat mg/Kg B 31800 2004
Magnesium UTNCBU-01-OCT97-01 Background Habitat mg/kg = 32700 1997
Magnesium UTNCBU-02-OCT97-01 Background Habitat mg/kg = 29500 1997
Magnesium UTNCBU-03-1298-01 Background Habitat mg/kg = 36900 1998
Magnesium UTNCBU-04-1298-01 Background Habitat mg/kg = 35700 1998
Magnesium UTNCBU-05-1298-01 Background Habitat mg/kg = 29800 1998
Magnesium UTNCBU-06-1298-01 Background Habitat mg/kg = 28200 1998
Magnesium UTNEB-03-1298-01 Background Habitat mg/kg = 21800 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 23 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Magnesium UTNEB-04-1298-01 Background Habitat mg/kg = 29700 1998
Magnesium UTNEB-05-1298-01 Background Habitat mg/kg = 32300 1998
Magnesium UTNEB-06-1298-01 Background Habitat mg/kg = 26800 1998
Magnesium UTNERB-01-OCT97-01 Background Habitat mg/kg = 38700 1997
Magnesium UTNERB-02-OCT97-01 Background Habitat mg/kg = 37700 1997
Magnesium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 16500 1997
Magnesium UTNOCB-02-OCT97-01 Background Habitat mg/kg = 23100 1997
Magnesium UTNOCBG-03-1298-01 Background Habitat mg/kg = 20600 1998
Magnesium UTNOCBG-04-1298-01 Background Habitat mg/kg = 20200 1998
Magnesium UTNOCBG-05-1298-01 Background Habitat mg/kg = 19300 1998
Magnesium UTNOCBG-06-1298-01 Background Habitat mg/kg = 24700 1998
Magnesium NR-226 OnSite Habitat mg/Kg = 11500 2002
Magnesium NR-227 OnSite Habitat mg/Kg = 15700 2002
Magnesium NR-228 OnSite OB/OD mg/Kg = 17800 2002
Magnesium NR-229 OnSite Habitat mg/Kg = 22900 2002
Magnesium NR-230 OnSite Habitat mg/Kg = 19800 2002
Magnesium NR-231 OnSite OB/OD mg/Kg = 20600 2002
Magnesium NR-232 OnSite Habitat mg/Kg = 22300 2002
Magnesium NR-233 OnSite Habitat mg/Kg = 12200 2002
Magnesium NR-234 OnSite Habitat mg/Kg = 24300 2002
Magnesium NR-235 OnSite Habitat mg/Kg = 20900 2002
Magnesium NR-236 OnSite Habitat mg/Kg = 20100 2002
Magnesium NR-237 OnSite Habitat mg/Kg = 17200 2002
Magnesium NR-526 OnSite Habitat mg/Kg B 12200 2004
Magnesium NR-527 OnSite Habitat mg/Kg B 22500 2004
Magnesium NR-528 OnSite Habitat mg/Kg B 13900 2004
Magnesium NR-529 OnSite Habitat mg/Kg B 17600 2004
Magnesium NR-530 OnSite Habitat mg/Kg B 14200 2004
Magnesium NR-531 OnSite OB/OD mg/Kg B 11000 2004
Magnesium NR-532 OnSite OB/OD mg/Kg B 10800 2004
Magnesium NR-533 OnSite OB/OD mg/Kg B 14200 2004
Magnesium NR-534 OnSite OB/OD mg/Kg B 11800 2004
Magnesium NR-535 OnSite OB/OD mg/Kg B 11000 2004
Magnesium SS1 OnSite OB/OD mg/Kg = 15000 1991
Magnesium SS10 OnSite OB/OD mg/Kg = 16000 1991
Magnesium SS11 OnSite OB/OD mg/Kg = 22000 1991
Magnesium SS12 OnSite OB/OD mg/Kg = 19000 1991
Magnesium SS13 OnSite OB/OD mg/Kg = 19000 1991
Magnesium SS14 OnSite OB/OD mg/Kg = 18000 1991
Magnesium SS15 OnSite OB/OD mg/Kg = 19000 1991
Magnesium SS16 OnSite Habitat mg/Kg = 17000 1991
Magnesium SS17 OnSite Habitat mg/Kg = 22000 1991
Magnesium SS18 OnSite Habitat mg/Kg = 20000 1991
Magnesium SS19 OnSite Habitat mg/Kg = 17000 1991
Magnesium SS2 OnSite OB/OD mg/Kg = 9700 1991
Magnesium SS20 OnSite Habitat mg/Kg = 22000 1991
Magnesium SS3 OnSite OB/OD mg/Kg = 13000 1991
Magnesium SS4 OnSite OB/OD mg/Kg = 14000 1991
Magnesium SS5 OnSite OB/OD mg/Kg = 14000 1991
Magnesium SS6 OnSite OB/OD mg/Kg = 19000 1991
Magnesium SS7 OnSite OB/OD mg/Kg = 14000 1991
Magnesium SS8 OnSite OB/OD mg/Kg = 14000 1991
Magnesium SS9 OnSite OB/OD mg/Kg = 13000 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 24 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Manganese AMTOF-01-1298-01 Background Habitat mg/kg = 436 1998
Manganese AMTOF-02-1298-01 Background Habitat mg/kg = 313 1998
Manganese AMTOF-03-1298-01 Background Habitat mg/kg = 456 1998
Manganese AMTOF-04-1298-01 Background Habitat mg/kg = 429 1998
Manganese AMTOF-05-1298-01 Background Habitat mg/kg = 386 1998
Manganese AMTOF-06-1298-01 Background Habitat mg/kg = 395 1998
Manganese NR-238 Background Habitat mg/Kg = 432 2002
Manganese NR-239 Background Habitat mg/Kg = 464 2002
Manganese NR-500-0800-01 Background Habitat mg/kg = 356 2000
Manganese NR-501-0800-01 Background Habitat mg/kg = 196 2000
Manganese NR-502-0800-01 Background Habitat mg/kg = 364 2000
Manganese NR-503-0800-01 Background Habitat mg/kg = 338 2000
Manganese NR-504-0800-01 Background Habitat mg/kg = 296 2000
Manganese NR-505-0800-01 Background Habitat mg/kg = 371 2000
Manganese NR-506-0800-01 Background Habitat mg/kg = 331 2000
Manganese NR-507-0800-01 Background Habitat mg/kg = 305 2000
Manganese NR-508-0800-01 Background Habitat mg/kg = 335 2000
Manganese NR-509-0800-01 Background Habitat mg/kg = 351 2000
Manganese NR-510-0800-01 Background Habitat mg/kg = 322 2000
Manganese NR-511-0800-01 Background Habitat mg/kg = 389 2000
Manganese NR-512-0800-01 Background Habitat mg/kg = 403 2000
Manganese NR-513-0800-01 Background Habitat mg/kg = 370 2000
Manganese NR-514-0800-01 Background Habitat mg/kg = 314 2000
Manganese NR-515-0800-01 Background Habitat mg/kg = 60.1 2000
Manganese NR-516-0800-01 Background Habitat mg/kg = 859 2000
Manganese NR-517-0800-01 Background Habitat mg/kg = 138 2000
Manganese NR-518-0800-01 Background Habitat mg/kg = 43.4 2000
Manganese NR-519-0800-01 Background Habitat mg/kg = 183 2000
Manganese NR-520-0800-01 Background Habitat mg/kg = 183 2000
Manganese NR-521-0800-01 Background Habitat mg/kg = 131 2000
Manganese NR-522-0800-01 Background Habitat mg/kg = 223 2000
Manganese NR-523-0800-01 Background Habitat mg/kg = 229 2000
Manganese NR-524-0800-01 Background Habitat mg/kg = 142 2000
Manganese NR-525-0800-01 Background Habitat mg/kg = 106 2000
Manganese NR-536 Background Habitat mg/Kg = 517 2004
Manganese NR-537 Background Habitat mg/Kg = 602 2004
Manganese UTNCBU-01-OCT97-01 Background Habitat mg/kg = 287 1997
Manganese UTNCBU-02-OCT97-01 Background Habitat mg/kg = 274 1997
Manganese UTNCBU-03-1298-01 Background Habitat mg/kg = 396 1998
Manganese UTNCBU-04-1298-01 Background Habitat mg/kg = 396 1998
Manganese UTNCBU-05-1298-01 Background Habitat mg/kg = 309 1998
Manganese UTNCBU-06-1298-01 Background Habitat mg/kg = 318 1998
Manganese UTNEB-03-1298-01 Background Habitat mg/kg = 421 1998
Manganese UTNEB-04-1298-01 Background Habitat mg/kg = 400 1998
Manganese UTNEB-05-1298-01 Background Habitat mg/kg = 386 1998
Manganese UTNEB-06-1298-01 Background Habitat mg/kg = 320 1998
Manganese UTNERB-01-OCT97-01 Background Habitat mg/kg = 361 1997
Manganese UTNERB-02-OCT97-01 Background Habitat mg/kg = 326 1997
Manganese UTNOCB-01-OCT97-01 Background Habitat mg/kg = 246 1997
Manganese UTNOCB-02-OCT97-01 Background Habitat mg/kg = 317 1997
Manganese UTNOCBG-03-1298-01 Background Habitat mg/kg = 418 1998
Manganese UTNOCBG-04-1298-01 Background Habitat mg/kg = 478 1998
Manganese UTNOCBG-05-1298-01 Background Habitat mg/kg = 455 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 25 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Manganese UTNOCBG-06-1298-01 Background Habitat mg/kg = 468 1998
Manganese NR-226 OnSite Habitat mg/Kg = 204 2002
Manganese NR-227 OnSite Habitat mg/Kg = 377 2002
Manganese NR-228 OnSite OB/OD mg/Kg = 376 2002
Manganese NR-229 OnSite Habitat mg/Kg = 481 2002
Manganese NR-230 OnSite Habitat mg/Kg = 519 2002
Manganese NR-231 OnSite OB/OD mg/Kg = 420 2002
Manganese NR-232 OnSite Habitat mg/Kg = 458 2002
Manganese NR-233 OnSite Habitat mg/Kg = 204 2002
Manganese NR-234 OnSite Habitat mg/Kg = 429 2002
Manganese NR-235 OnSite Habitat mg/Kg = 430 2002
Manganese NR-236 OnSite Habitat mg/Kg = 458 2002
Manganese NR-237 OnSite Habitat mg/Kg = 308 2002
Manganese NR-526 OnSite Habitat mg/Kg = 218 2004
Manganese NR-527 OnSite Habitat mg/Kg = 451 2004
Manganese NR-528 OnSite Habitat mg/Kg = 333 2004
Manganese NR-529 OnSite Habitat mg/Kg = 305 2004
Manganese NR-530 OnSite Habitat mg/Kg = 203 2004
Manganese NR-531 OnSite OB/OD mg/Kg = 171 2004
Manganese NR-532 OnSite OB/OD mg/Kg = 125 2004
Manganese NR-533 OnSite OB/OD mg/Kg = 225 2004
Manganese NR-534 OnSite OB/OD mg/Kg J 191 2004
Manganese NR-535 OnSite OB/OD mg/Kg = 190 2004
Manganese SS1 OnSite OB/OD mg/Kg = 270 1991
Manganese SS10 OnSite OB/OD mg/Kg = 290 1991
Manganese SS11 OnSite OB/OD mg/Kg = 480 1991
Manganese SS12 OnSite OB/OD mg/Kg = 440 1991
Manganese SS13 OnSite OB/OD mg/Kg = 350 1991
Manganese SS14 OnSite OB/OD mg/Kg = 360 1991
Manganese SS15 OnSite OB/OD mg/Kg = 410 1991
Manganese SS16 OnSite Habitat mg/Kg = 400 1991
Manganese SS17 OnSite Habitat mg/Kg = 490 1991
Manganese SS18 OnSite Habitat mg/Kg = 430 1991
Manganese SS19 OnSite Habitat mg/Kg = 390 1991
Manganese SS2 OnSite OB/OD mg/Kg = 140 1991
Manganese SS20 OnSite Habitat mg/Kg = 460 1991
Manganese SS3 OnSite OB/OD mg/Kg = 120 1991
Manganese SS4 OnSite OB/OD mg/Kg = 200 1991
Manganese SS5 OnSite OB/OD mg/Kg = 320 1991
Manganese SS6 OnSite OB/OD mg/Kg = 410 1991
Manganese SS7 OnSite OB/OD mg/Kg = 330 1991
Manganese SS8 OnSite OB/OD mg/Kg = 310 1991
Manganese SS9 OnSite OB/OD mg/Kg = 280 1991
Manganese TTU-SS01S OnSite OB/OD mg/Kg = 181 1989
Manganese TTU-SS02S OnSite OB/OD mg/Kg = 219 1989
Manganese TTU-SS03S OnSite OB/OD mg/Kg = 189 1989
Manganese TTU-SS04S(D) OnSite OB/OD mg/Kg = 139 1989
Manganese TTU-SS05S OnSite OB/OD mg/Kg = 219 1989
Manganese TTU-SS06S(BG) OnSite Habitat mg/Kg = 345 1989
Mercury NR-238 Background Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-239 Background Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-536 Background Habitat mg/Kg B 0.0262 2004
Mercury NR-537 Background Habitat mg/Kg B 0.025 2004
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 26 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Mercury NR-226 OnSite Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-227 OnSite Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-228 OnSite OB/OD mg/Kg U 0.01 0.02 2002
Mercury NR-229 OnSite Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-230 OnSite Habitat mg/Kg = 0.03 2002
Mercury NR-231 OnSite OB/OD mg/Kg U 0.01 0.02 2002
Mercury NR-232 OnSite Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-233 OnSite Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-234 OnSite Habitat mg/Kg = 0.03 2002
Mercury NR-235 OnSite Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-236 OnSite Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-237 OnSite Habitat mg/Kg U 0.01 0.02 2002
Mercury NR-526 OnSite Habitat mg/Kg B 0.0087 2004
Mercury NR-527 OnSite Habitat mg/Kg B 0.0206 2004
Mercury NR-528 OnSite Habitat mg/Kg B 0.0152 2004
Mercury NR-529 OnSite Habitat mg/Kg B 0.0085 2004
Mercury NR-530 OnSite Habitat mg/Kg B 0.0064 2004
Mercury NR-531 OnSite OB/OD mg/Kg B 0.0065 2004
Mercury NR-532 OnSite OB/OD mg/Kg B 0.005 2004
Mercury NR-533 OnSite OB/OD mg/Kg B 0.0086 2004
Mercury NR-534 OnSite OB/OD mg/Kg B 0.0073 2004
Mercury NR-535 OnSite OB/OD mg/Kg B 0.0071 2004
Mercury SS1 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS10 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS11 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS12 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS13 OnSite OB/OD mg/Kg = 0.07 1991
Mercury SS14 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS15 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS16 OnSite Habitat mg/Kg U 0.025 0.05 1991
Mercury SS17 OnSite Habitat mg/Kg U 0.025 0.05 1991
Mercury SS18 OnSite Habitat mg/Kg U 0.025 0.05 1991
Mercury SS19 OnSite Habitat mg/Kg U 0.025 0.05 1991
Mercury SS2 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS20 OnSite Habitat mg/Kg U 0.025 0.05 1991
Mercury SS3 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS4 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS5 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS6 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS7 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS8 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury SS9 OnSite OB/OD mg/Kg U 0.025 0.05 1991
Mercury TTU-SS01S OnSite OB/OD mg/Kg U 0.045 0.09 1989
Mercury TTU-SS02S OnSite OB/OD mg/Kg U 0.005 0.01 1989
Mercury TTU-SS03S OnSite OB/OD mg/Kg U 0.055 0.11 1989
Mercury TTU-SS04S(D) OnSite OB/OD mg/Kg U 0.055 0.11 1989
Mercury TTU-SS05S OnSite OB/OD mg/Kg U 0.055 0.11 1989
Mercury TTU-SS06S(BG) OnSite Habitat mg/Kg U 0.055 0.11 1989
Molybdenum AMTOF-01-1298-01 Background Habitat mg/kg = 0.679 1998
Molybdenum AMTOF-02-1298-01 Background Habitat mg/kg = 0.685 1998
Molybdenum AMTOF-03-1298-01 Background Habitat mg/kg = 0.696 1998
Molybdenum AMTOF-04-1298-01 Background Habitat mg/kg = 0.612 1998
Molybdenum AMTOF-05-1298-01 Background Habitat mg/kg = 0.658 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 27 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Molybdenum AMTOF-06-1298-01 Background Habitat mg/kg = 0.494 1998
Molybdenum NR-238 Background Habitat mg/Kg = 1.1 2002
Molybdenum NR-239 Background Habitat mg/Kg = 0.85 2002
Molybdenum NR-500-0800-01 Background Habitat mg/kg J 0.748 2000
Molybdenum NR-501-0800-01 Background Habitat mg/kg J 0.242 2000
Molybdenum NR-502-0800-01 Background Habitat mg/kg J 0.523 2000
Molybdenum NR-503-0800-01 Background Habitat mg/kg J 0.517 2000
Molybdenum NR-504-0800-01 Background Habitat mg/kg J 0.509 2000
Molybdenum NR-505-0800-01 Background Habitat mg/kg J 0.921 2000
Molybdenum NR-506-0800-01 Background Habitat mg/kg = 1.2 2000
Molybdenum NR-507-0800-01 Background Habitat mg/kg J 0.381 2000
Molybdenum NR-508-0800-01 Background Habitat mg/kg J 0.692 2000
Molybdenum NR-509-0800-01 Background Habitat mg/kg = 3.34 2000
Molybdenum NR-510-0800-01 Background Habitat mg/kg J 0.623 2000
Molybdenum NR-511-0800-01 Background Habitat mg/kg J 0.465 2000
Molybdenum NR-512-0800-01 Background Habitat mg/kg J 0.373 2000
Molybdenum NR-513-0800-01 Background Habitat mg/kg = 0.895 2000
Molybdenum NR-514-0800-01 Background Habitat mg/kg J 0.575 2000
Molybdenum NR-515-0800-01 Background Habitat mg/kg J 0.247 2000
Molybdenum NR-516-0800-01 Background Habitat mg/kg = 4.91 2000
Molybdenum NR-517-0800-01 Background Habitat mg/kg J 0.5 2000
Molybdenum NR-518-0800-01 Background Habitat mg/kg J 0.13 2000
Molybdenum NR-519-0800-01 Background Habitat mg/kg U 0.073 0.146 2000
Molybdenum NR-520-0800-01 Background Habitat mg/kg J 0.23 2000
Molybdenum NR-521-0800-01 Background Habitat mg/kg J 0.422 2000
Molybdenum NR-522-0800-01 Background Habitat mg/kg J 0.662 2000
Molybdenum NR-523-0800-01 Background Habitat mg/kg J 0.719 2000
Molybdenum NR-524-0800-01 Background Habitat mg/kg J 0.577 2000
Molybdenum NR-525-0800-01 Background Habitat mg/kg J 0.589 2000
Molybdenum NR-536 Background Habitat mg/Kg J 0.98 2004
Molybdenum NR-537 Background Habitat mg/Kg J 0.8 2004
Molybdenum UTNCBU-01-OCT97-01 Background Habitat mg/kg = 0.587 1997
Molybdenum UTNCBU-02-OCT97-01 Background Habitat mg/kg B 0.352 1997
Molybdenum UTNCBU-03-1298-01 Background Habitat mg/kg B 0.527 1998
Molybdenum UTNCBU-04-1298-01 Background Habitat mg/kg B 0.399 1998
Molybdenum UTNCBU-05-1298-01 Background Habitat mg/kg B 0.409 1998
Molybdenum UTNCBU-06-1298-01 Background Habitat mg/kg B 0.513 1998
Molybdenum UTNEB-03-1298-01 Background Habitat mg/kg B 0.598 1998
Molybdenum UTNEB-04-1298-01 Background Habitat mg/kg B 0.616 1998
Molybdenum UTNEB-05-1298-01 Background Habitat mg/kg B 0.501 1998
Molybdenum UTNEB-06-1298-01 Background Habitat mg/kg B 0.538 1998
Molybdenum UTNERB-01-OCT97-01 Background Habitat mg/kg = 1.04 1997
Molybdenum UTNERB-02-OCT97-01 Background Habitat mg/kg = 0.701 1997
Molybdenum UTNOCB-01-OCT97-01 Background Habitat mg/kg = 1.37 1997
Molybdenum UTNOCB-02-OCT97-01 Background Habitat mg/kg = 1.62 1997
Molybdenum UTNOCBG-03-1298-01 Background Habitat mg/kg = 0.966 1998
Molybdenum UTNOCBG-04-1298-01 Background Habitat mg/kg = 1.88 1998
Molybdenum UTNOCBG-05-1298-01 Background Habitat mg/kg = 1.81 1998
Molybdenum UTNOCBG-06-1298-01 Background Habitat mg/kg = 1.45 1998
Molybdenum NR-226 OnSite Habitat mg/Kg U 0.15 0.3 2002
Molybdenum NR-227 OnSite Habitat mg/Kg U 0.15 0.3 2002
Molybdenum NR-228 OnSite OB/OD mg/Kg = 0.75 2002
Molybdenum NR-229 OnSite Habitat mg/Kg = 0.92 2002
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 28 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Molybdenum NR-230 OnSite Habitat mg/Kg = 1 2002
Molybdenum NR-231 OnSite OB/OD mg/Kg = 1.3 2002
Molybdenum NR-232 OnSite Habitat mg/Kg = 0.86 2002
Molybdenum NR-233 OnSite Habitat mg/Kg = 1.3 2002
Molybdenum NR-234 OnSite Habitat mg/Kg = 0.9 2002
Molybdenum NR-235 OnSite Habitat mg/Kg = 1 2002
Molybdenum NR-236 OnSite Habitat mg/Kg = 1.3 2002
Molybdenum NR-237 OnSite Habitat mg/Kg = 1.2 2002
Molybdenum NR-526 OnSite Habitat mg/Kg J 0.77 2004
Molybdenum NR-527 OnSite Habitat mg/Kg J 0.8 2004
Molybdenum NR-528 OnSite Habitat mg/Kg J 0.6 2004
Molybdenum NR-529 OnSite Habitat mg/Kg J 1 2004
Molybdenum NR-530 OnSite Habitat mg/Kg J 0.75 2004
Molybdenum NR-531 OnSite OB/OD mg/Kg B 17 2004
Molybdenum NR-532 OnSite OB/OD mg/Kg J 2.8 2004
Molybdenum NR-533 OnSite OB/OD mg/Kg J 1.1 2004
Molybdenum NR-534 OnSite OB/OD mg/Kg J 1.3 2004
Molybdenum NR-535 OnSite OB/OD mg/Kg J 1.1 2004
Nickel AMTOF-01-1298-01 Background Habitat mg/kg = 11.9 1998
Nickel AMTOF-02-1298-01 Background Habitat mg/kg = 16.3 1998
Nickel AMTOF-03-1298-01 Background Habitat mg/kg = 11.7 1998
Nickel AMTOF-04-1298-01 Background Habitat mg/kg = 11.8 1998
Nickel AMTOF-05-1298-01 Background Habitat mg/kg = 12 1998
Nickel AMTOF-06-1298-01 Background Habitat mg/kg = 10.8 1998
Nickel NR-238 Background Habitat mg/Kg = 11.9 2002
Nickel NR-239 Background Habitat mg/Kg = 10.7 2002
Nickel NR-500-0800-01 Background Habitat mg/kg = 10.5 2000
Nickel NR-501-0800-01 Background Habitat mg/kg = 7.29 2000
Nickel NR-502-0800-01 Background Habitat mg/kg = 11.5 2000
Nickel NR-503-0800-01 Background Habitat mg/kg = 10.5 2000
Nickel NR-504-0800-01 Background Habitat mg/kg = 9.01 2000
Nickel NR-505-0800-01 Background Habitat mg/kg = 10.6 2000
Nickel NR-506-0800-01 Background Habitat mg/kg = 10.8 2000
Nickel NR-507-0800-01 Background Habitat mg/kg = 9.28 2000
Nickel NR-508-0800-01 Background Habitat mg/kg = 10.2 2000
Nickel NR-509-0800-01 Background Habitat mg/kg = 13.3 2000
Nickel NR-510-0800-01 Background Habitat mg/kg = 8.8 2000
Nickel NR-511-0800-01 Background Habitat mg/kg = 11.3 2000
Nickel NR-512-0800-01 Background Habitat mg/kg = 12.4 2000
Nickel NR-513-0800-01 Background Habitat mg/kg = 11.5 2000
Nickel NR-514-0800-01 Background Habitat mg/kg = 10.1 2000
Nickel NR-515-0800-01 Background Habitat mg/kg = 3.14 2000
Nickel NR-516-0800-01 Background Habitat mg/kg = 20.2 2000
Nickel NR-517-0800-01 Background Habitat mg/kg = 6.08 2000
Nickel NR-518-0800-01 Background Habitat mg/kg = 3 2000
Nickel NR-519-0800-01 Background Habitat mg/kg = 6.12 2000
Nickel NR-520-0800-01 Background Habitat mg/kg = 6.76 2000
Nickel NR-521-0800-01 Background Habitat mg/kg = 5.42 2000
Nickel NR-522-0800-01 Background Habitat mg/kg = 10.7 2000
Nickel NR-523-0800-01 Background Habitat mg/kg = 9.27 2000
Nickel NR-524-0800-01 Background Habitat mg/kg = 7.5 2000
Nickel NR-525-0800-01 Background Habitat mg/kg = 5.56 2000
Nickel NR-536 Background Habitat mg/Kg = 13.3 2004
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 29 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Nickel NR-537 Background Habitat mg/Kg = 15.7 2004
Nickel UTNCBU-01-OCT97-01 Background Habitat mg/kg = 9.16 1997
Nickel UTNCBU-02-OCT97-01 Background Habitat mg/kg = 8.13 1997
Nickel UTNCBU-03-1298-01 Background Habitat mg/kg = 11.4 1998
Nickel UTNCBU-04-1298-01 Background Habitat mg/kg = 10.9 1998
Nickel UTNCBU-05-1298-01 Background Habitat mg/kg = 8.31 1998
Nickel UTNCBU-06-1298-01 Background Habitat mg/kg = 8.21 1998
Nickel UTNEB-03-1298-01 Background Habitat mg/kg = 8.93 1998
Nickel UTNEB-04-1298-01 Background Habitat mg/kg = 13.2 1998
Nickel UTNEB-05-1298-01 Background Habitat mg/kg = 9.45 1998
Nickel UTNEB-06-1298-01 Background Habitat mg/kg = 8.48 1998
Nickel UTNERB-01-OCT97-01 Background Habitat mg/kg = 15.8 1997
Nickel UTNERB-02-OCT97-01 Background Habitat mg/kg = 12.3 1997
Nickel UTNOCB-01-OCT97-01 Background Habitat mg/kg = 12.2 1997
Nickel UTNOCB-02-OCT97-01 Background Habitat mg/kg = 11.3 1997
Nickel UTNOCBG-03-1298-01 Background Habitat mg/kg = 9.49 1998
Nickel UTNOCBG-04-1298-01 Background Habitat mg/kg = 9.42 1998
Nickel UTNOCBG-05-1298-01 Background Habitat mg/kg = 9.2 1998
Nickel UTNOCBG-06-1298-01 Background Habitat mg/kg = 12.3 1998
Nickel NR-226 OnSite Habitat mg/Kg = 6.8 2002
Nickel NR-227 OnSite Habitat mg/Kg = 9.3 2002
Nickel NR-228 OnSite OB/OD mg/Kg = 11.4 2002
Nickel NR-229 OnSite Habitat mg/Kg = 12.8 2002
Nickel NR-230 OnSite Habitat mg/Kg = 9.7 2002
Nickel NR-231 OnSite OB/OD mg/Kg = 11.4 2002
Nickel NR-232 OnSite Habitat mg/Kg = 13 2002
Nickel NR-233 OnSite Habitat mg/Kg = 9.6 2002
Nickel NR-234 OnSite Habitat mg/Kg = 13 2002
Nickel NR-235 OnSite Habitat mg/Kg = 11 2002
Nickel NR-236 OnSite Habitat mg/Kg = 10.5 2002
Nickel NR-237 OnSite Habitat mg/Kg = 10.4 2002
Nickel NR-526 OnSite Habitat mg/Kg = 8.6 2004
Nickel NR-527 OnSite Habitat mg/Kg = 12.2 2004
Nickel NR-528 OnSite Habitat mg/Kg = 8.5 2004
Nickel NR-529 OnSite Habitat mg/Kg = 9.6 2004
Nickel NR-530 OnSite Habitat mg/Kg = 8.9 2004
Nickel NR-531 OnSite OB/OD mg/Kg = 41.3 2004
Nickel NR-532 OnSite OB/OD mg/Kg = 10 2004
Nickel NR-533 OnSite OB/OD mg/Kg = 9.2 2004
Nickel NR-534 OnSite OB/OD mg/Kg = 9.1 2004
Nickel NR-535 OnSite OB/OD mg/Kg = 10 2004
Nickel SS1 OnSite OB/OD mg/Kg = 8 1991
Nickel SS10 OnSite OB/OD mg/Kg = 8 1991
Nickel SS11 OnSite OB/OD mg/Kg = 12 1991
Nickel SS12 OnSite OB/OD mg/Kg = 11 1991
Nickel SS13 OnSite OB/OD mg/Kg = 9 1991
Nickel SS14 OnSite OB/OD mg/Kg = 10 1991
Nickel SS15 OnSite OB/OD mg/Kg = 11 1991
Nickel SS16 OnSite Habitat mg/Kg = 9 1991
Nickel SS17 OnSite Habitat mg/Kg = 9 1991
Nickel SS18 OnSite Habitat mg/Kg = 11 1991
Nickel SS19 OnSite Habitat mg/Kg = 7 1991
Nickel SS2 OnSite OB/OD mg/Kg = 9 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 30 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Nickel SS20 OnSite Habitat mg/Kg = 10 1991
Nickel SS3 OnSite OB/OD mg/Kg = 19 1991
Nickel SS4 OnSite OB/OD mg/Kg = 8 1991
Nickel SS5 OnSite OB/OD mg/Kg = 31 1991
Nickel SS6 OnSite OB/OD mg/Kg = 11 1991
Nickel SS7 OnSite OB/OD mg/Kg = 17 1991
Nickel SS8 OnSite OB/OD mg/Kg = 8 1991
Nickel SS9 OnSite OB/OD mg/Kg = 9 1991
Nickel TTU-SS01S OnSite OB/OD mg/Kg = 9 1989
Nickel TTU-SS02S OnSite OB/OD mg/Kg = 10.2 1989
Nickel TTU-SS03S OnSite OB/OD mg/Kg = 7.5 1989
Nickel TTU-SS04S(D) OnSite OB/OD mg/Kg = 6.7 1989
Nickel TTU-SS05S OnSite OB/OD mg/Kg = 10.4 1989
Nickel TTU-SS06S(BG) OnSite Habitat mg/Kg = 13.9 1989
Nitrate NR-238 Background Habitat mg/Kg = 16 2002
Nitrate NR-239 Background Habitat mg/Kg = 5.1 2002
Nitrate NR-226 OnSite Habitat mg/Kg = 3.8 2002
Nitrate NR-227 OnSite Habitat mg/Kg = 3.45 2002
Nitrate NR-228 OnSite OB/OD mg/Kg = 7.7 2002
Nitrate NR-229 OnSite Habitat mg/Kg = 1.1 2002
Nitrate NR-230 OnSite Habitat mg/Kg = 12.2 2002
Nitrate NR-231 OnSite OB/OD mg/Kg = 10.5 2002
Nitrate NR-232 OnSite Habitat mg/Kg = 12.2 2002
Nitrate NR-233 OnSite Habitat mg/Kg = 3.2 2002
Nitrate NR-234 OnSite Habitat mg/Kg = 15.5 2002
Nitrate NR-235 OnSite Habitat mg/Kg = 7.7 2002
Nitrate NR-236 OnSite Habitat mg/Kg = 15.9 2002
Nitrate NR-237 OnSite Habitat mg/Kg = 10.8 2002
Nitrate NR-526 OnSite Habitat mg/Kg J 22.8 2004
Nitrate NR-527 OnSite Habitat mg/Kg B 9 2004
Nitrate NR-528 OnSite Habitat mg/Kg B 9.1 2004
Nitrate NR-529 OnSite Habitat mg/Kg B 19.2 2004
Nitrate NR-530 OnSite Habitat mg/Kg UB 1.25 2.5 2004
Nitrate NR-531 OnSite OB/OD mg/Kg UB 0.85 1.7 2004
Nitrate NR-532 OnSite OB/OD mg/Kg UB 1.2 2.4 2004
Nitrate NR-533 OnSite OB/OD mg/Kg B 2.9 2004
Nitrate NR-534 OnSite OB/OD mg/Kg J 13.1 2004
Nitrate NR-535 OnSite OB/OD mg/Kg UB 1.05 2.1 2004
Nitrate SS1 OnSite OB/OD mg/Kg = 0.007 1991
Nitrate SS10 OnSite OB/OD mg/Kg = 0.009 1991
Nitrate SS11 OnSite OB/OD mg/Kg = 0.015 1991
Nitrate SS12 OnSite OB/OD mg/Kg = 0.043 1991
Nitrate SS13 OnSite OB/OD mg/Kg = 0.11 1991
Nitrate SS14 OnSite OB/OD mg/Kg = 0.007 1991
Nitrate SS15 OnSite OB/OD mg/Kg = 0.006 1991
Nitrate SS16 OnSite Habitat mg/Kg = 0.004 1991
Nitrate SS17 OnSite Habitat mg/Kg = 0.011 1991
Nitrate SS18 OnSite Habitat mg/Kg = 0.01 1991
Nitrate SS19 OnSite Habitat mg/Kg = 0.008 1991
Nitrate SS2 OnSite OB/OD mg/Kg = 0.009 1991
Nitrate SS20 OnSite Habitat mg/Kg = 0.008 1991
Nitrate SS3 OnSite OB/OD mg/Kg = 0.009 1991
Nitrate SS4 OnSite OB/OD mg/Kg = 0.045 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 31 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Nitrate SS5 OnSite OB/OD mg/Kg = 0.013 1991
Nitrate SS6 OnSite OB/OD mg/Kg = 0.009 1991
Nitrate SS7 OnSite OB/OD mg/Kg = 0.026 1991
Nitrate SS8 OnSite OB/OD mg/Kg = 0.015 1991
Nitrate SS9 OnSite OB/OD mg/Kg = 0.007 1991
Nitrate TTU-SS01S OnSite OB/OD mg/Kg = 1.5 1989
Nitrate TTU-SS02S OnSite OB/OD mg/Kg = 1.6 1989
Nitrate TTU-SS03S OnSite OB/OD mg/Kg = 1.8 1989
Nitrate TTU-SS04S(D) OnSite OB/OD mg/Kg = 1.6 1989
Nitrate TTU-SS05S OnSite OB/OD mg/Kg = 8.5 1989
Nitrate TTU-SS06S(BG) OnSite Habitat mg/Kg = 5.4 1989
Phosphorus AMTOF-01-1298-01 Background Habitat mg/kg = 1130 1998
Phosphorus AMTOF-02-1298-01 Background Habitat mg/kg = 1470 1998
Phosphorus AMTOF-03-1298-01 Background Habitat mg/kg = 1040 1998
Phosphorus AMTOF-04-1298-01 Background Habitat mg/kg = 988 1998
Phosphorus AMTOF-05-1298-01 Background Habitat mg/kg = 868 1998
Phosphorus AMTOF-06-1298-01 Background Habitat mg/kg = 1030 1998
Phosphorus NR-500-0800-01 Background Habitat mg/kg B 728 2000
Phosphorus NR-501-0800-01 Background Habitat mg/kg B 575 2000
Phosphorus NR-502-0800-01 Background Habitat mg/kg B 825 2000
Phosphorus NR-503-0800-01 Background Habitat mg/kg B 794 2000
Phosphorus NR-504-0800-01 Background Habitat mg/kg B 754 2000
Phosphorus NR-505-0800-01 Background Habitat mg/kg B 772 2000
Phosphorus NR-506-0800-01 Background Habitat mg/kg B 668 2000
Phosphorus NR-507-0800-01 Background Habitat mg/kg B 682 2000
Phosphorus NR-508-0800-01 Background Habitat mg/kg B 719 2000
Phosphorus NR-509-0800-01 Background Habitat mg/kg B 713 2000
Phosphorus NR-510-0800-01 Background Habitat mg/kg B 612 2000
Phosphorus NR-511-0800-01 Background Habitat mg/kg B 767 2000
Phosphorus NR-512-0800-01 Background Habitat mg/kg B 719 2000
Phosphorus NR-513-0800-01 Background Habitat mg/kg B 762 2000
Phosphorus NR-514-0800-01 Background Habitat mg/kg B 774 2000
Phosphorus NR-515-0800-01 Background Habitat mg/kg B 230 2000
Phosphorus NR-516-0800-01 Background Habitat mg/kg B 669 2000
Phosphorus NR-517-0800-01 Background Habitat mg/kg B 519 2000
Phosphorus NR-518-0800-01 Background Habitat mg/kg B 198 2000
Phosphorus NR-519-0800-01 Background Habitat mg/kg B 356 2000
Phosphorus NR-520-0800-01 Background Habitat mg/kg B 575 2000
Phosphorus NR-521-0800-01 Background Habitat mg/kg B 328 2000
Phosphorus NR-522-0800-01 Background Habitat mg/kg B 575 2000
Phosphorus NR-523-0800-01 Background Habitat mg/kg B 697 2000
Phosphorus NR-524-0800-01 Background Habitat mg/kg B 492 2000
Phosphorus NR-525-0800-01 Background Habitat mg/kg B 431 2000
Phosphorus UTNCBU-01-OCT97-01 Background Habitat mg/kg = 639 1997
Phosphorus UTNCBU-02-OCT97-01 Background Habitat mg/kg = 658 1997
Phosphorus UTNCBU-03-1298-01 Background Habitat mg/kg = 820 1998
Phosphorus UTNCBU-04-1298-01 Background Habitat mg/kg = 862 1998
Phosphorus UTNCBU-05-1298-01 Background Habitat mg/kg = 722 1998
Phosphorus UTNCBU-06-1298-01 Background Habitat mg/kg = 621 1998
Phosphorus UTNEB-03-1298-01 Background Habitat mg/kg = 821 1998
Phosphorus UTNEB-04-1298-01 Background Habitat mg/kg = 885 1998
Phosphorus UTNEB-05-1298-01 Background Habitat mg/kg = 790 1998
Phosphorus UTNEB-06-1298-01 Background Habitat mg/kg = 726 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 32 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Phosphorus UTNERB-01-OCT97-01 Background Habitat mg/kg = 738 1997
Phosphorus UTNERB-02-OCT97-01 Background Habitat mg/kg = 719 1997
Phosphorus UTNOCB-01-OCT97-01 Background Habitat mg/kg = 659 1997
Phosphorus UTNOCB-02-OCT97-01 Background Habitat mg/kg = 835 1997
Phosphorus UTNOCBG-03-1298-01 Background Habitat mg/kg = 820 1998
Phosphorus UTNOCBG-04-1298-01 Background Habitat mg/kg = 764 1998
Phosphorus UTNOCBG-05-1298-01 Background Habitat mg/kg = 753 1998
Phosphorus UTNOCBG-06-1298-01 Background Habitat mg/kg = 799 1998
Phosphorus SS1 OnSite OB/OD mg/Kg = 460 1991
Phosphorus SS10 OnSite OB/OD mg/Kg = 460 1991
Phosphorus SS11 OnSite OB/OD mg/Kg = 730 1991
Phosphorus SS12 OnSite OB/OD mg/Kg = 590 1991
Phosphorus SS13 OnSite OB/OD mg/Kg = 500 1991
Phosphorus SS14 OnSite OB/OD mg/Kg = 660 1991
Phosphorus SS15 OnSite OB/OD mg/Kg = 750 1991
Phosphorus SS16 OnSite Habitat mg/Kg = 860 1991
Phosphorus SS17 OnSite Habitat mg/Kg = 820 1991
Phosphorus SS18 OnSite Habitat mg/Kg = 830 1991
Phosphorus SS19 OnSite Habitat mg/Kg = 820 1991
Phosphorus SS2 OnSite OB/OD mg/Kg = 450 1991
Phosphorus SS20 OnSite Habitat mg/Kg = 890 1991
Phosphorus SS3 OnSite OB/OD mg/Kg = 990 1991
Phosphorus SS4 OnSite OB/OD mg/Kg = 470 1991
Phosphorus SS5 OnSite OB/OD mg/Kg = 500 1991
Phosphorus SS6 OnSite OB/OD mg/Kg = 700 1991
Phosphorus SS7 OnSite OB/OD mg/Kg = 570 1991
Phosphorus SS8 OnSite OB/OD mg/Kg = 570 1991
Phosphorus SS9 OnSite OB/OD mg/Kg = 500 1991
Selenium AMTOF-01-1298-01 Background Habitat mg/kg = 0.585 1998
Selenium AMTOF-02-1298-01 Background Habitat mg/kg = 1.07 1998
Selenium AMTOF-03-1298-01 Background Habitat mg/kg = 0.546 1998
Selenium AMTOF-04-1298-01 Background Habitat mg/kg = 0.335 1998
Selenium AMTOF-05-1298-01 Background Habitat mg/kg = 0.379 1998
Selenium AMTOF-06-1298-01 Background Habitat mg/kg = 0.449 1998
Selenium NR-238 Background Habitat mg/Kg U 1.15 2.3 2002
Selenium NR-239 Background Habitat mg/Kg U 1.05 2.1 2002
Selenium NR-500-0800-01 Background Habitat mg/kg J 0.355 2000
Selenium NR-501-0800-01 Background Habitat mg/kg J 0.696 2000
Selenium NR-502-0800-01 Background Habitat mg/kg J 0.498 2000
Selenium NR-503-0800-01 Background Habitat mg/kg J 0.511 2000
Selenium NR-504-0800-01 Background Habitat mg/kg J 0.44 2000
Selenium NR-505-0800-01 Background Habitat mg/kg J 0.493 2000
Selenium NR-506-0800-01 Background Habitat mg/kg J 0.617 2000
Selenium NR-507-0800-01 Background Habitat mg/kg J 0.645 2000
Selenium NR-508-0800-01 Background Habitat mg/kg J 0.388 2000
Selenium NR-509-0800-01 Background Habitat mg/kg J 0.778 2000
Selenium NR-510-0800-01 Background Habitat mg/kg J 0.64 2000
Selenium NR-511-0800-01 Background Habitat mg/kg J 0.54 2000
Selenium NR-512-0800-01 Background Habitat mg/kg J 0.476 2000
Selenium NR-513-0800-01 Background Habitat mg/kg J 0.451 2000
Selenium NR-514-0800-01 Background Habitat mg/kg J 0.768 2000
Selenium NR-515-0800-01 Background Habitat mg/kg J 0.702 2000
Selenium NR-516-0800-01 Background Habitat mg/kg J 0.699 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 33 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Selenium NR-517-0800-01 Background Habitat mg/kg U 0.2205 0.441 2000
Selenium NR-518-0800-01 Background Habitat mg/kg J 0.806 2000
Selenium NR-519-0800-01 Background Habitat mg/kg J 1.05 2000
Selenium NR-520-0800-01 Background Habitat mg/kg U 0.297 0.594 2000
Selenium NR-521-0800-01 Background Habitat mg/kg J 0.872 2000
Selenium NR-522-0800-01 Background Habitat mg/kg J 0.934 2000
Selenium NR-523-0800-01 Background Habitat mg/kg J 0.755 2000
Selenium NR-524-0800-01 Background Habitat mg/kg J 1.5 2000
Selenium NR-525-0800-01 Background Habitat mg/kg J 1.32 2000
Selenium NR-536 Background Habitat mg/Kg U 0.345 0.69 2004
Selenium NR-537 Background Habitat mg/Kg U 0.35 0.7 2004
Selenium UTNCBU-01-OCT97-01 Background Habitat mg/kg BJ 0.162 1997
Selenium UTNCBU-02-OCT97-01 Background Habitat mg/kg U 0.1325 0.265 1997
Selenium UTNCBU-03-1298-01 Background Habitat mg/kg U 0.0865 0.173 1998
Selenium UTNCBU-04-1298-01 Background Habitat mg/kg J 0.00815 1998
Selenium UTNCBU-05-1298-01 Background Habitat mg/kg U 0.0745 0.149 1998
Selenium UTNCBU-06-1298-01 Background Habitat mg/kg U 0.097 0.194 1998
Selenium UTNEB-03-1298-01 Background Habitat mg/kg U 0.072 0.144 1998
Selenium UTNEB-04-1298-01 Background Habitat mg/kg U 0.083 0.166 1998
Selenium UTNEB-05-1298-01 Background Habitat mg/kg U 0.069 0.138 1998
Selenium UTNEB-06-1298-01 Background Habitat mg/kg U 0.0945 0.189 1998
Selenium UTNERB-01-OCT97-01 Background Habitat mg/kg U 0.1595 0.319 1997
Selenium UTNERB-02-OCT97-01 Background Habitat mg/kg U 0.13 0.26 1997
Selenium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 0.52 1997
Selenium UTNOCB-02-OCT97-01 Background Habitat mg/kg B 0.56 1997
Selenium UTNOCBG-03-1298-01 Background Habitat mg/kg = 0.405 1998
Selenium UTNOCBG-04-1298-01 Background Habitat mg/kg = 0.537 1998
Selenium UTNOCBG-05-1298-01 Background Habitat mg/kg = 0.381 1998
Selenium UTNOCBG-06-1298-01 Background Habitat mg/kg = 0.413 1998
Selenium NR-226 OnSite Habitat mg/Kg U 1.05 2.1 2002
Selenium NR-227 OnSite Habitat mg/Kg U 0.105 0.21 2002
Selenium NR-228 OnSite OB/OD mg/Kg U 1 2 2002
Selenium NR-229 OnSite Habitat mg/Kg U 1.05 2.1 2002
Selenium NR-230 OnSite Habitat mg/Kg U 1.05 2.1 2002
Selenium NR-231 OnSite OB/OD mg/Kg U 1 2 2002
Selenium NR-232 OnSite Habitat mg/Kg U 1 2 2002
Selenium NR-233 OnSite Habitat mg/Kg U 1 2 2002
Selenium NR-234 OnSite Habitat mg/Kg U 1.1 2.2 2002
Selenium NR-235 OnSite Habitat mg/Kg U 1.05 2.1 2002
Selenium NR-236 OnSite Habitat mg/Kg U 1.05 2.1 2002
Selenium NR-237 OnSite Habitat mg/Kg U 1.05 2.1 2002
Selenium NR-526 OnSite Habitat mg/Kg U 0.315 0.63 2004
Selenium NR-527 OnSite Habitat mg/Kg U 0.345 0.69 2004
Selenium NR-528 OnSite Habitat mg/Kg U 0.335 0.67 2004
Selenium NR-529 OnSite Habitat mg/Kg U 0.36 0.72 2004
Selenium NR-530 OnSite Habitat mg/Kg U 0.38 0.76 2004
Selenium NR-531 OnSite OB/OD mg/Kg U 0.3 0.6 2004
Selenium NR-532 OnSite OB/OD mg/Kg U 0.29 0.58 2004
Selenium NR-533 OnSite OB/OD mg/Kg U 0.325 0.65 2004
Selenium NR-534 OnSite OB/OD mg/Kg U 0.315 0.63 2004
Selenium NR-535 OnSite OB/OD mg/Kg U 0.325 0.65 2004
Selenium SS1 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS10 OnSite OB/OD mg/Kg U 5 10 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 34 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Selenium SS11 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS12 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS13 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS14 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS15 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS16 OnSite Habitat mg/Kg U 5 10 1991
Selenium SS17 OnSite Habitat mg/Kg U 5 10 1991
Selenium SS18 OnSite Habitat mg/Kg U 5 10 1991
Selenium SS19 OnSite Habitat mg/Kg U 5 10 1991
Selenium SS2 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS20 OnSite Habitat mg/Kg U 5 10 1991
Selenium SS3 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS4 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS5 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS6 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS7 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS8 OnSite OB/OD mg/Kg U 5 10 1991
Selenium SS9 OnSite OB/OD mg/Kg U 5 10 1991
Selenium TTU-SS01S OnSite OB/OD mg/Kg U 0.8 1.6 1989
Selenium TTU-SS02S OnSite OB/OD mg/Kg U 0.75 1.5 1989
Selenium TTU-SS03S OnSite OB/OD mg/Kg U 0.85 1.7 1989
Selenium TTU-SS04S(D) OnSite OB/OD mg/Kg U 0.85 1.7 1989
Selenium TTU-SS05S OnSite OB/OD mg/Kg U 0.09 0.18 1989
Selenium TTU-SS06S(BG) OnSite Habitat mg/Kg U 0.85 1.7 1989
Silicon AMTOF-01-1298-01 Background Habitat mg/kg = 310 1998
Silicon AMTOF-02-1298-01 Background Habitat mg/kg = 196 1998
Silicon AMTOF-03-1298-01 Background Habitat mg/kg = 252 1998
Silicon AMTOF-04-1298-01 Background Habitat mg/kg = 354 1998
Silicon AMTOF-05-1298-01 Background Habitat mg/kg = 370 1998
Silicon AMTOF-06-1298-01 Background Habitat mg/kg = 307 1998
Silicon NR-500-0800-01 Background Habitat mg/kg = 269 2000
Silicon NR-501-0800-01 Background Habitat mg/kg = 228 2000
Silicon NR-502-0800-01 Background Habitat mg/kg = 412 2000
Silicon NR-503-0800-01 Background Habitat mg/kg = 354 2000
Silicon NR-504-0800-01 Background Habitat mg/kg = 229 2000
Silicon NR-505-0800-01 Background Habitat mg/kg = 327 2000
Silicon NR-506-0800-01 Background Habitat mg/kg = 277 2000
Silicon NR-507-0800-01 Background Habitat mg/kg = 356 2000
Silicon NR-508-0800-01 Background Habitat mg/kg = 129 2000
Silicon NR-509-0800-01 Background Habitat mg/kg = 274 2000
Silicon NR-510-0800-01 Background Habitat mg/kg = 252 2000
Silicon NR-511-0800-01 Background Habitat mg/kg = 282 2000
Silicon NR-512-0800-01 Background Habitat mg/kg = 381 2000
Silicon NR-513-0800-01 Background Habitat mg/kg = 291 2000
Silicon NR-514-0800-01 Background Habitat mg/kg = 200 2000
Silicon NR-515-0800-01 Background Habitat mg/kg = 871 2000
Silicon NR-516-0800-01 Background Habitat mg/kg = 325 2000
Silicon NR-517-0800-01 Background Habitat mg/kg = 238 2000
Silicon NR-518-0800-01 Background Habitat mg/kg = 369 2000
Silicon NR-519-0800-01 Background Habitat mg/kg = 394 2000
Silicon NR-520-0800-01 Background Habitat mg/kg = 296 2000
Silicon NR-521-0800-01 Background Habitat mg/kg = 325 2000
Silicon NR-522-0800-01 Background Habitat mg/kg = 330 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 35 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Silicon NR-523-0800-01 Background Habitat mg/kg = 329 2000
Silicon NR-524-0800-01 Background Habitat mg/kg = 427 2000
Silicon NR-525-0800-01 Background Habitat mg/kg = 291 2000
Silicon UTNCBU-01-OCT97-01 Background Habitat mg/kg = 310 1997
Silicon UTNCBU-02-OCT97-01 Background Habitat mg/kg = 204 1997
Silicon UTNCBU-03-1298-01 Background Habitat mg/kg = 281 1998
Silicon UTNCBU-04-1298-01 Background Habitat mg/kg = 271 1998
Silicon UTNCBU-05-1298-01 Background Habitat mg/kg = 297 1998
Silicon UTNCBU-06-1298-01 Background Habitat mg/kg = 163 1998
Silicon UTNEB-03-1298-01 Background Habitat mg/kg = 233 1998
Silicon UTNEB-04-1298-01 Background Habitat mg/kg = 281 1998
Silicon UTNEB-05-1298-01 Background Habitat mg/kg = 256 1998
Silicon UTNEB-06-1298-01 Background Habitat mg/kg = 297 1998
Silicon UTNERB-01-OCT97-01 Background Habitat mg/kg = 315 1997
Silicon UTNERB-02-OCT97-01 Background Habitat mg/kg = 266 1997
Silicon UTNOCB-01-OCT97-01 Background Habitat mg/kg = 342 1997
Silicon UTNOCB-02-OCT97-01 Background Habitat mg/kg = 279 1997
Silicon UTNOCBG-03-1298-01 Background Habitat mg/kg = 294 1998
Silicon UTNOCBG-04-1298-01 Background Habitat mg/kg = 202 1998
Silicon UTNOCBG-05-1298-01 Background Habitat mg/kg = 265 1998
Silicon UTNOCBG-06-1298-01 Background Habitat mg/kg = 215 1998
Silver AMTOF-01-1298-01 Background Habitat mg/kg J 0.109 1998
Silver AMTOF-02-1298-01 Background Habitat mg/kg = 0.102 1998
Silver AMTOF-03-1298-01 Background Habitat mg/kg J 0.105 1998
Silver AMTOF-04-1298-01 Background Habitat mg/kg J 0.0302 1998
Silver AMTOF-05-1298-01 Background Habitat mg/kg J 0.0158 1998
Silver AMTOF-06-1298-01 Background Habitat mg/kg J 0.0755 1998
Silver NR-238 Background Habitat mg/Kg U 0.21 0.42 2002
Silver NR-239 Background Habitat mg/Kg U 0.19 0.38 2002
Silver NR-500-0800-01 Background Habitat mg/kg U 0.03495 0.0699 2000
Silver NR-501-0800-01 Background Habitat mg/kg U 0.0385 0.077 2000
Silver NR-502-0800-01 Background Habitat mg/kg U 0.0456 0.0912 2000
Silver NR-503-0800-01 Background Habitat mg/kg U 0.03715 0.0743 2000
Silver NR-504-0800-01 Background Habitat mg/kg U 0.03955 0.0791 2000
Silver NR-505-0800-01 Background Habitat mg/kg U 0.0441 0.0882 2000
Silver NR-506-0800-01 Background Habitat mg/kg U 0.0351 0.0702 2000
Silver NR-507-0800-01 Background Habitat mg/kg U 0.0447 0.0894 2000
Silver NR-508-0800-01 Background Habitat mg/kg U 0.0371 0.0742 2000
Silver NR-509-0800-01 Background Habitat mg/kg U 0.04405 0.0881 2000
Silver NR-510-0800-01 Background Habitat mg/kg U 0.0456 0.0912 2000
Silver NR-511-0800-01 Background Habitat mg/kg U 0.03735 0.0747 2000
Silver NR-512-0800-01 Background Habitat mg/kg U 0.0425 0.085 2000
Silver NR-513-0800-01 Background Habitat mg/kg U 0.03175 0.0635 2000
Silver NR-514-0800-01 Background Habitat mg/kg U 0.04665 0.0933 2000
Silver NR-515-0800-01 Background Habitat mg/kg U 0.04645 0.0929 2000
Silver NR-516-0800-01 Background Habitat mg/kg U 0.0585 0.117 2000
Silver NR-517-0800-01 Background Habitat mg/kg U 0.044 0.088 2000
Silver NR-518-0800-01 Background Habitat mg/kg U 0.0415 0.083 2000
Silver NR-519-0800-01 Background Habitat mg/kg U 0.0605 0.121 2000
Silver NR-520-0800-01 Background Habitat mg/kg U 0.0615 0.123 2000
Silver NR-521-0800-01 Background Habitat mg/kg U 0.0492 0.0984 2000
Silver NR-522-0800-01 Background Habitat mg/kg U 0.0499 0.0998 2000
Silver NR-523-0800-01 Background Habitat mg/kg U 0.0476 0.0952 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 36 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Silver NR-524-0800-01 Background Habitat mg/kg U 0.073 0.146 2000
Silver NR-525-0800-01 Background Habitat mg/kg U 0.063 0.126 2000
Silver NR-536 Background Habitat mg/Kg U 0.094 0.188 2004
Silver NR-537 Background Habitat mg/Kg J 0.23 2004
Silver UTNCBU-01-OCT97-01 Background Habitat mg/kg BJ 0.0245 1997
Silver UTNCBU-02-OCT97-01 Background Habitat mg/kg BJ 0.00572 1997
Silver UTNCBU-03-1298-01 Background Habitat mg/kg B 0.16 1998
Silver UTNCBU-04-1298-01 Background Habitat mg/kg B 0.164 1998
Silver UTNCBU-05-1298-01 Background Habitat mg/kg B 0.0896 1998
Silver UTNCBU-06-1298-01 Background Habitat mg/kg B 0.102 1998
Silver UTNEB-03-1298-01 Background Habitat mg/kg B 0.203 1998
Silver UTNEB-04-1298-01 Background Habitat mg/kg B 0.162 1998
Silver UTNEB-05-1298-01 Background Habitat mg/kg B 0.114 1998
Silver UTNEB-06-1298-01 Background Habitat mg/kg B 0.115 1998
Silver UTNERB-01-OCT97-01 Background Habitat mg/kg J 0.0666 1997
Silver UTNERB-02-OCT97-01 Background Habitat mg/kg BJ 0.0591 1997
Silver UTNOCB-01-OCT97-01 Background Habitat mg/kg BJ 0.0536 1997
Silver UTNOCB-02-OCT97-01 Background Habitat mg/kg = 0.161 1997
Silver UTNOCBG-03-1298-01 Background Habitat mg/kg J 0.0862 1998
Silver UTNOCBG-04-1298-01 Background Habitat mg/kg = 0.109 1998
Silver UTNOCBG-05-1298-01 Background Habitat mg/kg J 0.0921 1998
Silver UTNOCBG-06-1298-01 Background Habitat mg/kg = 0.175 1998
Silver NR-226 OnSite Habitat mg/Kg U 0.195 0.39 2002
Silver NR-227 OnSite Habitat mg/Kg U 0.19 0.38 2002
Silver NR-228 OnSite OB/OD mg/Kg U 0.18 0.36 2002
Silver NR-229 OnSite Habitat mg/Kg U 0.19 0.38 2002
Silver NR-230 OnSite Habitat mg/Kg U 0.19 0.38 2002
Silver NR-231 OnSite OB/OD mg/Kg U 0.185 0.37 2002
Silver NR-232 OnSite Habitat mg/Kg U 0.18 0.36 2002
Silver NR-233 OnSite Habitat mg/Kg U 0.185 0.37 2002
Silver NR-234 OnSite Habitat mg/Kg U 0.195 0.39 2002
Silver NR-235 OnSite Habitat mg/Kg U 0.19 0.38 2002
Silver NR-236 OnSite Habitat mg/Kg U 0.195 0.39 2002
Silver NR-237 OnSite Habitat mg/Kg U 0.19 0.38 2002
Silver NR-526 OnSite Habitat mg/Kg J 0.18 2004
Silver NR-527 OnSite Habitat mg/Kg U 0.0935 0.187 2004
Silver NR-528 OnSite Habitat mg/Kg U 0.0915 0.183 2004
Silver NR-529 OnSite Habitat mg/Kg U 0.0975 0.195 2004
Silver NR-530 OnSite Habitat mg/Kg U 0.104 0.208 2004
Silver NR-531 OnSite OB/OD mg/Kg J 0.17 2004
Silver NR-532 OnSite OB/OD mg/Kg J 0.22 2004
Silver NR-533 OnSite OB/OD mg/Kg U 0.088 0.176 2004
Silver NR-534 OnSite OB/OD mg/Kg U 0.0855 0.171 2004
Silver NR-535 OnSite OB/OD mg/Kg U 0.089 0.178 2004
Silver SS1 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS10 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS11 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS12 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS13 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS14 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS15 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS16 OnSite Habitat mg/Kg U 1 2 1991
Silver SS17 OnSite Habitat mg/Kg U 1 2 1991
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 37 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Silver SS18 OnSite Habitat mg/Kg U 1 2 1991
Silver SS19 OnSite Habitat mg/Kg U 1 2 1991
Silver SS2 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS20 OnSite Habitat mg/Kg U 1 2 1991
Silver SS3 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS4 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS5 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS6 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS7 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS8 OnSite OB/OD mg/Kg U 1 2 1991
Silver SS9 OnSite OB/OD mg/Kg U 1 2 1991
Silver TTU-SS01S OnSite OB/OD mg/Kg U 0.335 0.67 1989
Silver TTU-SS02S OnSite OB/OD mg/Kg = 4 1989
Silver TTU-SS03S OnSite OB/OD mg/Kg U 0.34 0.68 1989
Silver TTU-SS04S(D) OnSite OB/OD mg/Kg U 0.35 0.7 1989
Silver TTU-SS05S OnSite OB/OD mg/Kg U 0.33 0.66 1989
Silver TTU-SS06S(BG) OnSite Habitat mg/Kg U 0.33 0.66 1989
Strontium AMTOF-01-1298-01 Background Habitat mg/kg = 308 1998
Strontium AMTOF-02-1298-01 Background Habitat mg/kg = 267 1998
Strontium AMTOF-03-1298-01 Background Habitat mg/kg = 354 1998
Strontium AMTOF-04-1298-01 Background Habitat mg/kg = 351 1998
Strontium AMTOF-05-1298-01 Background Habitat mg/kg = 359 1998
Strontium AMTOF-06-1298-01 Background Habitat mg/kg = 343 1998
Strontium NR-238 Background Habitat mg/Kg = 231 2002
Strontium NR-239 Background Habitat mg/Kg = 290 2002
Strontium NR-500-0800-01 Background Habitat mg/kg B 304 2000
Strontium NR-501-0800-01 Background Habitat mg/kg B 1300 2000
Strontium NR-502-0800-01 Background Habitat mg/kg B 660 2000
Strontium NR-503-0800-01 Background Habitat mg/kg B 598 2000
Strontium NR-504-0800-01 Background Habitat mg/kg B 614 2000
Strontium NR-505-0800-01 Background Habitat mg/kg B 278 2000
Strontium NR-506-0800-01 Background Habitat mg/kg B 456 2000
Strontium NR-507-0800-01 Background Habitat mg/kg B 293 2000
Strontium NR-508-0800-01 Background Habitat mg/kg B 354 2000
Strontium NR-509-0800-01 Background Habitat mg/kg B 448 2000
Strontium NR-510-0800-01 Background Habitat mg/kg B 315 2000
Strontium NR-511-0800-01 Background Habitat mg/kg B 283 2000
Strontium NR-512-0800-01 Background Habitat mg/kg B 211 2000
Strontium NR-513-0800-01 Background Habitat mg/kg B 248 2000
Strontium NR-514-0800-01 Background Habitat mg/kg B 601 2000
Strontium NR-515-0800-01 Background Habitat mg/kg B 2290 2000
Strontium NR-516-0800-01 Background Habitat mg/kg B 461 2000
Strontium NR-517-0800-01 Background Habitat mg/kg B 213 2000
Strontium NR-518-0800-01 Background Habitat mg/kg B 2650 2000
Strontium NR-519-0800-01 Background Habitat mg/kg B 2000 2000
Strontium NR-520-0800-01 Background Habitat mg/kg B 834 2000
Strontium NR-521-0800-01 Background Habitat mg/kg B 2420 2000
Strontium NR-522-0800-01 Background Habitat mg/kg B 1400 2000
Strontium NR-523-0800-01 Background Habitat mg/kg B 605 2000
Strontium NR-524-0800-01 Background Habitat mg/kg B 3090 2000
Strontium NR-525-0800-01 Background Habitat mg/kg B 3680 2000
Strontium NR-536 Background Habitat mg/Kg = 343 2004
Strontium NR-537 Background Habitat mg/Kg = 307 2004
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 38 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Strontium UTNCBU-01-OCT97-01 Background Habitat mg/kg = 379 1997
Strontium UTNCBU-02-OCT97-01 Background Habitat mg/kg = 439 1997
Strontium UTNCBU-03-1298-01 Background Habitat mg/kg = 535 1998
Strontium UTNCBU-04-1298-01 Background Habitat mg/kg = 533 1998
Strontium UTNCBU-05-1298-01 Background Habitat mg/kg = 458 1998
Strontium UTNCBU-06-1298-01 Background Habitat mg/kg = 945 1998
Strontium UTNEB-03-1298-01 Background Habitat mg/kg = 518 1998
Strontium UTNEB-04-1298-01 Background Habitat mg/kg = 558 1998
Strontium UTNEB-05-1298-01 Background Habitat mg/kg = 627 1998
Strontium UTNEB-06-1298-01 Background Habitat mg/kg = 568 1998
Strontium UTNERB-01-OCT97-01 Background Habitat mg/kg = 467 1997
Strontium UTNERB-02-OCT97-01 Background Habitat mg/kg = 603 1997
Strontium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 391 1997
Strontium UTNOCB-02-OCT97-01 Background Habitat mg/kg = 459 1997
Strontium UTNOCBG-03-1298-01 Background Habitat mg/kg = 361 1998
Strontium UTNOCBG-04-1298-01 Background Habitat mg/kg = 398 1998
Strontium UTNOCBG-05-1298-01 Background Habitat mg/kg = 368 1998
Strontium UTNOCBG-06-1298-01 Background Habitat mg/kg = 370 1998
Strontium NR-226 OnSite Habitat mg/Kg = 333 2002
Strontium NR-227 OnSite Habitat mg/Kg = 321 2002
Strontium NR-228 OnSite OB/OD mg/Kg = 266 2002
Strontium NR-229 OnSite Habitat mg/Kg = 244 2002
Strontium NR-230 OnSite Habitat mg/Kg = 304 2002
Strontium NR-231 OnSite OB/OD mg/Kg = 283 2002
Strontium NR-232 OnSite Habitat mg/Kg = 246 2002
Strontium NR-233 OnSite Habitat mg/Kg = 402 2002
Strontium NR-234 OnSite Habitat mg/Kg = 322 2002
Strontium NR-235 OnSite Habitat mg/Kg = 334 2002
Strontium NR-236 OnSite Habitat mg/Kg = 248 2002
Strontium NR-237 OnSite Habitat mg/Kg = 358 2002
Strontium NR-526 OnSite Habitat mg/Kg = 460 2004
Strontium NR-527 OnSite Habitat mg/Kg = 292 2004
Strontium NR-528 OnSite Habitat mg/Kg = 416 2004
Strontium NR-529 OnSite Habitat mg/Kg = 456 2004
Strontium NR-530 OnSite Habitat mg/Kg = 404 2004
Strontium NR-531 OnSite OB/OD mg/Kg = 484 2004
Strontium NR-532 OnSite OB/OD mg/Kg = 386 2004
Strontium NR-533 OnSite OB/OD mg/Kg = 401 2004
Strontium NR-534 OnSite OB/OD mg/Kg = 387 2004
Strontium NR-535 OnSite OB/OD mg/Kg = 371 2004
Sulfur AMTOF-01-1298-01 Background Habitat mg/kg = 334 1998
Sulfur AMTOF-02-1298-01 Background Habitat mg/kg = 244 1998
Sulfur AMTOF-03-1298-01 Background Habitat mg/kg = 330 1998
Sulfur AMTOF-04-1298-01 Background Habitat mg/kg = 391 1998
Sulfur AMTOF-05-1298-01 Background Habitat mg/kg = 383 1998
Sulfur AMTOF-06-1298-01 Background Habitat mg/kg = 386 1998
Sulfur NR-500-0800-01 Background Habitat mg/kg B 277 2000
Sulfur NR-501-0800-01 Background Habitat mg/kg B 1160 2000
Sulfur NR-502-0800-01 Background Habitat mg/kg B 640 2000
Sulfur NR-503-0800-01 Background Habitat mg/kg B 440 2000
Sulfur NR-504-0800-01 Background Habitat mg/kg B 382 2000
Sulfur NR-505-0800-01 Background Habitat mg/kg = 450 2000
Sulfur NR-506-0800-01 Background Habitat mg/kg B 424 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 39 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Sulfur NR-507-0800-01 Background Habitat mg/kg B 255 2000
Sulfur NR-508-0800-01 Background Habitat mg/kg B 284 2000
Sulfur NR-509-0800-01 Background Habitat mg/kg B 610 2000
Sulfur NR-510-0800-01 Background Habitat mg/kg B 265 2000
Sulfur NR-511-0800-01 Background Habitat mg/kg B 261 2000
Sulfur NR-512-0800-01 Background Habitat mg/kg B 242 2000
Sulfur NR-513-0800-01 Background Habitat mg/kg B 266 2000
Sulfur NR-514-0800-01 Background Habitat mg/kg B 535 2000
Sulfur NR-515-0800-01 Background Habitat mg/kg B 3660 2000
Sulfur NR-516-0800-01 Background Habitat mg/kg B 1290 2000
Sulfur NR-517-0800-01 Background Habitat mg/kg B 3320 2000
Sulfur NR-518-0800-01 Background Habitat mg/kg = 3070 2000
Sulfur NR-519-0800-01 Background Habitat mg/kg = 2890 2000
Sulfur NR-520-0800-01 Background Habitat mg/kg = 2890 2000
Sulfur NR-521-0800-01 Background Habitat mg/kg = 4020 2000
Sulfur NR-522-0800-01 Background Habitat mg/kg = 4010 2000
Sulfur NR-523-0800-01 Background Habitat mg/kg = 2250 2000
Sulfur NR-524-0800-01 Background Habitat mg/kg = 2910 2000
Sulfur NR-525-0800-01 Background Habitat mg/kg = 4720 2000
Sulfur UTNCBU-01-OCT97-01 Background Habitat mg/kg = 329 1997
Sulfur UTNCBU-02-OCT97-01 Background Habitat mg/kg = 356 1997
Sulfur UTNCBU-03-1298-01 Background Habitat mg/kg = 424 1998
Sulfur UTNCBU-04-1298-01 Background Habitat mg/kg = 468 1998
Sulfur UTNCBU-05-1298-01 Background Habitat mg/kg = 351 1998
Sulfur UTNCBU-06-1298-01 Background Habitat mg/kg = 403 1998
Sulfur UTNEB-03-1298-01 Background Habitat mg/kg = 482 1998
Sulfur UTNEB-04-1298-01 Background Habitat mg/kg = 582 1998
Sulfur UTNEB-05-1298-01 Background Habitat mg/kg = 527 1998
Sulfur UTNEB-06-1298-01 Background Habitat mg/kg = 433 1998
Sulfur UTNERB-01-OCT97-01 Background Habitat mg/kg = 1100 1997
Sulfur UTNERB-02-OCT97-01 Background Habitat mg/kg = 673 1997
Sulfur UTNOCB-01-OCT97-01 Background Habitat mg/kg = 648 1997
Sulfur UTNOCB-02-OCT97-01 Background Habitat mg/kg = 741 1997
Sulfur UTNOCBG-03-1298-01 Background Habitat mg/kg = 384 1998
Sulfur UTNOCBG-04-1298-01 Background Habitat mg/kg = 350 1998
Sulfur UTNOCBG-05-1298-01 Background Habitat mg/kg = 371 1998
Sulfur UTNOCBG-06-1298-01 Background Habitat mg/kg = 351 1998
Tellurium AMTOF-01-1298-01 Background Habitat mg/kg J 0.419 1998
Tellurium AMTOF-02-1298-01 Background Habitat mg/kg J 0.171 1998
Tellurium AMTOF-03-1298-01 Background Habitat mg/kg J 0.255 1998
Tellurium AMTOF-04-1298-01 Background Habitat mg/kg J 0.36 1998
Tellurium AMTOF-05-1298-01 Background Habitat mg/kg J 0.444 1998
Tellurium AMTOF-06-1298-01 Background Habitat mg/kg J 0.279 1998
Tellurium NR-500-0800-01 Background Habitat mg/kg U 0.1515 0.303 2000
Tellurium NR-501-0800-01 Background Habitat mg/kg U 0.167 0.334 2000
Tellurium NR-502-0800-01 Background Habitat mg/kg U 0.198 0.396 2000
Tellurium NR-503-0800-01 Background Habitat mg/kg U 0.161 0.322 2000
Tellurium NR-504-0800-01 Background Habitat mg/kg U 0.1715 0.343 2000
Tellurium NR-505-0800-01 Background Habitat mg/kg U 0.191 0.382 2000
Tellurium NR-506-0800-01 Background Habitat mg/kg U 0.1525 0.305 2000
Tellurium NR-507-0800-01 Background Habitat mg/kg U 0.194 0.388 2000
Tellurium NR-508-0800-01 Background Habitat mg/kg U 0.161 0.322 2000
Tellurium NR-509-0800-01 Background Habitat mg/kg U 0.191 0.382 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 40 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Tellurium NR-510-0800-01 Background Habitat mg/kg U 0.198 0.396 2000
Tellurium NR-511-0800-01 Background Habitat mg/kg U 0.162 0.324 2000
Tellurium NR-512-0800-01 Background Habitat mg/kg U 0.1845 0.369 2000
Tellurium NR-513-0800-01 Background Habitat mg/kg U 0.1375 0.275 2000
Tellurium NR-514-0800-01 Background Habitat mg/kg U 0.2025 0.405 2000
Tellurium NR-515-0800-01 Background Habitat mg/kg U 0.2015 0.403 2000
Tellurium NR-516-0800-01 Background Habitat mg/kg U 0.2535 0.507 2000
Tellurium NR-517-0800-01 Background Habitat mg/kg U 0.191 0.382 2000
Tellurium NR-518-0800-01 Background Habitat mg/kg U 0.18 0.36 2000
Tellurium NR-519-0800-01 Background Habitat mg/kg U 0.2615 0.523 2000
Tellurium NR-520-0800-01 Background Habitat mg/kg U 0.266 0.532 2000
Tellurium NR-521-0800-01 Background Habitat mg/kg U 0.2135 0.427 2000
Tellurium NR-522-0800-01 Background Habitat mg/kg U 0.2165 0.433 2000
Tellurium NR-523-0800-01 Background Habitat mg/kg U 0.2065 0.413 2000
Tellurium NR-524-0800-01 Background Habitat mg/kg U 0.317 0.634 2000
Tellurium NR-525-0800-01 Background Habitat mg/kg U 0.451 0.902 2000
Tellurium UTNCBU-01-OCT97-01 Background Habitat mg/kg U 0.372 0.744 1997
Tellurium UTNCBU-02-OCT97-01 Background Habitat mg/kg U 0.376 0.752 1997
Tellurium UTNCBU-03-1298-01 Background Habitat mg/kg = 0.506 1998
Tellurium UTNCBU-04-1298-01 Background Habitat mg/kg = 0.704 1998
Tellurium UTNCBU-05-1298-01 Background Habitat mg/kg = 0.712 1998
Tellurium UTNCBU-06-1298-01 Background Habitat mg/kg = 0.349 1998
Tellurium UTNEB-03-1298-01 Background Habitat mg/kg = 0.769 1998
Tellurium UTNEB-04-1298-01 Background Habitat mg/kg = 0.549 1998
Tellurium UTNEB-05-1298-01 Background Habitat mg/kg = 0.627 1998
Tellurium UTNEB-06-1298-01 Background Habitat mg/kg J 0.12 1998
Tellurium UTNERB-01-OCT97-01 Background Habitat mg/kg U 0.4525 0.905 1997
Tellurium UTNERB-02-OCT97-01 Background Habitat mg/kg U 0.3695 0.739 1997
Tellurium UTNOCB-01-OCT97-01 Background Habitat mg/kg U 0.414 0.828 1997
Tellurium UTNOCB-02-OCT97-01 Background Habitat mg/kg U 0.3485 0.697 1997
Tellurium UTNOCBG-03-1298-01 Background Habitat mg/kg B 0.617 1998
Tellurium UTNOCBG-04-1298-01 Background Habitat mg/kg B 0.45 1998
Tellurium UTNOCBG-05-1298-01 Background Habitat mg/kg B 0.661 1998
Tellurium UTNOCBG-06-1298-01 Background Habitat mg/kg B 0.526 1998
Thallium AMTOF-01-1298-01 Background Habitat mg/kg J 0.259 1998
Thallium AMTOF-02-1298-01 Background Habitat mg/kg J 0.317 1998
Thallium AMTOF-03-1298-01 Background Habitat mg/kg = 0.523 1998
Thallium AMTOF-04-1298-01 Background Habitat mg/kg = 0.475 1998
Thallium AMTOF-05-1298-01 Background Habitat mg/kg = 0.352 1998
Thallium AMTOF-06-1298-01 Background Habitat mg/kg = 0.435 1998
Thallium NR-238 Background Habitat mg/Kg = 0.32 2002
Thallium NR-239 Background Habitat mg/Kg = 0.34 2002
Thallium NR-500-0800-01 Background Habitat mg/kg U 0.55 1.1 2000
Thallium NR-501-0800-01 Background Habitat mg/kg U 0.605 1.21 2000
Thallium NR-502-0800-01 Background Habitat mg/kg U 0.72 1.44 2000
Thallium NR-503-0800-01 Background Habitat mg/kg U 0.585 1.17 2000
Thallium NR-504-0800-01 Background Habitat mg/kg U 0.62 1.24 2000
Thallium NR-505-0800-01 Background Habitat mg/kg U 0.695 1.39 2000
Thallium NR-506-0800-01 Background Habitat mg/kg U 0.555 1.11 2000
Thallium NR-507-0800-01 Background Habitat mg/kg U 0.705 1.41 2000
Thallium NR-508-0800-01 Background Habitat mg/kg U 0.585 1.17 2000
Thallium NR-509-0800-01 Background Habitat mg/kg U 0.695 1.39 2000
Thallium NR-510-0800-01 Background Habitat mg/kg U 0.72 1.44 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 41 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Thallium NR-511-0800-01 Background Habitat mg/kg U 0.59 1.18 2000
Thallium NR-512-0800-01 Background Habitat mg/kg U 0.67 1.34 2000
Thallium NR-513-0800-01 Background Habitat mg/kg = 0.999 2000
Thallium NR-514-0800-01 Background Habitat mg/kg U 0.735 1.47 2000
Thallium NR-515-0800-01 Background Habitat mg/kg U 0.73 1.46 2000
Thallium NR-516-0800-01 Background Habitat mg/kg U 0.92 1.84 2000
Thallium NR-517-0800-01 Background Habitat mg/kg U 0.04635 0.0927 2000
Thallium NR-518-0800-01 Background Habitat mg/kg U 0.605 1.21 2000
Thallium NR-519-0800-01 Background Habitat mg/kg U 0.1175 0.235 2000
Thallium NR-520-0800-01 Background Habitat mg/kg U 1.1 2.2 2000
Thallium NR-521-0800-01 Background Habitat mg/kg U 1.76 3.52 2000
Thallium NR-522-0800-01 Background Habitat mg/kg U 0.895 1.79 2000
Thallium NR-523-0800-01 Background Habitat mg/kg U 0.85 1.7 2000
Thallium NR-524-0800-01 Background Habitat mg/kg U 1.305 2.61 2000
Thallium NR-525-0800-01 Background Habitat mg/kg U 0.76 1.52 2000
Thallium NR-536 Background Habitat mg/Kg J 0.24 2004
Thallium NR-537 Background Habitat mg/Kg J 0.28 2004
Thallium UTNCBU-01-OCT97-01 Background Habitat mg/kg BJ 0.123 1997
Thallium UTNCBU-02-OCT97-01 Background Habitat mg/kg BJ 0.142 1997
Thallium UTNCBU-03-1298-01 Background Habitat mg/kg J 0.144 1998
Thallium UTNCBU-04-1298-01 Background Habitat mg/kg J 0.178 1998
Thallium UTNCBU-05-1298-01 Background Habitat mg/kg J 0.0425 1998
Thallium UTNCBU-06-1298-01 Background Habitat mg/kg J 0.0151 1998
Thallium UTNEB-03-1298-01 Background Habitat mg/kg U 0.1705 0.341 1998
Thallium UTNEB-04-1298-01 Background Habitat mg/kg U 0.1965 0.393 1998
Thallium UTNEB-05-1298-01 Background Habitat mg/kg U 0.1625 0.325 1998
Thallium UTNEB-06-1298-01 Background Habitat mg/kg U 0.223 0.446 1998
Thallium UTNERB-01-OCT97-01 Background Habitat mg/kg = 1.2 1997
Thallium UTNERB-02-OCT97-01 Background Habitat mg/kg B 0.566 1997
Thallium UTNOCB-01-OCT97-01 Background Habitat mg/kg BJ 0.223 1997
Thallium UTNOCB-02-OCT97-01 Background Habitat mg/kg BJ 0.236 1997
Thallium UTNOCBG-03-1298-01 Background Habitat mg/kg = 0.558 1998
Thallium UTNOCBG-04-1298-01 Background Habitat mg/kg J 0.189 1998
Thallium UTNOCBG-05-1298-01 Background Habitat mg/kg J 0.279 1998
Thallium UTNOCBG-06-1298-01 Background Habitat mg/kg = 0.515 1998
Thallium NR-226 OnSite Habitat mg/Kg = 0.21 2002
Thallium NR-227 OnSite Habitat mg/Kg = 0.17 2002
Thallium NR-228 OnSite OB/OD mg/Kg = 0.34 2002
Thallium NR-229 OnSite Habitat mg/Kg = 0.3 2002
Thallium NR-230 OnSite Habitat mg/Kg = 0.4 2002
Thallium NR-231 OnSite OB/OD mg/Kg = 0.35 2002
Thallium NR-232 OnSite Habitat mg/Kg = 0.55 2002
Thallium NR-233 OnSite Habitat mg/Kg = 0.34 2002
Thallium NR-234 OnSite Habitat mg/Kg = 0.35 2002
Thallium NR-235 OnSite Habitat mg/Kg = 0.29 2002
Thallium NR-236 OnSite Habitat mg/Kg = 0.32 2002
Thallium NR-237 OnSite Habitat mg/Kg = 0.32 2002
Thallium NR-526 OnSite Habitat mg/Kg J 0.28 2004
Thallium NR-527 OnSite Habitat mg/Kg J 0.22 2004
Thallium NR-528 OnSite Habitat mg/Kg J 0.15 2004
Thallium NR-529 OnSite Habitat mg/Kg J 0.26 2004
Thallium NR-530 OnSite Habitat mg/Kg J 0.24 2004
Thallium NR-531 OnSite OB/OD mg/Kg J 0.11 2004
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 42 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Thallium NR-532 OnSite OB/OD mg/Kg J 0.11 2004
Thallium NR-533 OnSite OB/OD mg/Kg J 0.21 2004
Thallium NR-534 OnSite OB/OD mg/Kg J 0.42 2004
Thallium NR-535 OnSite OB/OD mg/Kg J 0.21 2004
Thallium SS1 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS10 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS11 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS12 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS13 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS14 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS15 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS16 OnSite Habitat mg/Kg U 2.5 5 1991
Thallium SS17 OnSite Habitat mg/Kg U 2.5 5 1991
Thallium SS18 OnSite Habitat mg/Kg U 2.5 5 1991
Thallium SS19 OnSite Habitat mg/Kg U 2.5 5 1991
Thallium SS2 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS20 OnSite Habitat mg/Kg U 2.5 5 1991
Thallium SS3 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS4 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS5 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS6 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS7 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS8 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium SS9 OnSite OB/OD mg/Kg U 2.5 5 1991
Thallium TTU-SS01S OnSite OB/OD mg/Kg = 0.22 1989
Thallium TTU-SS02S OnSite OB/OD mg/Kg = 0.22 1989
Thallium TTU-SS03S OnSite OB/OD mg/Kg U 0.085 0.17 1989
Thallium TTU-SS04S(D) OnSite OB/OD mg/Kg U 0.085 0.17 1989
Thallium TTU-SS05S OnSite OB/OD mg/Kg = 0.42 1989
Thallium TTU-SS06S(BG) OnSite Habitat mg/Kg = 0.24 1989
Tin AMTOF-01-1298-01 Background Habitat mg/kg = 1.15 1998
Tin AMTOF-02-1298-01 Background Habitat mg/kg = 0.798 1998
Tin AMTOF-03-1298-01 Background Habitat mg/kg = 1.18 1998
Tin AMTOF-04-1298-01 Background Habitat mg/kg = 1.23 1998
Tin AMTOF-05-1298-01 Background Habitat mg/kg = 0.942 1998
Tin AMTOF-06-1298-01 Background Habitat mg/kg = 1.3 1998
Tin NR-500-0800-01 Background Habitat mg/kg JB 0.475 2000
Tin NR-501-0800-01 Background Habitat mg/kg JB 0.427 2000
Tin NR-502-0800-01 Background Habitat mg/kg JB 0.663 2000
Tin NR-503-0800-01 Background Habitat mg/kg JB 0.427 2000
Tin NR-504-0800-01 Background Habitat mg/kg JB 0.54 2000
Tin NR-505-0800-01 Background Habitat mg/kg JB 0.444 2000
Tin NR-506-0800-01 Background Habitat mg/kg JB 0.383 2000
Tin NR-507-0800-01 Background Habitat mg/kg JB 0.486 2000
Tin NR-508-0800-01 Background Habitat mg/kg JB 0.258 2000
Tin NR-509-0800-01 Background Habitat mg/kg JB 0.519 2000
Tin NR-510-0800-01 Background Habitat mg/kg JB 0.428 2000
Tin NR-511-0800-01 Background Habitat mg/kg JB 0.406 2000
Tin NR-512-0800-01 Background Habitat mg/kg JB 0.481 2000
Tin NR-513-0800-01 Background Habitat mg/kg JB 0.349 2000
Tin NR-514-0800-01 Background Habitat mg/kg JB 0.468 2000
Tin NR-515-0800-01 Background Habitat mg/kg JB 0.404 2000
Tin NR-516-0800-01 Background Habitat mg/kg JB 0.754 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 43 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Tin NR-517-0800-01 Background Habitat mg/kg JB 0.432 2000
Tin NR-518-0800-01 Background Habitat mg/kg JB 0.537 2000
Tin NR-519-0800-01 Background Habitat mg/kg JB 0.622 2000
Tin NR-520-0800-01 Background Habitat mg/kg JB 0.663 2000
Tin NR-521-0800-01 Background Habitat mg/kg JB 0.586 2000
Tin NR-522-0800-01 Background Habitat mg/kg JB 0.78 2000
Tin NR-523-0800-01 Background Habitat mg/kg JB 0.591 2000
Tin NR-524-0800-01 Background Habitat mg/kg JB 0.752 2000
Tin NR-525-0800-01 Background Habitat mg/kg JB 0.636 2000
Tin UTNCBU-01-OCT97-01 Background Habitat mg/kg J 0.624 1997
Tin UTNCBU-02-OCT97-01 Background Habitat mg/kg J 0.591 1997
Tin UTNCBU-03-1298-01 Background Habitat mg/kg = 1.01 1998
Tin UTNCBU-04-1298-01 Background Habitat mg/kg = 0.964 1998
Tin UTNCBU-05-1298-01 Background Habitat mg/kg = 0.465 1998
Tin UTNCBU-06-1298-01 Background Habitat mg/kg = 0.551 1998
Tin UTNEB-03-1298-01 Background Habitat mg/kg = 0.709 1998
Tin UTNEB-04-1298-01 Background Habitat mg/kg = 1.28 1998
Tin UTNEB-05-1298-01 Background Habitat mg/kg = 0.925 1998
Tin UTNEB-06-1298-01 Background Habitat mg/kg = 0.509 1998
Tin UTNERB-01-OCT97-01 Background Habitat mg/kg J 1.28 1997
Tin UTNERB-02-OCT97-01 Background Habitat mg/kg J 0.975 1997
Tin UTNOCB-01-OCT97-01 Background Habitat mg/kg J 0.799 1997
Tin UTNOCB-02-OCT97-01 Background Habitat mg/kg J 0.828 1997
Tin UTNOCBG-03-1298-01 Background Habitat mg/kg = 0.991 1998
Tin UTNOCBG-04-1298-01 Background Habitat mg/kg = 0.83 1998
Tin UTNOCBG-05-1298-01 Background Habitat mg/kg = 0.902 1998
Tin UTNOCBG-06-1298-01 Background Habitat mg/kg = 0.807 1998
Titanium AMTOF-01-1298-01 Background Habitat mg/kg = 446 1998
Titanium AMTOF-02-1298-01 Background Habitat mg/kg = 300 1998
Titanium AMTOF-03-1298-01 Background Habitat mg/kg = 417 1998
Titanium AMTOF-04-1298-01 Background Habitat mg/kg = 487 1998
Titanium AMTOF-05-1298-01 Background Habitat mg/kg = 399 1998
Titanium AMTOF-06-1298-01 Background Habitat mg/kg = 432 1998
Titanium NR-500-0800-01 Background Habitat mg/kg = 360 2000
Titanium NR-501-0800-01 Background Habitat mg/kg = 220 2000
Titanium NR-502-0800-01 Background Habitat mg/kg = 392 2000
Titanium NR-503-0800-01 Background Habitat mg/kg = 378 2000
Titanium NR-504-0800-01 Background Habitat mg/kg = 365 2000
Titanium NR-505-0800-01 Background Habitat mg/kg = 422 2000
Titanium NR-506-0800-01 Background Habitat mg/kg = 340 2000
Titanium NR-507-0800-01 Background Habitat mg/kg = 338 2000
Titanium NR-508-0800-01 Background Habitat mg/kg = 319 2000
Titanium NR-509-0800-01 Background Habitat mg/kg = 285 2000
Titanium NR-510-0800-01 Background Habitat mg/kg = 226 2000
Titanium NR-511-0800-01 Background Habitat mg/kg = 308 2000
Titanium NR-512-0800-01 Background Habitat mg/kg = 385 2000
Titanium NR-513-0800-01 Background Habitat mg/kg = 331 2000
Titanium NR-514-0800-01 Background Habitat mg/kg = 372 2000
Titanium NR-515-0800-01 Background Habitat mg/kg = 81.6 2000
Titanium NR-516-0800-01 Background Habitat mg/kg = 385 2000
Titanium NR-517-0800-01 Background Habitat mg/kg = 229 2000
Titanium NR-518-0800-01 Background Habitat mg/kg = 59.7 2000
Titanium NR-519-0800-01 Background Habitat mg/kg = 161 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 44 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Titanium NR-520-0800-01 Background Habitat mg/kg = 167 2000
Titanium NR-521-0800-01 Background Habitat mg/kg = 113 2000
Titanium NR-522-0800-01 Background Habitat mg/kg = 266 2000
Titanium NR-523-0800-01 Background Habitat mg/kg = 240 2000
Titanium NR-524-0800-01 Background Habitat mg/kg = 185 2000
Titanium NR-525-0800-01 Background Habitat mg/kg = 155 2000
Titanium UTNCBU-01-OCT97-01 Background Habitat mg/kg = 337 1997
Titanium UTNCBU-02-OCT97-01 Background Habitat mg/kg = 336 1997
Titanium UTNCBU-03-1298-01 Background Habitat mg/kg = 409 1998
Titanium UTNCBU-04-1298-01 Background Habitat mg/kg = 429 1998
Titanium UTNCBU-05-1298-01 Background Habitat mg/kg = 220 1998
Titanium UTNCBU-06-1298-01 Background Habitat mg/kg = 224 1998
Titanium UTNEB-03-1298-01 Background Habitat mg/kg = 281 1998
Titanium UTNEB-04-1298-01 Background Habitat mg/kg = 497 1998
Titanium UTNEB-05-1298-01 Background Habitat mg/kg = 377 1998
Titanium UTNEB-06-1298-01 Background Habitat mg/kg = 235 1998
Titanium UTNERB-01-OCT97-01 Background Habitat mg/kg = 501 1997
Titanium UTNERB-02-OCT97-01 Background Habitat mg/kg = 493 1997
Titanium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 392 1997
Titanium UTNOCB-02-OCT97-01 Background Habitat mg/kg = 345 1997
Titanium UTNOCBG-03-1298-01 Background Habitat mg/kg H 349 1998
Titanium UTNOCBG-04-1298-01 Background Habitat mg/kg = 334 1998
Titanium UTNOCBG-05-1298-01 Background Habitat mg/kg = 351 1998
Titanium UTNOCBG-06-1298-01 Background Habitat mg/kg = 300 1998
Tungsten AMTOF-01-1298-01 Background Habitat mg/kg U 0.147 0.294 1998
Tungsten AMTOF-02-1298-01 Background Habitat mg/kg U 0.11 0.22 1998
Tungsten AMTOF-03-1298-01 Background Habitat mg/kg U 0.1365 0.273 1998
Tungsten AMTOF-04-1298-01 Background Habitat mg/kg U 0.1415 0.283 1998
Tungsten AMTOF-05-1298-01 Background Habitat mg/kg U 0.1435 0.287 1998
Tungsten AMTOF-06-1298-01 Background Habitat mg/kg U 0.144 0.288 1998
Tungsten NR-500-0800-01 Background Habitat mg/kg UB 0.2045 0.409 2000
Tungsten NR-501-0800-01 Background Habitat mg/kg UB 0.225 0.45 2000
Tungsten NR-502-0800-01 Background Habitat mg/kg UB 0.267 0.534 2000
Tungsten NR-503-0800-01 Background Habitat mg/kg UB 0.2175 0.435 2000
Tungsten NR-504-0800-01 Background Habitat mg/kg UB 0.2315 0.463 2000
Tungsten NR-505-0800-01 Background Habitat mg/kg UB 0.258 0.516 2000
Tungsten NR-506-0800-01 Background Habitat mg/kg UB 0.2055 0.411 2000
Tungsten NR-507-0800-01 Background Habitat mg/kg UB 0.2615 0.523 2000
Tungsten NR-508-0800-01 Background Habitat mg/kg UB 0.132 0.264 2000
Tungsten NR-509-0800-01 Background Habitat mg/kg UB 0.258 0.516 2000
Tungsten NR-510-0800-01 Background Habitat mg/kg UB 0.267 0.534 2000
Tungsten NR-511-0800-01 Background Habitat mg/kg UB 0.2185 0.437 2000
Tungsten NR-512-0800-01 Background Habitat mg/kg UB 0.2485 0.497 2000
Tungsten NR-513-0800-01 Background Habitat mg/kg UB 0.186 0.372 2000
Tungsten NR-514-0800-01 Background Habitat mg/kg UB 0.273 0.546 2000
Tungsten NR-515-0800-01 Background Habitat mg/kg UB 0.2715 0.543 2000
Tungsten NR-516-0800-01 Background Habitat mg/kg UB 0.342 0.684 2000
Tungsten NR-517-0800-01 Background Habitat mg/kg UB 0.2575 0.515 2000
Tungsten NR-518-0800-01 Background Habitat mg/kg UB 0.243 0.486 2000
Tungsten NR-519-0800-01 Background Habitat mg/kg UB 0.3525 0.705 2000
Tungsten NR-520-0800-01 Background Habitat mg/kg UB 0.3595 0.719 2000
Tungsten NR-521-0800-01 Background Habitat mg/kg UB 0.288 0.576 2000
Tungsten NR-522-0800-01 Background Habitat mg/kg UB 0.292 0.584 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 45 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Tungsten NR-523-0800-01 Background Habitat mg/kg UB 0.2785 0.557 2000
Tungsten NR-524-0800-01 Background Habitat mg/kg UB 0.4275 0.855 2000
Tungsten NR-525-0800-01 Background Habitat mg/kg UB 0.158 0.316 2000
Tungsten UTNCBU-01-OCT97-01 Background Habitat mg/kg BJ 0.0623 1997
Tungsten UTNCBU-02-OCT97-01 Background Habitat mg/kg U 0.895 1.79 1997
Tungsten UTNCBU-03-1298-01 Background Habitat mg/kg BJ 0.629 1998
Tungsten UTNCBU-04-1298-01 Background Habitat mg/kg BJ 0.323 1998
Tungsten UTNCBU-05-1298-01 Background Habitat mg/kg BJ 0.338 1998
Tungsten UTNCBU-06-1298-01 Background Habitat mg/kg BJ 0.114 1998
Tungsten UTNEB-03-1298-01 Background Habitat mg/kg BJ 0.331 1998
Tungsten UTNEB-04-1298-01 Background Habitat mg/kg BJ 0.0279 1998
Tungsten UTNEB-05-1298-01 Background Habitat mg/kg BJ 0.103 1998
Tungsten UTNEB-06-1298-01 Background Habitat mg/kg BJ 0.0978 1998
Tungsten UTNERB-01-OCT97-01 Background Habitat mg/kg BJ 0.116 1997
Tungsten UTNERB-02-OCT97-01 Background Habitat mg/kg BJ 0.233 1997
Tungsten UTNOCB-01-OCT97-01 Background Habitat mg/kg BJ 0.197 1997
Tungsten UTNOCB-02-OCT97-01 Background Habitat mg/kg U 0.83 1.66 1997
Tungsten UTNOCBG-03-1298-01 Background Habitat mg/kg U 0.3555 0.711 1998
Tungsten UTNOCBG-04-1298-01 Background Habitat mg/kg U 0.3405 0.681 1998
Tungsten UTNOCBG-05-1298-01 Background Habitat mg/kg U 0.3295 0.659 1998
Tungsten UTNOCBG-06-1298-01 Background Habitat mg/kg U 0.245 0.49 1998
Vanadium AMTOF-01-1298-01 Background Habitat mg/kg = 21.1 1998
Vanadium AMTOF-02-1298-01 Background Habitat mg/kg = 23.9 1998
Vanadium AMTOF-03-1298-01 Background Habitat mg/kg = 24 1998
Vanadium AMTOF-04-1298-01 Background Habitat mg/kg = 25.2 1998
Vanadium AMTOF-05-1298-01 Background Habitat mg/kg = 17.8 1998
Vanadium AMTOF-06-1298-01 Background Habitat mg/kg = 21.7 1998
Vanadium NR-238 Background Habitat mg/Kg = 22.8 2002
Vanadium NR-239 Background Habitat mg/Kg = 17.3 2002
Vanadium NR-500-0800-01 Background Habitat mg/kg = 20.9 2000
Vanadium NR-501-0800-01 Background Habitat mg/kg = 17.9 2000
Vanadium NR-502-0800-01 Background Habitat mg/kg = 22.8 2000
Vanadium NR-503-0800-01 Background Habitat mg/kg = 21.6 2000
Vanadium NR-504-0800-01 Background Habitat mg/kg = 20.9 2000
Vanadium NR-505-0800-01 Background Habitat mg/kg = 22.2 2000
Vanadium NR-506-0800-01 Background Habitat mg/kg = 20.4 2000
Vanadium NR-507-0800-01 Background Habitat mg/kg = 18.2 2000
Vanadium NR-508-0800-01 Background Habitat mg/kg = 18.9 2000
Vanadium NR-509-0800-01 Background Habitat mg/kg = 21.7 2000
Vanadium NR-510-0800-01 Background Habitat mg/kg = 14.9 2000
Vanadium NR-511-0800-01 Background Habitat mg/kg = 19.1 2000
Vanadium NR-512-0800-01 Background Habitat mg/kg = 22.5 2000
Vanadium NR-513-0800-01 Background Habitat mg/kg = 19.1 2000
Vanadium NR-514-0800-01 Background Habitat mg/kg = 22.4 2000
Vanadium NR-515-0800-01 Background Habitat mg/kg = 8.28 2000
Vanadium NR-516-0800-01 Background Habitat mg/kg = 26.9 2000
Vanadium NR-517-0800-01 Background Habitat mg/kg = 16.4 2000
Vanadium NR-518-0800-01 Background Habitat mg/kg = 9.48 2000
Vanadium NR-519-0800-01 Background Habitat mg/kg = 14.9 2000
Vanadium NR-520-0800-01 Background Habitat mg/kg = 14.4 2000
Vanadium NR-521-0800-01 Background Habitat mg/kg = 11.6 2000
Vanadium NR-522-0800-01 Background Habitat mg/kg = 23.3 2000
Vanadium NR-523-0800-01 Background Habitat mg/kg = 20.1 2000
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 46 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Vanadium NR-524-0800-01 Background Habitat mg/kg = 17.5 2000
Vanadium NR-525-0800-01 Background Habitat mg/kg = 12.5 2000
Vanadium NR-536 Background Habitat mg/Kg = 19.5 2004
Vanadium NR-537 Background Habitat mg/Kg = 21.9 2004
Vanadium UTNCBU-01-OCT97-01 Background Habitat mg/kg = 21.3 1997
Vanadium UTNCBU-02-OCT97-01 Background Habitat mg/kg = 20.5 1997
Vanadium UTNCBU-03-1298-01 Background Habitat mg/kg = 25.6 1998
Vanadium UTNCBU-04-1298-01 Background Habitat mg/kg = 25.7 1998
Vanadium UTNCBU-05-1298-01 Background Habitat mg/kg = 20.6 1998
Vanadium UTNCBU-06-1298-01 Background Habitat mg/kg = 21.1 1998
Vanadium UTNEB-03-1298-01 Background Habitat mg/kg = 23.8 1998
Vanadium UTNEB-04-1298-01 Background Habitat mg/kg = 28 1998
Vanadium UTNEB-05-1298-01 Background Habitat mg/kg = 23.9 1998
Vanadium UTNEB-06-1298-01 Background Habitat mg/kg = 23.2 1998
Vanadium UTNERB-01-OCT97-01 Background Habitat mg/kg = 35.5 1997
Vanadium UTNERB-02-OCT97-01 Background Habitat mg/kg = 33.2 1997
Vanadium UTNOCB-01-OCT97-01 Background Habitat mg/kg = 25.5 1997
Vanadium UTNOCB-02-OCT97-01 Background Habitat mg/kg = 20.7 1997
Vanadium UTNOCBG-03-1298-01 Background Habitat mg/kg J 19.6 1998
Vanadium UTNOCBG-04-1298-01 Background Habitat mg/kg = 18.3 1998
Vanadium UTNOCBG-05-1298-01 Background Habitat mg/kg = 19.6 1998
Vanadium UTNOCBG-06-1298-01 Background Habitat mg/kg = 24.3 1998
Vanadium NR-226 OnSite Habitat mg/Kg = 9.9 2002
Vanadium NR-227 OnSite Habitat mg/Kg = 13.6 2002
Vanadium NR-228 OnSite OB/OD mg/Kg = 15.6 2002
Vanadium NR-229 OnSite Habitat mg/Kg = 21.5 2002
Vanadium NR-230 OnSite Habitat mg/Kg = 19.9 2002
Vanadium NR-231 OnSite OB/OD mg/Kg = 19.8 2002
Vanadium NR-232 OnSite Habitat mg/Kg = 25.7 2002
Vanadium NR-233 OnSite Habitat mg/Kg = 18.8 2002
Vanadium NR-234 OnSite Habitat mg/Kg = 18.8 2002
Vanadium NR-235 OnSite Habitat mg/Kg = 20.3 2002
Vanadium NR-236 OnSite Habitat mg/Kg = 16.4 2002
Vanadium NR-237 OnSite Habitat mg/Kg = 18.7 2002
Vanadium NR-526 OnSite Habitat mg/Kg = 12.9 2004
Vanadium NR-527 OnSite Habitat mg/Kg = 17.8 2004
Vanadium NR-528 OnSite Habitat mg/Kg = 11.3 2004
Vanadium NR-529 OnSite Habitat mg/Kg = 16.2 2004
Vanadium NR-530 OnSite Habitat mg/Kg = 15 2004
Vanadium NR-531 OnSite OB/OD mg/Kg = 14.1 2004
Vanadium NR-532 OnSite OB/OD mg/Kg = 11.8 2004
Vanadium NR-533 OnSite OB/OD mg/Kg = 17.5 2004
Vanadium NR-534 OnSite OB/OD mg/Kg = 16 2004
Vanadium NR-535 OnSite OB/OD mg/Kg = 19.2 2004
Vanadium TTU-SS01S OnSite OB/OD mg/Kg = 14.9 1989
Vanadium TTU-SS02S OnSite OB/OD mg/Kg = 16.5 1989
Vanadium TTU-SS03S OnSite OB/OD mg/Kg = 16.4 1989
Vanadium TTU-SS04S(D) OnSite OB/OD mg/Kg = 13.1 1989
Vanadium TTU-SS05S OnSite OB/OD mg/Kg = 17 1989
Vanadium TTU-SS06S(BG) OnSite Habitat mg/Kg = 19.2 1989
Zinc AMTOF-01-1298-01 Background Habitat mg/kg = 47 1998
Zinc AMTOF-02-1298-01 Background Habitat mg/kg = 48.5 1998
Zinc AMTOF-03-1298-01 Background Habitat mg/kg = 48.3 1998
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 47 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Zinc AMTOF-04-1298-01 Background Habitat mg/kg = 49.2 1998
Zinc AMTOF-05-1298-01 Background Habitat mg/kg = 40.8 1998
Zinc AMTOF-06-1298-01 Background Habitat mg/kg = 45.2 1998
Zinc NR-238 Background Habitat mg/Kg = 53.2 2002
Zinc NR-239 Background Habitat mg/Kg = 45.3 2002
Zinc NR-500-0800-01 Background Habitat mg/kg B 41.2 2000
Zinc NR-501-0800-01 Background Habitat mg/kg B 23.9 2000
Zinc NR-502-0800-01 Background Habitat mg/kg B 45.3 2000
Zinc NR-503-0800-01 Background Habitat mg/kg B 39.5 2000
Zinc NR-504-0800-01 Background Habitat mg/kg B 34 2000
Zinc NR-505-0800-01 Background Habitat mg/kg B 44.5 2000
Zinc NR-506-0800-01 Background Habitat mg/kg B 41.5 2000
Zinc NR-507-0800-01 Background Habitat mg/kg B 38.3 2000
Zinc NR-508-0800-01 Background Habitat mg/kg B 37.8 2000
Zinc NR-509-0800-01 Background Habitat mg/kg B 39.4 2000
Zinc NR-510-0800-01 Background Habitat mg/kg B 33.3 2000
Zinc NR-511-0800-01 Background Habitat mg/kg B 44.5 2000
Zinc NR-512-0800-01 Background Habitat mg/kg B 50.7 2000
Zinc NR-513-0800-01 Background Habitat mg/kg B 46.6 2000
Zinc NR-514-0800-01 Background Habitat mg/kg B 37.4 2000
Zinc NR-515-0800-01 Background Habitat mg/kg B 8.83 2000
Zinc NR-516-0800-01 Background Habitat mg/kg B 52.3 2000
Zinc NR-517-0800-01 Background Habitat mg/kg B 13.2 2000
Zinc NR-518-0800-01 Background Habitat mg/kg = 6.37 2000
Zinc NR-519-0800-01 Background Habitat mg/kg = 17.6 2000
Zinc NR-520-0800-01 Background Habitat mg/kg = 18.1 2000
Zinc NR-521-0800-01 Background Habitat mg/kg = 12 2000
Zinc NR-522-0800-01 Background Habitat mg/kg = 34.2 2000
Zinc NR-523-0800-01 Background Habitat mg/kg = 29 2000
Zinc NR-524-0800-01 Background Habitat mg/kg = 22.6 2000
Zinc NR-525-0800-01 Background Habitat mg/kg = 17.8 2000
Zinc NR-536 Background Habitat mg/Kg = 61.1 2004
Zinc NR-537 Background Habitat mg/Kg = 78 2004
Zinc UTNCBU-01-OCT97-01 Background Habitat mg/kg = 32.6 1997
Zinc UTNCBU-02-OCT97-01 Background Habitat mg/kg = 28.5 1997
Zinc UTNCBU-03-1298-01 Background Habitat mg/kg = 42.2 1998
Zinc UTNCBU-04-1298-01 Background Habitat mg/kg = 40.9 1998
Zinc UTNCBU-05-1298-01 Background Habitat mg/kg = 30.1 1998
Zinc UTNCBU-06-1298-01 Background Habitat mg/kg = 30.1 1998
Zinc UTNEB-03-1298-01 Background Habitat mg/kg = 34.2 1998
Zinc UTNEB-04-1298-01 Background Habitat mg/kg = 50.4 1998
Zinc UTNEB-05-1298-01 Background Habitat mg/kg = 36.9 1998
Zinc UTNEB-06-1298-01 Background Habitat mg/kg = 32.2 1998
Zinc UTNERB-01-OCT97-01 Background Habitat mg/kg = 54 1997
Zinc UTNERB-02-OCT97-01 Background Habitat mg/kg = 43.4 1997
Zinc UTNOCB-01-OCT97-01 Background Habitat mg/kg = 48.4 1997
Zinc UTNOCB-02-OCT97-01 Background Habitat mg/kg = 44.3 1997
Zinc UTNOCBG-03-1298-01 Background Habitat mg/kg = 42.9 1998
Zinc UTNOCBG-04-1298-01 Background Habitat mg/kg = 38.9 1998
Zinc UTNOCBG-05-1298-01 Background Habitat mg/kg = 40.5 1998
Zinc UTNOCBG-06-1298-01 Background Habitat mg/kg = 51.1 1998
Zinc NR-226 OnSite Habitat mg/Kg = 29.7 2002
Zinc NR-227 OnSite Habitat mg/Kg = 38.8 2002
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 48 OF 49
Table B-1
Sample Data for Inorganics in TTU Background and Site Soils
Attachment 10A - Thermal Treatment Unit, Ecological Risk Assessment
Analyte Location Type Habitat Units Qualifier Result
Detection
Limit
Sample
Year
Zinc NR-228 OnSite OB/OD mg/Kg = 51.9 2002
Zinc NR-229 OnSite Habitat mg/Kg = 54.7 2002
Zinc NR-230 OnSite Habitat mg/Kg = 55.5 2002
Zinc NR-231 OnSite OB/OD mg/Kg = 52.7 2002
Zinc NR-232 OnSite Habitat mg/Kg = 57.5 2002
Zinc NR-233 OnSite Habitat mg/Kg = 36.4 2002
Zinc NR-234 OnSite Habitat mg/Kg = 59.2 2002
Zinc NR-235 OnSite Habitat mg/Kg = 53.2 2002
Zinc NR-236 OnSite Habitat mg/Kg = 48.8 2002
Zinc NR-237 OnSite Habitat mg/Kg = 42 2002
Zinc NR-526 OnSite Habitat mg/Kg = 42 2004
Zinc NR-527 OnSite Habitat mg/Kg = 60.1 2004
Zinc NR-528 OnSite Habitat mg/Kg = 39.8 2004
Zinc NR-529 OnSite Habitat mg/Kg = 58.2 2004
Zinc NR-530 OnSite Habitat mg/Kg = 33.5 2004
Zinc NR-531 OnSite OB/OD mg/Kg = 583 2004
Zinc NR-532 OnSite OB/OD mg/Kg = 82.7 2004
Zinc NR-533 OnSite OB/OD mg/Kg = 37.1 2004
Zinc NR-534 OnSite OB/OD mg/Kg = 33.6 2004
Zinc NR-535 OnSite OB/OD mg/Kg = 35.6 2004
Zinc SS1 OnSite OB/OD mg/Kg = 43 1991
Zinc SS10 OnSite OB/OD mg/Kg = 61 1991
Zinc SS11 OnSite OB/OD mg/Kg = 63 1991
Zinc SS12 OnSite OB/OD mg/Kg = 75 1991
Zinc SS13 OnSite OB/OD mg/Kg = 68 1991
Zinc SS14 OnSite OB/OD mg/Kg = 61 1991gg
Zinc SS16 OnSite Habitat mg/Kg = 67 1991
Zinc SS17 OnSite Habitat mg/Kg = 55 1991
Zinc SS18 OnSite Habitat mg/Kg = 55 1991
Zinc SS19 OnSite Habitat mg/Kg = 51 1991
Zinc SS2 OnSite OB/OD mg/Kg = 34 1991
Zinc SS20 OnSite Habitat mg/Kg = 57 1991
Zinc SS3 OnSite OB/OD mg/Kg = 60 1991
Zinc SS4 OnSite OB/OD mg/Kg = 36 1991
Zinc SS5 OnSite OB/OD mg/Kg = 2300 1991
Zinc SS6 OnSite OB/OD mg/Kg = 130 1991
Zinc SS7 OnSite OB/OD mg/Kg = 490 1991
Zinc SS8 OnSite OB/OD mg/Kg = 63 1991
Zinc SS9 OnSite OB/OD mg/Kg = 240 1991
Zinc TTU-SS01S OnSite OB/OD mg/Kg = 60.7 1989
Zinc TTU-SS02S OnSite OB/OD mg/Kg = 88.7 1989
Zinc TTU-SS03S OnSite OB/OD mg/Kg = 59.7 1989
Zinc TTU-SS04S(D) OnSite OB/OD mg/Kg = 43.2 1989
Zinc TTU-SS05S OnSite OB/OD mg/Kg = 66.8 1989
Zinc TTU-SS06S(BG) OnSite Habitat mg/Kg = 48.3 1989
B - found in blank
J - estimated value
H - high, qualified result within acceptable range
L - low, qualified result within acceptable range
R - unusable
U - below detection
SLC JMS ES112005010SLC/HillAFB_TTU_06Oct05_CAI-unarmedv2_101405.xls/B-1 PAGE 49 OF 49
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1
Figure B-1.Example box plot diagram displaying a graphical
representation of underlying data distribution.
Se
d
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m
e
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t

C
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n
c
e
n
t
r
a
t
i
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(
u
g
/
k
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100
1000
10000
100000
31/36
Median
25th Percentile
75th Percentile
10th Percentile
90th Percentile
Outlier:
<10th Percentile
Outlier:
>90th Percentile
number detects/
number samples
Figure B-2.Comparison of distributions of on-site and background
concentrations of a) aluminum and b) antimony at the Thermal
Treatment Unit, Hill Air Force Base, Utah. On-site data includes
samples through 2004.
Location
So
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a
t
i
o
n

(
m
g
/
k
g
)
1000
10000
100000
On-site
54/54 48/48
Wilcoxon Rank Sum Test p-Value = 0.8751
2-Tailed; Not Significantly Different
Background
a) Aluminum
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.001
0.01
0.1
1
10
100
1000
On-siteBackground
22/2829/54
b) Antimony
Wilcoxon Rank Sum Test p-Value = 0.0156
2-Tailed; Site > Background
Figure B-3.Comparison of distributions of on-site and background
concentrations of a) arsenic and b) barium at the Thermal Treatment
Unit, Hill Air Force Base, Utah. On-site data includes samples through
2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
1
10
100
On-site
54/54 28/48
Wilcoxon Rank Sum Test p-Value = 0.0017
2-Tailed; Background > On-site
Background
a) Arsenic
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
100
1000
On-siteBackground
48/48
54/54
b) Barium
Wilcoxon Rank Sum Test p-Value = <0.0001
2-Tailed; Background > On-site
Figure B-4.Comparison of distributions of on-site and background
concentrations of a) beryllium and b) cadmium at the Thermal
Treatment Unit, Hill Air Force Base, Utah. On-site data includes
samples through 2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.001
0.01
0.1
1
10
On-site
48/54 23/48
Wilcoxon Rank Sum Test p-Value = 0.4427
2-Tailed; Not Significantly Different
Background
a) Beryllium
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.001
0.01
0.1
1
10
100
On-siteBackground
21/4835/54
b) Cadmium
Wilcoxon Rank Sum Test p-Value = <0.0001
2-Tailed; Site > Background
Figure B-5.Comparison of distributions of on-site and background
concentrations of a) chromium and b) cobalt at the Thermal Treatment
Unit, Hill Air Force Base, Utah. On-site data includes samples through
2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
1
10
100
On-site
54/54 48/48
Wilcoxon Rank Sum Test p-Value = 0.8253
2-Tailed; Not Significantly Different
Background
a) Chromium
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.1
1
10
On-siteBackground
22/2854/54
b) Cobalt
Wilcoxon Rank Sum Test p-Value = 0.0070
2-Tailed; Not Significantly Different
Figure B-6.Comparison of distributions of on-site and background
concentrations of a) copper and b) iron at the Thermal Treatment Unit,
Hill Air Force Base, Utah. On-site data includes samples through
2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.1
1
10
100
1000
10000
100000
On-site
54/54 41/48
Wilcoxon Rank Sum Test p-Value = <0.0001
2-Tailed; On-site > Background
Background
a) Copper
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
1000
10000
100000
On-siteBackground
42/4254/54
b) Iron
Wilcoxon Rank Sum Test p-Value = 0.4919
2-Tailed; Not Significantly Different
Figure B-7.Comparison of distributions of on-site and background
concentrations of a) lead and b) magnesium at the Thermal Treatment
Unit, Hill Air Force Base, Utah. On-site data includes samples through
2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.1
1
10
100
1000
10000
100000
On-site
54/54 40/48
Wilcoxon Rank Sum Test p-Value = 0.0017
2-Tailed; On-site > Background
Background
a) Lead
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
1e+3
1e+4
1e+5
1e+6
On-siteBackground
42/4254/54
b) Magnesium
Wilcoxon Rank Sum Test p-Value = <0.0001
2-Tailed; Background > On-site
Figure B-8.Comparison of distributions of on-site and background
concentrations of a) manganese and b) mercury at the Thermal
Treatment Unit, Hill Air Force Base, Utah. On-site data includes
samples through 2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
10
100
1000
On-site
54/54 48/48
Wilcoxon Rank Sum Test p-Value = 0.5409
2-Tailed; Not Significantly Different
Background
a) Manganese
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.001
0.01
0.1
On-siteBackground
13/482/4
b) Mercury
Wilcoxon Rank Sum Test p-Value = 0.9435
2-Tailed; Not Significantly Different
Figure B-9.Comparison of distributions of on-site and background
concentrations of a) molybdenum and b) nickel at the Thermal
Treatment Unit, Hill Air Force Base, Utah. On-site data includes
samples through 2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.01
0.1
1
10
100
On-site
53/54 20/22
Wilcoxon Rank Sum Test p-Value = 0.0025
2-Tailed; On-site > Background
Background
a) Molybdenum
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
1
10
100
On-siteBackground
48/4854/54
b) Nickel
Wilcoxon Rank Sum Test p-Value = 0.6932
2-Tailed; Not Significantly Different
Figure B-10.Comparison of distributions of on-site and background
concentrations of a) phosphorus and b) selenium at the Thermal
Treatment Unit, Hill Air Force Base, Utah. On-site data includes
samples through 2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
100
1000
10000
On-site
50/50 20/20
Wilcoxon Rank Sum Test p-Value = 0.1956
2-Tailed; Not Significantly Different
Background
a) Phosphorus
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.001
0.01
0.1
1
10
On-siteBackground
0/4838/54
b) Selenium
Wilcoxon Rank Sum Test p-Value = <0.0001
2-Tailed; On-site > Background
Figure B-11.Comparison of distributions of on-site and background
concentrations of a) silver and b) strontium at the Thermal Treatment
Unit, Hill Air Force Base, Utah. On-site data includes samples through
2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.001
0.01
0.1
1
10
On-site
25/54 4/48
Wilcoxon Rank Sum Test p-Value = <0.0001
2-Tailed; On-site > Background
Background
a) Silver
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
100
1000
10000
On-siteBackground
22/2254/54
b) Strontium
Wilcoxon Rank Sum Test p-Value = 0.0107
2-Tailed; Background > On-site
Figure B-12.Comparison of distributions of on-site and background
concentrations of a) thallium and b) vanadium at the Thermal
Treatment Unit, Hill Air Force Base, Utah. On-site data includes
samples through 2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
0.01
0.1
1
10
On-site
25/54 26/48
Wilcoxon Rank Sum Test p-Value = 0.1577
2-Tailed; Not Significantly Different
Background
a) Thallium
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
1
10
100
On-siteBackground
27/2754/54
b) Vanadium
Wilcoxon Rank Sum Test p-Value = <0.0001
2-Tailed; Background > On-site
Figure B-13.Comparison of distributions of on-site and background
concentrations of zinc at the Thermal Treatment Unit, Hill Air Force
Base, Utah. On-site data includes samples through 2004.
Location
So
i
l

C
o
n
c
e
n
t
r
a
t
i
o
n

(
m
g
/
k
g
)
1
10
100
1000
10000
On-site
54/54 48/48
Wilcoxon Rank Sum Test p-Value = <0.0001
2-Tailed; On-site > Background
Background

Appendix C

75 CEG/CEIE

FINAL
Utah Test and Training Range Thermal
Treatment Unit
2022 Ecological Risk Screen Evaluation
Contract No.: W9123822C0011
Prepared for:
Hill Air Force Base
75 CEG/CEIE
Environmental Branch
Civil Engineer Group
January 2023

6440 S. Millrock Dr.
Suite 300
Holladay, UT 84121
PPS0830221439SLC ES-1
Executive Summary
ES.0.0.1 Hill Air Force Base has been conducting open burn/open denotation operations at the Utah
Test and Training Range-North (U.S. Environmental Protection Agency Identification Number UT
0570090001) Thermal Treatment Unit (TTU) under a Resource Conservation and Recovery Act Part B
permit issued by the Utah Department of Environmental Quality. Section II.F.2 of the permit requires a
5-year evaluation of ecological risks.
ES.0.0.2 Data collected from soil in 2019 and 2021 were evaluated to determine if potential risks to
ecological receptors were consistent with the original 2005 evaluation (CH2M HILL, 2005) and any of the
subsequent updates completed in 2007, 2011, 2013, and 2018 (CH2M Hill, 2007, 2011, 2013, 2018), or if
new risks were present. Chemical concentrations detected in soil in 2019 and 2021 were compared to
the maximum detected concentrations from all previous sampling events to determine if additional
chemicals required evaluation. Nitroglycerin had higher maximum detected concentrations than
previously sampled and was retained for evaluation of potential risk to terrestrial receptors. The initial
screen used the maximum detected concentrations in soil and no observed effect concentrations/no
observed adverse effect levels to estimate potential toxicity to terrestrial plants, terrestrial
invertebrates, birds, or mammals. The initial screening and produced hazard quotients greater than 1 for
terrestrial invertebrates. Hazard quotients were less than 1 for terrestrial plants and mammals. Toxicity
reference values were not available for birds; however, studies indicate that nitroglycerin is not toxic to
birds under environmental conditions (Williams et al., 2015).
ES.0.0.3 Data from 2019 and 2021 were evaluated on a sample-by-sample basis for potential risks from
nitroglycerin to terrestrial invertebrates in the refined screen. Of the 14 samples collected (including 2
field duplicates), 1 sample showed nitroglycerin concentrations exceeding the no observed effect
concentration. However, there were no exceedances of the lowest observed effect concentration.
Potential risk to terrestrial invertebrates is considered low, especially given the active use of the site,
therefore nitroglycerin was not retained as a chemical of ecological concern.
ES.0.0.4 The overall conclusion of the evaluation of 2019 and 2021 data is that potential risks to
ecological receptors are within range of previously measured results and no analytes are retained as
chemicals of ecological concern.
PPS0830221439SLC ES-1
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PPS0830221439SLC i
Contents
Executive Summary ....................................................................................................................... ES-1
Acronyms and Abbreviations ............................................................................................................... i
1 General............................................................................................................................... 1-1
1.1 Evaluation of the Risk Assessments ................................................................................. 1-1
2 Approach ............................................................................................................................ 2-1
3 Results ................................................................................................................................ 3-1
3.1 Selection of Analytes for Additional Evaluation .............................................................. 3-1
3.2 Initial Screen .................................................................................................................... 3-1
3.3 Refined Screen ................................................................................................................. 3-2
4 Summary and Conclusions ................................................................................................... 4-1
5 References .......................................................................................................................... 5-1
Tables
Table 3-1. Comparison of New (2019-2021) and Historical (1989 through 2017) Analytical Results ....... 3-1
Table 3-2. Summary of Selection Criteria for Determination Whether to Revise Screening Evaluation
Using 2019–2021 Data .................................................................................................................. 3-4
Table 3-3. Ecological Screening Benchmarks for Terrestrial Plants Exposed to Soil.................................. 3-6
Table 3-4. Ecological Screening Benchmarks for Terrestrial Invertebrates Exposed to Soil ...................... 3-8
Table 3-5. Toxicity Reference Values for Birds ........................................................................................ 3-10
Table 3-6. Toxicity Reference Values for Mammals................................................................................. 3-12
Table 3-7. Chemical Uptake for Dietary Items ......................................................................................... 3-14
Table 3-8. Exposure Parameters for Selected Wildlife Receptors of Concern......................................... 3-16
Table 3-9. Risk Screening for Terrestrial Plants and Invertebrates .......................................................... 3 -18
Table 3-10. Risk Screening Evaluation for Birds and Mammals ............................................................... 3-20
Table 3-11. Point-by-Point Risk Estimation for Soil Invertebrates ........................................................... 3-22

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PPS0830221439SLC i
Acronyms and Abbreviations
-- not available
μg/L microgram(s) per liter
BAF bioaccumulation factor
CH2M HILL CH2M HILL, Inc.
COPEC chemical of potential ecological concern
det detects
DW dry weight
EPA U.S. Environmental Protection Agency
ERA ecological risk assessment
HMX cyclotetramethylene tetranitramine
HQ hazard quotient
LOAEL lowest observed adverse effect level
LOEC lowest observed effect concentration
kg kilogram(s)
kg/kg/d kilogram(s) per kilogram per day
mg/kg milligram(s) per kilogram
mg/kgbw-d milligram(s) per kilogram per body weight per day
mg/kg/d milligram(s) per kilogram per day
MIDAS Munitions Items Disposition Action System database
n number of samples
N/A not applicable
ND not detected
NOAEL no observed adverse effect level
NOEC no observed effect concentration
NSV no screening value available
PAH polynuclear aromatic hydrocarbon
RCRA Resource Conservation and Recovery Act
PETN pentaerythrite trinitromine
RDX cyclotrimethylene trinitromine
SLERA screening-level ecological risk assessment
SVOC semivolatile organic compound
TPH total petroleum hydrocarbon
TRV toxicity reference value
TTU Thermal Treatment Unit
UDEQ Utah Department of Environmental Quality
VOC volatile organic compound

ii PPS0830221439SLC

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SECTION 1
PPS0830221439SLC 1-1
General
1.0.0.1 Hill Air Force Base has been conducting open burn/open denotation operations at the Utah
Test and Training Range-North (U.S. Environmental Protection Agency [EPA] identification [ID] Number
UT 0570090001) Thermal Treatment Unit (TTU) under a Resource Conservation and Recovery Act Part B
permit issued by the Utah Department of Environmental Quality (UDEQ). Section II.F.2 of the permit
requires an evaluation of ecological risks every 5 years. A screening-level ecological risk assessment
(SLERA) was completed and submitted in 2005 (CH2M HILL, 2005) with subsequent evaluations in 2007,
2009, 2011, 2013, and 2018 (CH2M HILL, 2007, 2009, 2011, 2013, and 2018).
1.0.0.2 The risk assessment must be evaluated every 5 years with the biennial soil sampling data.
This SLERA was conducted using procedures outlined in the Ecological Risk Assessment Guidance for
Superfund: Process for Designing and Conducting Ecological Risk Assessments (EPA, 1997) and
incorporates site data collected in 2019 and 2021.
1.0.0.3 This evaluation of the completeness and accuracy of the Ecological Risk Assessment (ERA)
(Attachment 10A of the permit) has been prepared and is being submitted to UDEQ as required by
Condition II.F of the Resource Conservation and Recovery Act (RCRA) permit. This evaluation includes a
review of the chemicals in Attachment 10A (ecological risk) with respect to updates in the Munitions
Items Disposition Action System database (MIDAS) or other relevant emission data; a review of the
toxicity information in Attachment 10A; and any new or updated toxicity data. This 2022 evaluation
includes a review of the environmental sampling data acquired since the last evaluation and discusses
how the new data affect the risk assessments in Attachment 10A.
1.0.0.4 No new waste streams have been included in TTU operations since the 2013 risk assessment
evaluations were performed and waste streams such as small munitions and dunnage have been halted.
The burn pan used to treat those waste streams has been removed. Missile or rocket motors such as the
Polaris (A-3) and Antares IIB x-259 have been treated at the TTU and were addressed in the last
evaluation. These are not new waste streams and are consistent with the Hazard Class 1.1, double base
propellant (non-lead bearing) waste stream that comprises the majority of the TTU workload. It should
be noted that there are no more Polaris A-3 motors known to be in inventory or awaiting disposal.
1.1 Evaluation of the Risk Assessments
1.1.0.1 This evaluation of the completeness and accuracy of the ERA (Attachment 10A of the permit)
has been prepared and is being submitted to UDEQ as required by Condition II.F of the RCRA permit.
This evaluation includes a review of the chemicals in Attachment 10A (ecological risk) with respect to
updates in the MIDAS database or other relevant emission data; a review of the toxicity information in
Attachment 10A; and any new or updated toxicity data. This 2022 evaluation includes a review of the
environmental sampling data acquired since the last evaluation and discusses how the new data affect
the risk assessments in Attachment 10A.
1.1.0.2 The treatment of a single MOAB by OD on the TTU was reported as a new waste stream in the
2020 Waste Characterization Technical Memo. The MOAB weapon system can use either tritonal or H-6
explosive fill. While the MOAB weapon system is identified as a new waste stream since 2018, the
ingredients of both tritonal and H-6 explosives are included in the historic and current waste streams
treated at the TTU.
1.1.0.3 The conclusions of the 2005 SLERA (CH2M HILL) were that potential for risks from chemicals in
soil over the entire TTU site could not be excluded for zinc to plants; total petroleum hydrocarbons (TPH)
to plants and invertebrates; and cyclotetramethylene tetranitramine (HMX), antimony, cadmium, copper,
SECTION 1 – GENERAL
1-2 PPS0830221439SLC
lead, perchlorate, 2-methylnaphthalene, fluorene, total polynuclear aromatic hydrocarbons (PAHs), and
acetone to one or more wildlife receptors. Samples driving the potential for risks to receptors were
generally associated with open burning/open detonation areas and did not represent the potential for
risks in the surrounding wildlife habitat areas of the site due to incomplete exposure pathways.
1.1.0.4 One outcome of the 2005 SLERA was that soil samples would be collected at the conclusion of
disposal activities each year to monitor any changes in contaminant concentrations and distribution due
to TTU operations. Additional soil data have been collected annually starting in 2005 and analyzed for
energetics and metals. These additional data are evaluated relative to the previous onsite data and the
results of the 2005 and subsequent SLERAs to determine whether risk conclusions could potentially
change as a result of the new data. Because the most recent data (2005 to present) have been collected as
composite samples as opposed to discrete samples, they were not pooled with data from 2004 and earlier
(which were discrete samples). Rather, the post-2004 data were evaluated independently. Annual soil
sampling was conducted from 2004 to 2013 with biennial sampling conducted since 2013 (in 2015, 2017,
2019, and 2021). SLERA evaluations were conducted every 2 years from 2007 to 2013 and are now being
performed every 5 years.
1.1.0.5 The 2007 SLERA evaluation (based on 2005-2006 data) and the 2009 SLERA evaluation (based
on 2007-2008 data) concluded that cadmium, chromium, and vanadium in soil exceed the target hazard
quotient (HQ) of 1 for terrestrial plants, terrestrial invertebrates, or some small mammals. The 2011
SLERA evaluation (based on 2009 to 2010 data) concluded that mercury in soil exceeded the target HQ
of 1 for plants and invertebrates; however, none of these data are different from background (in the
case of chromium, mercury, and vanadium) or display only minimal levels of exceedance (cadmium). The
2013 SLERA evaluation (based on 2011 and 2012 data) concluded that RDX in soil exceeded target HQs
for mammals, but potential risks were driven by a single slightly elevated detect. The 2018 SLERA
evaluation (based on 2013, 2015, and 2017 data) concluded that perchlorate posed a limited risk to
terrestrial invertebrates, however, only one sample (2013) exceeded the previous site maximum.
In addition, a single sample from 2008 was analyzed for dioxin/dibenzofuran congeners. No exceedance of
the tetrachlorodibenzodioxin toxic equivalency quotient was observed for this sample for any receptor. It
should be noted that the sampling efforts conducted from 2013 to present focused on metals and
energetic compounds. The 2005 SLERA identified TPH, acetone, and PAHs in soil as potential risk drivers.
The absence of new data for these other analytes precludes any new conclusions; consequently, they are
still considered potential risk drivers.
The overall conclusion of the 2007, 2009, 2011, 2013 and 2018 SLERA evaluations is that calculated
ecological risk is not greater than that estimated previously for the TTU or is not considered to be
unacceptable.
1.1.0.6 Surface water was not evaluated in any of the earlier SLERAs (2005 through 2009). A heavy
rain event in August 2012 resulted in the accumulation of surface water runoff in one of the detonation
craters. The presence of surface water in the crater provided a complete exposure pathway for aquatic
organisms including aquatic plants (e.g., algae) and aquatic invertebrates (e.g., water boatman, water
skippers, snails, and insect nymphs) that may reside in standing water. Surface water may also provide a
complete exposure pathway for birds and mammals as a drinking water source. Surface water was
collected from the crater in 2012 and evaluated for potential risks in the 2013 SLERA. No accumulations
of surface water have been observed at the site since 2013. Therefore, surface water was not evaluated
in the 2018 SLERA or this 2022 SLERA.
1.1.0.7 This report summarizes the SLERA evaluation performed based on the newest data (2019 and
2021) from the TTU.

PPS0830221439SLC
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SECTION 2
PPS0830221439SLC 2-1
Approach
2.0.0.1 Rather than performing the SLERA anew for all analytes and receptors with the most recent
data collected (2019 and 2021), a multistep process was used to identify and evaluate potential risks for
data collected after the previous SLERA update. Four criteria were considered:
x Identification of analytes that require evaluation of potential risks to ecological receptors.
Comparison of maximum detected concentrations from 2019 and 2021 versus the maximum
site detection from all previous sampling events (2005 through 2017). Maximum detected
concentrations in the 2019 and 2021 data greater than those observed in the previous data
suggest the potential for a changed risk conclusion.
Analyte was retained as a potential risk driver during the original 2005 SLERA or any subsequent
SLERA updates.
x Comparison of 2019 and 2021 data to background concentrations (performed only for metals with
new maximum detected concentrations exceeding previous maximums):
Concentrations of inorganic analytes that are not statistically significantly different from
background concentrations generally indicate ambient levels and are not considered further in
the evaluation.
If 2019 and 2021 concentrations are not different from background, the likelihood that they
represent site-associated contamination and, thus, potential risk is low.
x Initial screen of analytes for potential risk for ecological receptors using maximum detected
concentrations and no observed effect concentrations (terrestrial plants and invertebrates) and no
observed adverse effect levels (birds and mammals).
All analytes judged to require further evaluation were screened using the methods previously
employed in the initial SLERA (CH2M HILL, 2005). Exposure and toxicity assumptions were
reviewed and updated as needed to ensure the SLERA used the most recent information.
If hazard quotients for the initial screen are below 1, potential risk to that receptor is considered
low and analyte is not retained for any further evaluation.
If hazard quotients in the initial screen exceed 1, potential risk for that receptor may exist and
analytes are retained for further evaluation in the refined screen.
x Refined screen of analytes with hazard quotients exceeding 1 under the initial screen.
Refined risk estimates for terrestrial plants or invertebrates are based on the sample-specific
results and the low observed ecological concentration.
Refined risk estimates for birds and mammals are based on the 95 percent upper confidence
level and the low observed adverse effect concentration.
2.0.0.2 Results for each step are evaluated to determine if there are any new risk drivers or if any
further evaluation is needed at this time.

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SECTION 3
PPS0830221439SLC 3-1
Results
3.1 Selection of Analytes for Additional Evaluation
3.1.0.1 Comparison of maximum detected concentrations for analytes evaluated in soil from 2019
and 2021 to the maximum detected concentrations of all previous years combined are presented in
Table 3-1. Nitroglycerin was the only analyte with a maximum detected concentration greater than the
site maximum from all previous sampling events.
3.1.0.2 A summary of risk drivers from each of the previous SLERA updates is presented in Table 3-2
along with the one analyte noted in the preceding section with greater maximum detects in 2019 and
2021 sampling events. Analytes requiring further evaluation were identified using the criteria outlined in
Section 2.
x Nitroglycerin – Retained for further evaluation in this 2018 SLERA update since maximum detected
concentrations are greater than previous data.
x Antimony, cadmium, chromium, copper, lead, vanadium, zinc, and perchlorate – Additional
evaluation of these analytes in this 2022 SLERA update was not warranted since the maximum
detected concentrations for 2019 and 2021 were below previously measured levels. These analytes
continue to be retained as risk drivers on the basis of their previous SLERA results.
x Mercury and RDX – Additional evaluation of these analytes in this 2022 SLERA update was not
warranted since the maximum detected concentrations for 2019 and 2021 were below previously
measured levels. These analytes were retained on the basis of their previous SLERA updates.
x Acetone, dioxins/dibenzofurans, 2-methylnaphthalene, fluorene, total PAHs, and TPHs – New data
were not collected during 2013 through 2017 sampling events. These analytes continue to be
retained as risk drivers on the basis of their previous SLERA results.
3.2 Initial Screen
3.2.0.1 Methods and parameters employed to perform the SLERAs submitted in
2005 (CH2M HILL, 2005), 2007 (CH2M HILL, 2007), 2009 (CH2M HILL, 2009), 2011 (CH2M HILL, 2011),
2013 (CH2M HILL, 2013), and 2018 (CH2M HILL, 2018) were applied to the 2019 and 2021 soils data.
Screening values for terrestrial plants, terrestrial invertebrates, birds, and mammals for the retained
analytes were reviewed and updated where new toxicity values were available from reputable sources.
Toxicity benchmarks and values are summarized in Tables 3-3 through 3-6. Bioaccumulation factors used
to estimate contaminant uptake into food items for birds and mammals are presented in Table 3-7.
Parameters for estimation of dietary exposures for birds and mammals are summarized in Table 3-8. The
initial screens for each receptor used the maximum detected concentrations of retained analytes,
uptake factors, and no observed effect concentrations (NOECs) or no observed adverse effect levels
(NOAELs) as summarized in the following sections.
3.2.0.2 Terrestrial Plants and Invertebrates. Initial risk screens for terrestrial plants and invertebrates
are presented in Table 3-9. The no observed effect concentration (NOEC) HQs for nitroglycerin exceeded
1 for terrestrial invertebrates and it was retained for further evaluation in the refined screen.
Nitroglycerin NOEC HQs were less than 1 for terrestrial plants and it was not retained for further
evaluation for this receptor group.
SECTION 3 – RESULTS
PPS0830221439SLC 3-2
3.2.0.3 Birds and Mammals. Initial screens for birds and mammals are presented in Table 3-10. Risk
estimates for birds and mammals include uptake from incidental ingestion of soil and ingestion of
dietary items (forage or prey) that may have accumulated chemicals of potential ecological concern
(COPECs) from soil. The no observed adverse effect level (NOAEL) HQs for mammals did not exceed 1 for
nitroglycerin. Toxicity reference values were not available for birds however, studies indicate that
nitroglycerin is not toxic to birds under environmental conditions (Williams et al., 2015).
3.3 Refined Screen
3.3.0.1 Methods and parameters employed to perform the SLERAs submitted in
2005 (CH2M HILL, 2005), 2007 (CH2M HILL, 2007), 2009 (CH2M HILL, 2009), 2011 (CH2M HILL, 2011),
2013 (CH2M HILL, 2013), and 2018 (CH2M HILL, 2018) were used to perform the refined screen.
Analyte/receptor combinations that were retained at the conclusion of the initial screen were evaluated
in the refined screen. For the 2019 and 2021 data, refinement was limited to nitroglycerin exposure to
terrestrial invertebrates. The refined evaluation for terrestrial invertebrates is a point-by-point
comparison of sample results against the NOEC and the lowest observed effect concentration (LOEC)
due to the limited mobility of this receptor group. Toxicity benchmarks for terrestrial invertebrates were
summarized in Table 3-4.
3.3.0.2 Terrestrial Invertebrates. The refined risk screen for terrestrial invertebrates potentially
exposed to nitroglycerin is presented in Table 3-11. Nitroglycerin was only detected in 3 of 14 samples of
which only 1 sample had concentrations exceeding the NOEC. None of the detected concentrations
exceeded the LOEC. Potential risks to terrestrial invertebrates are considered low. Nitroglycerin was not
retained as a chemical of ecological concern.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3-
1

TTable 3--11.. CCompparison of New (2019--22021) and Historical (11989 tthrough 2017) Analytical Results

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

Si
t
e

M
a
x
i
m
u
m

-

Al
l

Y
e
a
r
s

(1
9
8
9

t
h
r
o
u
g
h

2
0
1
7
)

2
0
1
9
-
2
0
2
1

D
a
t
a

Ne
w

M
a
x
i
m
u
m
>

Pr
e
v
i
o
u
s

S
i
t
e

Ma
x
i
m
u
m

(A
l
l

Y
e
a
r
s
)
?

An
a
l
y
t
e

T
y
p
e

A
n
a
l
y
t
e

U
n
i
t
s

Nu
m
b
e
r

o
f

De
t
e
c
t
s

Nu
m
b
e
r

o
f

Sa
m
p
l
e
s

Ma
x
i
m
u
m

De
t
e
c
t

So
i
l

Me
t
a
l
s

Al
u
m
i
n
u
m

mg
/
k
g

5
4
0
0
0

(
1
9
9
1
)

14

1
4

1
8
0
0
0

No

Me
t
a
l
s

An
t
i
m
o
n
y

mg
/
k
g

1
6
6
.
9
3

(
2
0
0
4
)

8
1
4

0
.
6
6

No

Me
t
a
l
s

Ar
s
e
n
i
c

mg
/
k
g

4
1
.
3

(
2
0
0
2
)

14

1
4

7

No

Me
t
a
l
s

Ba
r
i
u
m

mg
/
k
g

6
4
0

(
1
9
9
1
)

14

1
4

2
7
0

No

Me
t
a
l
s

Be
r
y
l
l
i
u
m

mg
/
k
g

0
.
9
8

(
2
0
0
7
)

14

1
4

0
.
7
3

No

Me
t
a
l
s

Ca
d
m
i
u
m

mg
/
k
g

3
2

(
1
9
9
1
)

14

1
4

0
.
6
7

No

Me
t
a
l
s

Ch
r
o
m
i
u
m

mg
/
k
g

1
0
0

(
2
0
0
5
)

14

1
4

1
5

No

Me
t
a
l
s

Co
b
a
l
t

mg
/
k
g

4
.
9

(
2
0
0
2
)

14

1
4

4
.
2

No

Me
t
a
l
s

Co
p
p
e
r

mg
/
k
g

1
8
0
0
0

(
1
9
9
1
)

14

1
4

1
8

No

Me
t
a
l
s

Ir
o
n

mg
/
k
g

1
5
0
0
0

(
2
0
0
4
)

14

1
4

1
3
0
0
0

No

Me
t
a
l
s

Le
a
d

mg
/
k
g

4
8
0
0
0

(
1
9
9
1
)

14

1
4

1
7

No

Me
t
a
l
s

Ma
n
g
a
n
e
s
e

mg
/
k
g

5
1
9

(
2
0
0
2
)

14

1
4

5
0
0

No

Me
t
a
l
s

Me
r
c
u
r
y

mg
/
k
g

0
.
4
6

(
2
0
0
9
)

10

1
4

0
.
0
1
5

No

Me
t
a
l
s

Mo
l
y
b
d
e
n
u
m

mg
/
k
g

5
6

(
2
0
0
7
)

14

1
4

2
.
8

No

Me
t
a
l
s

Ni
c
k
e
l

mg
/
k
g

4
1
.
3

(
2
0
0
4
)

14

1
4

1
2

No

Me
t
a
l
s

Ph
o
s
p
h
a
t
e

mg
/
k
g

1
.
8

(
2
0
0
7
)

N/
A

N
/
A

N
/
A

N/
A

Me
t
a
l
s

Se
l
e
n
i
u
m

mg
/
k
g

5

(
1
9
9
1
)

14

1
4

0
.
2
3

No

Me
t
a
l
s

Si
l
v
e
r

mg
/
k
g

4

(
1
9
8
9
)

14

1
4

0
.
2
3

No

Me
t
a
l
s

St
r
o
n
t
i
u
m

mg
/
k
g

6
5
0

(
2
0
1
1
)

14

1
4

4
2
0

No

Me
t
a
l
s

Th
a
l
l
i
u
m

mg
/
k
g

2
.
5

(
1
9
9
1
)

14

1
4

0
.
2
2

No

Me
t
a
l
s

Va
n
a
d
i
u
m

mg
/
k
g

2
8

(
2
0
0
5
)

14

1
4

2
4

No

Me
t
a
l
s

Zi
n
c

mg
/
k
g

2
3
0
0

(
1
9
9
1
)

14

1
4

4
8

No

In
o
r
g
a
n
i
c

Pe
r
c
h
l
o
r
a
t
e

mg
/
k
g

8
1

(
2
0
1
3
)

13

1
4

9
.
6

No

En
e
r
g
e
t
i
c

1,
3
,
5
-
T
r
i
n
i
t
r
o
b
e
n
z
e
n
e

mg
/
k
g

0
.
2

(
2
0
0
5
R
A
)

0
1
4

<
0
.
0
1
4

No

En
e
r
g
e
t
i
c

1,
3
-
D
i
n
i
t
r
o
b
e
n
z
e
n
e

mg
/
k
g

N
o

D
e
t
e
c
t
i
o
n
s

(
0
.
2

u
s
e
d
)

0
1
4

<
0
.
0
1
7

No

En
e
r
g
e
t
i
c

2,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

mg
/
k
g

2
.
2

(
2
0
1
3
)

0
1
4

<
0
.
0
3
1

No

En
e
r
g
e
t
i
c

2,
4
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

mg
/
k
g

1
0
.
5

(
1
9
8
9
)

3
1
4

0
.
7
6

No

En
e
r
g
e
t
i
c

2,
6
-
D
i
n
i
t
r
o
t
o
l
u
e
n
e

mg
/
k
g

1
0
.
5

(
1
9
8
9
)

1
1
4

0
.
0
1
9

No

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3-
2

TTable 3--11.. CCompparison of New (2019--22021) and Historical (11989 tthrough 2017) Analytical Results

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

Si
t
e

M
a
x
i
m
u
m

-

Al
l

Y
e
a
r
s

(1
9
8
9

t
h
r
o
u
g
h

2
0
1
7
)

2
0
1
9
-
2
0
2
1

D
a
t
a

Ne
w

M
a
x
i
m
u
m
>

Pr
e
v
i
o
u
s

S
i
t
e

Ma
x
i
m
u
m

(A
l
l

Y
e
a
r
s
)
?

An
a
l
y
t
e

T
y
p
e

A
n
a
l
y
t
e

U
n
i
t
s

Nu
m
b
e
r

o
f

De
t
e
c
t
s

Nu
m
b
e
r

o
f

Sa
m
p
l
e
s

Ma
x
i
m
u
m

De
t
e
c
t

En
e
r
g
e
t
i
c

2-
A
m
i
n
o
-
4
,
6
-
d
i
n
i
t
r
o
t
o
l
u
e
n
e

mg
/
k
g

1
.
5

(
1
9
9
1
)

0
1
4

<
0
.
0
3
3

No

En
e
r
g
e
t
i
c

2-
N
i
t
r
o
t
o
l
u
e
n
e

mg
/
k
g

0
.
2

(
0
.
5
x
N
D
,

2
0
0
5
R
A
)

0
1
4

<
0
.
0
4
7

No

En
e
r
g
e
t
i
c

3-
N
i
t
r
o
t
o
l
u
e
n
e

mg
/
k
g

0
.
2

(
0
.
5
x
N
D
,
1
9
8
9
)

0
1
4

<
0
.
0
6
4

No

En
e
r
g
e
t
i
c

4-
A
m
i
n
o
-
2
,
6
-
d
i
n
i
t
r
o
t
o
l
u
e
n
e

mg
/
k
g

0
.
2

(
2
0
1
2
)

0
7

<
0
.
0
3

No

En
e
r
g
e
t
i
c

4-
N
i
t
r
o
t
o
l
u
e
n
e

mg
/
k
g

0
.
2

(
0
.
5
x
N
D
,

1
9
8
9
)

0
7

<
0
.
0
3
7

No

En
e
r
g
e
t
i
c

HM
X

mg
/
k
g

2
5

(
1
9
9
1
)

4
1
4

1
.
1

No

En
e
r
g
e
t
i
c

Ni
t
r
o
b
e
n
z
e
n
e

mg
/
k
g

1
0
.
5

(
1
9
8
9
)

0
1
4

<
0
.
0
8
5

No

En
e
r
g
e
t
i
c

Ni
t
r
o
g
l
y
c
e
r
i
n

mg
/
k
g

6.
6

(
2
0
0
8
)

3
1
4

15

Ye
s

En
e
r
g
e
t
i
c

Ni
t
r
o
g
u
a
n
i
d
i
n
e

mg
/
k
g

0
.
3

(
1
9
9
1
)

(
0
.
5

u
s
e
d
)

0
1
4

<
0
.
0
2

No

En
e
r
g
e
t
i
c

PE
T
N

mg
/
k
g

N
o

D
e
t
e
c
t
i
o
n
s

(
0
.
6
5

u
s
e
d
)

0
1
4

<
0
.
4
9

No

En
e
r
g
e
t
i
c

Pi
c
r
i
c

A
c
i
d

mg
/
k
g

0
.
5

(
1
9
9
1
)

0
1
4

<
0
.
0
5
6

No

En
e
r
g
e
t
i
c

RD
X

mg
/
k
g

1
2

(
2
0
1
2
)

1
1
4

0
.
0
5
2

No

En
e
r
g
e
t
i
c

Te
t
r
y
l

mg
/
k
g

N
o

D
e
t
e
c
t
i
o
n
s

(
1
.
2

u
s
e
d
)

0
1
4

<
0
.
0
4
4

No

No
t
e
s
:

μg/
L

=

m
i
c
r
o
g
r
a
m
(
s
)

p
e
r

l
i
t
e
r

HM
X

=

c
y
d
o
t
e
t
r
a
m
e
t
h
y
l
e
n
e
t
e
t
r
a
n
i
t
r
a
m
i
n
e

N/
A

=

n
o
t

a
p
p
l
i
c
a
b
l
e
,

n
o

n
e
w

d
a
t
a

t
o

c
o
m
p
a
r
e

PA
H

=

p
o
l
y
n
u
c
l
e
a
r

a
r
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n

PE
T
N

=

p
e
n
t
a
e
r
y
t
h
r
i
t
e

t
r
i
n
i
t
r
o
m
i
n
e

RD
X

=

c
y
c
l
o
t
r
i
m
e
t
y
l
e
n
e

t
r
i
n
i
t
r
o
m
i
n
e

20
0
5
R
A
=
2
0
0
5

R
i
s
k

A
s
s
e
s
s
m
e
n
t

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
4

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

TTable 3--22. SSummary of Selection Criteria for Determination Whether to Revise Screening Evaluation Using 2019––22021 Data

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

20
1
9
-
2
0
2
1

D
a
t
a

S
u
m
m
a
r
y

An
a
l
y
t
e

Gr
o
u
p

Ch
e
m
i
c
a
l

o
f

P
o
t
e
n
t
i
a
l

Ec
o
l
o
g
i
c
a
l

C
o
n
c
e
r
n
a
An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
0
5

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
0
7

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
0
9

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
1
1

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
1
3

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
1
8

ER
A
?

20
1
3
–
2
0
1
7

D
a
t
a

Co
n
t
a
i
n

N
e
w

Ma
x
i
m
u
m

Co
n
c
e
n
t
r
a
t
i
o
n
?

Up
d
a
t
e

E
c
o
l
o
g
i
c
a
l

Ri
s
k

S
c
r
e
e
n
?

R
a
t
i
o
n
a
l
e

So
i
l

Ge
n
C
h
e
m

S
u
l
f
a
t
e

N
o

N
o

N
o

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

In
o
r
g
a
n
i
c

P
e
r
c
h
l
o
r
a
t
e

Y
e
s
—
W
i
l
d
l
i
f
e

N
o

N
o

N
o

N
o

Y
e
s
—

S
o
i
l

I
n
v
e
r
t
s
N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

Me
t
a
l
s

A
n
t
i
m
o
n
y

Y
e
s
—
W
i
l
d
l
i
f
e

N
o

N
o

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

Me
t
a
l
s

C
a
d
m
i
u
m

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s—
W
i
l
d
l
i
f
e

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

Me
t
a
l
s

C
h
r
o
m
i
u
m

N
o

Y
e
s
—
P
l
a
n
t
s

a
n
d

S
o
i
l

In
v
e
r
t
s

Ye
s
—
P
l
a
n
t
s

a
n
d

So
i
l

I
n
v
e
r
t
s

No

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

Me
t
a
l
s

C
o
p
p
e
r

Y
e
s
—
W
i
l
d
l
i
f
e

N
o

N
o

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

Me
t
a
l
s

L
e
a
d

Y
e
s
—
W
i
l
d
l
i
f
e

N
o

N
o

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

Me
t
a
l
s

M
e
r
c
u
r
y

N
o

N
o

N
o

Y
e
s
—
P
l
a
n
t
s

a
n
d

So
i
l

I
n
v
e
r
t
s

No

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

Me
t
a
l
s

V
a
n
a
d
i
u
m

N
o

Y
e
s
—
P
l
a
n
t
s

Y
e
s
—
P
l
a
n
t
s

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

Me
t
a
l
s

Z
i
n
c

Y
e
s
—
P
l
a
n
t
s

o
n
l
y

N
o

N
o

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

En
e
r
g
e
t
i
c

2
,
4
,
6
-
T
r
i
n
i
t
r
o
t
o
l
u
e
n
e

N
o

N
o

N
o

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

En
e
r
g
e
t
i
c

H
M
X

Y
e
s
—
W
i
l
d
l
i
f
e

N
o

N
o

N
o

N
o

N
o

N
o

N
o

2
0
1
9
–
2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

N
o

N
o

N
o

N
o

N
o

N
o

Ye
s

Ye
s

20
1
9
–
2
0
2
1

d
a
t
a

c
o
n
t
a
i
n

n
e
w

m
a
x
i
m
u
m

c
o
n
c
e
n
t
r
a
t
i
o
n
;

hi
g
h
e
r

m
a
x
i
m
u
m

m
a
y

i
n
d
i
c
a
t
e

i
n
c
r
e
a
s
e
d

r
i
s
k

e
s
t
i
m
a
t
e
s

an
d

t
h
e
r
e
f
o
r
e

r
e
q
u
i
r
e
s

e
v
a
l
u
a
t
i
o
n

En
e
r
g
e
t
i
c

R
D
X

N
o

N
o

N
o

N
o

Y
e
s
—
W
i
l
d
l
i
f
e

N
o

N
o

N
o

2
0
1
9
–2
0
2
1

d
a
t
a

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
i
n
g

d
a
t
a
;

n
o

c
h
a
n
g
e

to

c
o
n
c
l
u
s
i
o
n
s
.

PA
H

2
-
M
e
t
h
y
l

N
a
p
h
t
h
a
l
e
n
e

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

N/
A

N
/
A

N
o

N
o

N
/
A

N
o

n
e
w

d
a
t
a
;

i
n
i
t
i
a
l

c
o
n
c
l
u
s
i
o
n
s

a
r
e

u
n
c
h
a
n
g
e
d.

PA
H

F
l
u
o
r
e
n
e

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

N
/
A

N
/
A
N
o

N
o

N
/
A

N
o

n
e
w

d
a
t
a
;

i
n
i
t
i
a
l

c
o
n
c
l
u
s
i
o
n
s

a
r
e

u
n
c
h
a
n
g
e
d
.

PA
H

T
o
t
a
l

P
A
H

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

N
/
A

N
/
A
N
o

N
o

N
/
A

N
o

n
e
w

d
a
t
a
;

i
n
i
t
i
a
l

c
o
n
c
l
u
s
i
o
n
s

a
r
e

u
n
c
h
a
n
g
e
d
.

TP
H

T
P
H

Y
e
s
—
P
l
a
n
t
s

a
n
d

Wi
l
d
l
i
f
e

Ye
s
—
P
l
a
n
t
s

a
n
d

Wi
l
d
l
i
f
e

Ye
s
—
P
l
a
n
t
s

a
n
d

Wi
l
d
l
i
f
e

N/
A

N
/
A

N
o

N
o

N
/
A

N
o

n
e
w

d
a
t
a
;

i
n
i
t
i
a
l

c
o
n
c
l
u
s
i
o
n
s

a
r
e

u
n
c
h
a
n
g
e
d
.

VO
C

A
c
e
t
o
n
e

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

Y
e
s
—
W
i
l
d
l
i
f
e

N
/
A

N
/
A

No

N
o

N
/
A

N
o

n
e
w

d
a
t
a
;

i
n
i
t
i
a
l

c
o
n
c
l
u
s
i
o
n
s

a
r
e

u
n
c
h
a
n
g
e
d
.

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3-
5

TTable 3--22. SSummary of Selection Criteria for Determination Whether to Revise Screening Evaluation Using 2019––22021 Data

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

20
1
9
-
2
0
2
1

D
a
t
a

S
u
m
m
a
r
y

An
a
l
y
t
e

Gr
o
u
p

Ch
e
m
i
c
a
l

o
f

P
o
t
e
n
t
i
a
l

Ec
o
l
o
g
i
c
a
l

C
o
n
c
e
r
n
a
An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
0
5

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
0
7

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
0
9

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
1
1

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
1
3

ER
A
?

An
a
l
y
t
e

w
a
s

Re
t
a
i
n
e
d

i
n

2
0
1
8

ER
A
?

20
1
3
–
2
0
1
7

D
a
t
a

Co
n
t
a
i
n

N
e
w

Ma
x
i
m
u
m

Co
n
c
e
n
t
r
a
t
i
o
n
?

Up
d
a
t
e

E
c
o
l
o
g
i
c
a
l

Ri
s
k

S
c
r
e
e
n
?

R
a
t
i
o
n
a
l
e

No
t
e
s
:

a
Ch
e
m
i
c
a
l
s

o
f

p
o
t
e
n
t
i
a
l

e
c
o
l
o
g
i
c
a
l

c
o
n
c
e
r
n

(
C
O
P
E
C
s
)

a
r
e

t
h
o
s
e

a
n
a
l
y
t
es

t
h
a
t

w
e
r
e

r
e
t
a
i
n
e
d

f
o
r

f
u
r
t
he
r

e
v
a
l
u
a
t
i
o
n

i
n

h
i
s
t
o
r
i
c

S
L
E
RA
s

o
r

f
o
r

w
h
i
c
h

a

n
e
w

m
a
x
i
m
u
m

d
e
t
e
c
t

h
a
s

b
e
e
n

m
e
a
s
u
r
e
d
.

A
l
l

o
t
h
e
r

d
e
t
e
c
t
e
d

a
n
a
l
y
t
e
s

a
r
e

c
o
n
s
i
d
e
r
e
d

t
o

b
e

w
i
t
h
i
n

r
a
n
g
e

o
f

e
x
i
s
t
in
g

d
a
t
a

a
n
d

d
o

n
o
t

r
e
q
u
i
r
e
d

a
d
d
i
t
i
o
n
a
l

ev
a
l
u
a
t
i
o
n
.

ER
A

=

e
c
o
l
o
g
i
c
a
l

r
i
s
k

a
s
s
e
s
s
m
e
n
t

CO
P
E
C

=

c
h
e
m
i
c
a
l

o
f

p
o
t
e
n
t
i
a
l

e
c
o
l
o
g
i
c
a
l

c
o
n
c
e
r
n

HM
X

=

c
y
c
l
o
t
e
t
r
a
m
e
t
h
y
l
e
n
e
t
e
t
r
a
n
i
t
r
a
m
i
n
e

N/
A

=

n
o
t

a
p
p
l
i
c
a
b
l
e

PA
H

=

p
o
l
y
n
u
c
l
e
a
r

a
r
o
m
a
t
i
c

h
y
d
r
o
c
a
r
b
o
n

RD
X

=

c
y
c
l
o
t
r
i
m
e
t
h
y
l
e
n
e

t
r
i
n
i
t
r
o
m
i
n
e

TP
H

=

t
o
t
a
l

p
e
t
r
o
l
e
u
m

h
y
d
r
o
c
a
r
b
o
n

VO
C

=

v
o
l
a
t
i
l
e

o
r
g
a
n
i
c

c
o
m
p
o
u
n
d

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
6

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

TTable 3--33. EEcological Screening Benchmarks for Terrestrial Plants Exposed to Soil
Th
e
r
m
a
l

T
r
e
a
t
m
e
n
t

U
n
i
t

2
0
2
2

E
c
o
l
o
g
i
c
a
l

R
i
s
k

S
c
r
e
e
n
i
n
g

E
v
a
l
u
a
t
i
o
n

No

E
f
f
e
c
t

B
e
n
c
h
m
a
r
k

Lo
w

E
f
f
e
c
t

B
e
n
c
h
m
a
r
k

Ch
e
m
i
c
a
l

Gr
o
u
p

C
O
P
E
C

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e

Un
c
e
r
t
a
i
n
t
y

Fa
c
t
o
r
a
No
r
m
a
l
i
z
e
d

NO
E
C

(m
g
/
k
g
)

Un
c
e
r
t
a
i
n
t
y

Fa
c
t
o
r
b
No
r
m
a
l
i
z
e
d

L
O
E
C

(m
g
/
k
g
)

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

N
/
A

L
A
N
L
,

2
0
2
0

1

2
1

1

2
1
0

No
t
e
s
:

LO
E
C

=

l
o
w
e
s
t

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n

mg
/
k
g

=

m
i
l
l
i
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

N
/
A

=

n
o
t

a
p
p
l
i
c
a
b
l
e

NO
E
C

=

n
o

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n

NS
V

=

n
o

s
c
r
e
e
n
i
n
g

v
a
l
u
e

a
v
a
i
l
a
b
l
e

Un
c
e
r
t
a
i
n
t
y

f
a
c
t
o
r
s

w
e
r
e

a
p
p
l
i
e
d

a
s

f
o
l
l
o
w
s
:

a
Co
n
v
e
r
s
i
o
n

t
o

c
h
r
o
n
i
c

N
O
E
C

LO
E
C

t
o

N
O
E
C

=

0
.
1

Su
b
c
h
r
o
n
i
c

t
o

c
h
r
o
n
i
c

=

0
.
1

EC
5
0

t
o

c
h
r
o
n
i
c

=

0
.
0
1

Ac
u
t
e

t
o

c
h
r
o
n
i
c

=

0
.
0
1

b
Co
n
v
e
r
s
i
o
n

t
o

c
h
r
o
n
i
c

L
O
E
C

Su
b
c
h
r
o
n
i
c

t
o

c
h
r
o
n
i
c

=

0
.
1

EC
5
0

t
o

c
h
r
o
n
i
c

=

0
.
1

Ac
u
t
e

t
o

c
h
r
o
n
i
c

=

0
.
1

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
8

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

TTable 3--44. EEcological SScreening Benchmarks for Terrestrial Invertebrates Exposed to Soil

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

No

E
f
f
e
c
t

B
e
n
c
h
m
a
r
k

Lo
w

E
f
f
e
c
t

B
e
n
c
h
m
a
r
k

Ch
e
m
i
c
a
l

Gr
o
u
p

C
O
P
E
C

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e

Un
c
e
r
t
a
i
n
t
y

Fa
c
t
o
r
a
No
r
m
a
l
i
z
e
d

NO
E
C

(m
g
/
k
g
)

Un
c
e
r
t
a
i
n
t
y

Fa
c
t
o
r
b
No
r
m
a
l
i
z
e
d

L
O
E
C

(m
g
/
k
g
)

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

N
/
A

L
A
N
L
,

2
0
2
0

1

1
3

1

1
3
0

No
t
e
s
:

LO
E
C

=

l
o
w
e
s
t

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n

mg
/
k
g

=

m
i
l
l
i
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

N/
A

=

n
o
t

a
p
p
l
i
c
a
b
l
e

NO
E
C

=

n
o

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n

NS
V

=

n
o

s
c
r
e
e
n
i
n
g

v
a
l
u
e

a
v
a
i
l
a
b
l
e

Un
c
e
r
t
a
i
n
t
y

f
a
c
t
o
r
s

w
e
r
e

a
p
p
l
i
e
d

a
s

f
o
l
l
o
w
s
:

a
Co
n
v
e
r
s
i
o
n

t
o

c
h
r
o
n
i
c

N
O
E
C

LO
E
C

t
o

N
O
E
C

=

0
.
1

Su
b
c
h
r
o
n
i
c

t
o

c
h
r
o
n
i
c

=

0
.
1

EC
5
0

t
o

c
h
r
o
n
i
c

=

0
.
0
1

Ac
u
t
e

t
o

c
h
r
o
n
i
c

=

0
.
0
1

b
Co
n
v
e
r
s
i
o
n

t
o

c
h
r
o
n
i
c

L
O
E
C

Su
b
c
h
r
o
n
i
c

t
o

c
h
r
o
n
i
c

=

0
.
1

EC
5
0

t
o

c
h
r
o
n
i
c

=

0
.
1

Ac
u
t
e

t
o

c
h
r
o
n
i
c

=

0
.
1

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
9

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
1
0

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

TTable 3--55. TToxicity RReference Values for Birds

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

No

E
f
f
e
c
t

T
R
V
a

L
o
w

E
f
f
e
c
t

T
R
V
a
Ch
e
m
i
c
a
l

Gr
o
u
p

C
O
P
E
C

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e

Un
c
e
r
t
a
i
n
t
y

Fa
c
t
o
r
b
No
r
m
a
l
i
z
e
d

NO
A
E
L

TR
V

(m
g
/
k
g
b
w
-
d
)

Un
c
e
r
t
a
i
n
t
y

Fa
c
t
o
r
b
No
r
m
a
l
i
z
e
d

LO
A
E
L

T
R
V

(m
g
/
k
g
b
w
-
d
)

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

-
-

-
-

-
-

N
S
V

-
-

N
S
V

No
t
e
s
:

--

=

n
o
t

a
v
a
i
l
a
b
l
e

LO
A
E
L

=

l
o
w
e
s
t

o
b
s
e
r
v
e
d

a
d
v
e
r
s
e

e
f
f
e
c
t

l
e
v
e
l

mg
/
k
g
b
w
-
d

=

m
i
l
l
i
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

p
e
r

b
o
d
y

w
e
i
g
h
t

p
e
r

d
a
y

N/
A

=

n
o
t

a
p
p
l
i
c
a
b
l
e

NO
A
E
L

=

n
o

o
b
s
e
r
v
e
d

a
d
v
e
r
s
e

e
f
f
e
c
t

l
e
v
e
l

NS
V

=

n
o

s
c
r
e
e
n
i
n
g

v
a
l
u
e

a
v
a
i
l
a
b
l
e

TR
V

=

t
o
x
i
c
i
t
y

r
e
f
e
r
e
n
c
e

v
a
l
u
e

Se
l
e
c
t
i
o
n

o
f

T
R
V
s

a
n
d

a
p
p
l
i
c
a
t
i
o
n

o
f

u
n
c
e
r
t
a
i
n
t
y

f
a
c
t
o
r
s

w
a
s

p
e
r
f
o
r
m
e
d

i
n

a
c
c
o
r
d
a
n
c
e

w
i
t
h

E
P
A

(
1
9
9
7
)

a
s

d
e
s
c
r
i
b
e
d

i
n

f
o
o
t
n
o
t
e
s

2
a
n
d

3
.

a
Th
e

f
o
l
l
o
w
i
n
g

p
r
e
f
e
r
e
n
c
e
s

w
e
r
e

u
s
e
d

w
h
e
n

s
e
l
e
c
t
i
n
g

s
t
u
d
i
e
s
:

NO
A
E
L

e
n
d
p
o
i
n
t
s

w
e
r
e

g
i
v
e
n

p
r
e
f
e
r
e
n
c
e

o
v
e
r

L
O
A
E
L

e
n
d
p
o
i
n
t
s

w
h
e
n

b
o
t
h

w
e
r
e

a
v
a
i
l
a
b
l
e
.

S
t
u
d
i
e
s

w
i
t
h

L
D
5
0
s

a
s

e
n
d
p
o
i
n
t
s

w
e
r
e

o
n
l
y

se
l
e
c
t
e
d

w
h
e
n

s
t
u
d
i
e
s

f
o
r

s
u
b
l
e
t
h
a
l

e
f
f
e
c
t
s

we
r
e

n
o
t

a
v
a
i
l
a
b
l
e
.

C
h
r
o
n
i
c

s
t
u
d
i
e
s

w
e
r
e

s
e
l
e
c
t
e
d

o
v
e
r

s
u
b
c
h
r
o
n
i
c

s
t
u
d
i
e
s
,

a
n
d

s
u
b
c
h
r
o
n
i
c

s
t
u
d
i
e
s

w
e
r
e

s
e
l
e
c
t
e
d

o
v
e
r

a
c
u
t
e

s
t
u
d
ie
s

w
h
e
n

m
u
l
t
i
p
l
e

s
t
u
d
i
e
s

o
f

v
a
r
y
i
n
g

d
u
r
a
t
i
o
n

w
e
r
e

av
a
i
l
a
b
l
e

f
o
r

s
e
l
e
c
t
i
o
n
.

S
t
u
d
i
e
s

w
i
t
h

r
e
p
r
o
d
u
c
t
i
o
n

a
s

t
h
e

e
n
d
p
o
i
n
t

w
e
r
e

s
e
l
e
c
t
e
d

b
e
f
o
r
e

s
t
u
d
i
e
s

w
i
t
h

m
o
r
t
a
l
i
t
y

a
s

t
h
e

e
n
d
p
o
i
n
t
,
w
h
i
c
h

w
e
r
e

s
e
l
e
c
t
e
d

b
e
f
o
r
e

s
t
u
d
i
e
s

w
i
t
h

g
r
o
w
t
h

a
s

t
h
e

en
d
p
o
i
n
t
,

w
h
i
c
h

w
e
r
e

s
e
l
e
c
t
e
d

b
e
f
o
r
e

s
t
u
d
i
e
s

w
i
t
h

s
y
s
t
e
m
i
c

e
f
f
e
c
t
s

a
s

t
h
e

e
n
d
p
o
i
n
t
.

S
t
u
d
i
e
s

w
i
t
h

t
h
e

m
o
s
t

c
o
m
p
l
e
t
e

i
n
f
o
r
m
a
t
i
o
n

an
d

t
h
e
r
e
f
o
r
e

t
h
e

l
e
a
s
t

r
e
s
u
l
t
i
n
g

u
n
c
e
r
t
a
i
n
t
y

w
e
r
e

gi
v
e
n

p
r
e
f
e
r
e
n
c
e

i
n

s
t
u
d
y

s
e
l
e
c
t
i
o
n
.

S
t
u
d
i
e
s

f
r
o
m

s
u
r
r
o
g
a
t
e

c
h
e
m
i
c
a
l
s

w
e
r
e

o
n
l
y

s
e
l
e
c
t
e
d

w
h
e
n

n
o

o
t
h
e
r

s
t
u
d
y

f
o
r

a

p
a
r
t
i
c
u
l
a
r

c
on
t
a
m
i
n
a
n
t

o
f

p
o
t
e
n
t
i
a
l

e
c
o
l
o
g
i
c
a
l

c
o
n
c
e
r
n

w
a
s

f
o
u
n
d
.

b
Un
c
e
r
t
a
i
n
t
y

f
a
c
t
o
r
s

w
e
r
e

u
s
e
d

t
o

a
d
j
u
s
t

a
l
l

m
e
a
s
u
r
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
s

t
o

c
h
r
o
n
i
c

N
O
A
E
L
S

a
n
d

c
h
r
o
n
i
c

L
O
A
E
L
s

a
s

f
o
l
l
o
w
s
:

NO
A
E
L

t
o

L
O
A
E
L

=

0
.
1

Su
b
c
h
r
o
n
i
c

t
o

c
h
r
o
n
i
c

=

0
.
1

LD
5
0

t
o

c
h
r
o
n
i
c

=

0
.
0
1

Su
b
a
c
u
t
e

t
o

c
h
r
o
n
i
c

=

0
.
0
1

Ac
u
t
e

t
o

c
h
r
o
n
i
c

=

0
.
0
1

wh
e
r
e
:

Ch
r
o
n
i
c

=

>
1
2

w
e
e
k
s

o
r

d
u
r
i
n
g

c
r
i
t
i
c
a
l

l
i
f
e
s
t
a
g
e

Su
b
c
h
r
o
n
i
c

=

4
–
1
2

w
e
e
k
s

Su
b
a
c
u
t
e

=

<
4

w
e
e
k
s
,

m
u
l
t
i
p
l
e

d
o
s
e
s

Ac
u
t
e

=

o
n
l
y

o
n
e

d
o
s
e

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
1
1

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
1
2

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

TTable 3--66. TToxicity Reference Values for Mammals

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

No

E
f
f
e
c
t

T
R
V
a

L
o
w

E
f
f
e
c
t

T
R
V
a
Ch
e
m
i
c
a
l

Gr
o
u
p

C
O
P
E
C

S
u
r
r
o
g
a
t
e

R
e
f
e
r
e
n
c
e

Un
c
e
r
t
a
i
n
t
y

Fa
c
t
o
r
b
No
r
m
a
l
i
z
e
d

NO
A
E
L

T
R
V

(m
g
/
k
g
b
w
-
d
)

Un
c
e
r
t
a
i
n
t
y

Fa
c
t
o
r
b
No
r
m
a
l
i
z
e
d

LO
A
E
L

T
R
V

(m
g
/
k
g
b
w
-
d
)

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

N
/
A

L
A
N
L
,

2
0
2
0

1

9
6
.
4

1

1
0
2
0

No
t
e
s
:

LO
A
E
L

=

l
o
w
e
s
t

o
b
s
e
r
v
e
d

a
d
v
e
r
s
e

e
f
f
e
c
t

l
e
v
e
l

mg
/
k
g
b
w
-
d

=

m
i
l
l
i
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

p
e
r

b
o
d
y

w
e
i
g
h
t

p
e
r

d
a
y

N/
A

=

n
o
t

a
p
p
l
i
c
a
b
l
e

NO
A
E
L

=

n
o

o
b
s
e
r
v
e
d

a
d
v
e
r
s
e

e
f
f
e
c
t

l
e
v
e
l

NS
V

=

n
o

s
c
r
e
e
n
i
n
g

v
a
l
u
e

a
v
a
i
l
a
b
l
e

TR
V

=

t
o
x
i
c
i
t
y

r
e
f
e
r
e
n
c
e

v
a
l
u
e

Se
l
e
c
t
i
o
n

o
f

T
R
V
s

a
n
d

a
p
p
l
i
c
a
t
i
o
n

o
f

u
n
c
e
r
t
a
i
n
t
y

f
a
c
t
o
r
s

w
a
s

p
e
r
f
o
r
m
e
d

i
n

a
c
c
o
r
d
a
n
c
e

w
i
t
h

E
P
A

(
1
9
9
7
)

a
s

d
e
s
c
r
i
b
e
d

i
n

f
o
o
t
n
o
t
e
s

2
a
n
d

3
.

a
Th
e

f
o
l
l
o
w
i
n
g

p
r
e
f
e
r
e
n
c
e
s

w
e
r
e

u
s
e
d

w
h
e
n

s
e
l
e
c
t
i
n
g

s
t
u
d
i
e
s
:

NO
A
E
L

e
n
d
p
o
i
n
t
s

w
e
r
e

g
i
v
e
n

p
r
e
f
e
r
e
n
c
e

o
v
e
r

L
O
A
E
L

e
n
d
p
o
i
n
t
s

w
h
e
n

b
o
t
h

w
e
r
e

a
v
a
i
l
a
b
l
e
.

S
t
u
d
i
e
s

w
i
t
h

L
D
5
0
s

a
s

e
n
d
p
o
i
n
t
s

w
e
r
e

o
n
l
y

se
l
e
c
t
e
d

w
h
e
n

s
t
u
d
i
e
s

f
o
r

s
u
b
l
e
t
h
a
l

e
f
f
e
c
t
s

we
r
e

n
o
t

a
v
a
i
l
a
b
l
e
.

C
h
r
o
n
i
c

s
t
u
d
i
e
s

w
e
r
e

s
e
l
e
c
t
e
d

o
v
e
r

s
u
b
c
h
r
o
n
i
c

s
t
u
d
i
e
s
,

a
n
d

s
u
b
c
h
r
o
n
i
c

s
t
u
d
i
e
s

w
e
r
e

s
e
l
e
c
t
e
d

o
v
e
r

a
c
u
t
e

s
t
u
d
ie
s

w
h
e
n

m
u
l
t
i
p
l
e

s
t
u
d
i
e
s

o
f

v
a
r
y
i
n
g

d
u
r
a
t
i
o
n

w
e
r
e

av
a
i
l
a
b
l
e

f
o
r

s
e
l
e
c
t
i
o
n
.

S
t
u
d
i
e
s

w
i
t
h

r
e
p
r
o
d
u
c
t
i
o
n

a
s

t
h
e

e
n
d
p
o
i
n
t

w
e
r
e

s
e
l
e
c
t
e
d

b
e
f
o
r
e

s
t
u
d
i
e
s

w
i
t
h

m
o
r
t
a
l
i
t
y

a
s

t
h
e

e
n
d
p
o
i
n
t
,
w
h
i
c
h

w
e
r
e

s
e
l
e
c
t
e
d

b
e
f
o
r
e

s
t
u
d
i
e
s

w
i
t
h

g
r
o
w
t
h

a
s

t
h
e

en
d
p
o
i
n
t
,

w
h
i
c
h

w
e
r
e

s
e
l
e
c
t
e
d

b
e
f
o
r
e

s
t
u
d
i
e
s

w
i
t
h

s
y
s
t
e
m
i
c

e
f
f
e
c
t
s

a
s

t
h
e

e
n
d
p
o
i
n
t
.

S
t
u
d
i
e
s

w
i
t
h

t
h
e

m
o
s
t

c
o
m
p
l
e
t
e

i
n
f
o
r
m
a
t
i
o
n

an
d

t
h
e
r
e
f
o
r
e

t
h
e

l
e
a
s
t

r
e
s
u
l
t
i
n
g

u
n
c
e
r
t
a
i
n
t
y

w
e
r
e

gi
v
e
n

p
r
e
f
e
r
e
n
c
e

i
n

s
t
u
d
y

s
e
l
e
c
t
i
o
n
.

S
t
u
d
i
e
s

f
r
o
m

s
u
r
r
o
g
a
t
e

c
h
e
m
i
c
a
l
s

w
e
r
e

o
n
l
y

s
e
l
e
c
t
e
d

w
h
e
n

n
o

o
t
h
e
r

s
t
u
d
y

f
o
r

a

p
a
r
t
i
c
u
l
a
r

c
on
t
a
m
i
n
a
n
t

o
f

p
o
t
e
n
t
i
a
l

e
c
o
l
o
g
i
c
a
l

c
o
n
c
e
r
n

w
a
s

f
o
u
n
d
.

b
Un
c
e
r
t
a
i
n
t
y

f
a
c
t
o
r
s

w
e
r
e

u
s
e
d

t
o

a
d
j
u
s
t

a
l
l

m
e
a
s
u
r
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n
s

t
o

c
h
r
o
n
i
c

N
O
A
E
L
S

a
n
d

c
h
r
o
n
i
c

L
O
A
E
L
s

a
s

f
o
l
l
o
w
s
:

NO
A
E
L

t
o

L
O
A
E
L

=

0
.
1

Su
b
c
h
r
o
n
i
c

t
o

c
h
r
o
n
i
c

=

0
.
1

LD
5
0

t
o

c
h
r
o
n
i
c

=

0
.
0
1

Su
b
a
c
u
t
e

t
o

c
h
r
o
n
i
c

=

0
.
0
1

Ac
u
t
e

t
o

c
h
r
o
n
i
c

=

0
.
0
1

wh
e
r
e
:

Ch
r
o
n
i
c

=

>
1
2

w
e
e
k
s

o
r

d
u
r
i
n
g

c
r
i
t
i
c
a
l

l
i
f
e
s
t
a
g
e

Su
b
c
h
r
o
n
i
c

=

4
–
1
2

w
e
e
k
s

Su
b
a
c
u
t
e

=

<
4

w
e
e
k
s
,

m
u
l
t
i
p
l
e

d
o
s
e
s

Ac
u
t
e

=

o
n
l
y

o
n
e

d
o
s
e

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
1
3

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
1
4

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

TTable 3--77. CChemical Uptake for Dietary Items

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

Ch
e
m
i
c
a
l

G
r
o
u
p

Pl
a
n
t

BA
F

Te
r
r
e
s
t
r
i
a
l

In
v
e
r
t
e
b
r
a
t
e
s

BA
F

Sm
a
l
l

Ma
m
m
a
l

BA
F

An
a
l
y
t
e

S
o
u
r
c
e

S
o
u
r
c
e

S
o
u
r
c
e

En
e
r
g
e
t
i
c

Ni
t
r
o
g
l
y
c
e
r
i
n
13
.
3

LA
N
L
,

20
2
0

0.
3
4
7

LA
N
L
,

20
2
0

0.
1
1
6

L
A
N
L
,

2
0
2
0

No
t
e
s
:

BA
F

=

b
i
o
a
c
c
u
m
u
l
a
t
i
o
n

f
a
c
t
o
r

N/
A

=

n
o
t

a
p
p
l
i
c
a
b
l
e
;

a
p
p
l
i
e
s

t
o

u
p
t
a
k
e

f
a
c
t
o
r
s

f
o
r

a
n
a
l
y
t
e
s

w
i
t
h
o
u
t

t
o
x
i
c
i
t
y

r
e
f
e
r
e
n
c
e

va
l
u
e
s

f
o
r

t
h
e

g
i
v
e
n

r
e
c
e
p
t
o
r

Al
l

b
i
o
a
c
c
u
m
u
l
a
t
i
o
n

f
a
c
t
o
r
s

a
r
e

e
x
p
r
e
s
s
e
d

a
s

d
r
y

w
e
i
g
h
t
.

Fu
l
l

r
e
f
e
r
e
n
c
e
s

c
a
n

b
e

f
o
u
n
d

i
n

t
h
e

r
e
f
e
r
e
n
c
e

s
e
c
t
i
o
n

o
f

t
h
e

m
a
i
n

b
o
d
y

o
f

t
h
e

ec
o
l
o
g
i
c
a
l

r
i
s
k

a
s
s
e
s
s
m
e
n
t
.

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

3-
1
5

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3-
1
6

TTable 3--88. EExposure Parameters for Selected Wildlife Receptors of Concern

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

B
o
d
y

w
e
i
g
h
t

F
o
o
d

I
n
g
e
s
t
i
o
n

R
a
t
e
a
Di
e
t
a
r
y

C
o
m
p
o
s
i
t
i
o
n

fr
a
c
t
i
o
n
)

Sp
e
c
i
e
s

Re
c
e
p
t
o
r

Gu
i
l
d

k
g

R
e
f
e
r
e
n
c
e

kg
/
k
g
/
d

dr
y

w
e
i
g
h
t

R
e
f
e
r
e
n
c
e

P
l
a
n
t
s

Te
r
r
e
s
t
r
i
a
l

In
v
e
r
t
e
b
r
a
t
e
s

Sm
a
l
l

M
a
m
m
a
l
s

a
n
d

Ot
h
e
r

V
e
r
t
e
b
r
a
t
e
s

R
e
f
e
r
e
n
c
e
(1
)
S
o
i
l

R
e
f
e
r
e
n
c
e
(1
)

Bi
r
d
s

Bu
r
r
o
w
i
n
g

O
w
l

C
a
r
n
i
v
o
r
e

0
.
1
5
7

A
v
e
r
a
g
e

o
f

m
a
l
e
s

a
n
d

fe
m
a
l
e
s

i
n

C
o
l
o
r
a
d
o

fr
o
m

H
a
u
g

e
t

a
l
.
,

1
9
9
3
,

in

S
a
m
p
l
e

e
t

a
l
.
,

1
9
9
7

0.
0
1
6
3

N
a
g
y
,

2
0
0
1

-
-

-
-

1

A
s
s
u
m
e
d

(
7
1

p
e
r
c
e
n
t

ve
r
t
e
b
r
a
t
e
s
/
2
9

p
e
r
c
e
n
t

in
v
e
r
t
e
b
r
a
t
e
s

i
n

d
i
e
t
—
Gl
e
a
s
o
n

a
n
d

C
r
a
i
g
,

1
9
7
9
)

0.
0
5

T
h
o
m
s
e
n
,

1
9
7
1
,

i
n

S
a
m
p
l
e

et

a
l
.
,

1
9
9
7

Lo
g
g
e
r
h
e
a
d

S
h
r
i
k
e

I
n
s
e
c
t
i
v
o
r
e

0
.
0
4
7

Y
o
s
e
f
,

1
9
9
6

0
.
0
1
4
8

N
a
g
y
,

2
0
0
1

-
-

1

-
-

A
s
s
u
m
e
d

(
6
6

p
e
r
c
e
n
t

in
v
e
r
t
e
b
r
a
t
e
s

a
n
d

3
4

p
e
r
c
e
n
t

ve
r
t
e
b
r
a
t
e
s

i
n

d
i
e
t
—
B
u
r
t
o
n
,

19
9
0
,

i
n

Y
o
s
e
f
,

1
9
9
6
)

0
S
p
e
c
i
e
s

d
o
e
s

n
o
t

g
e
n
e
r
a
l
l
y

fo
r
a
g
e

n
e
a
r

g
r
o
u
n
d

Sa
g
e

S
p
a
r
r
o
w

H
e
r
b
i
v
o
r
e

0
.
0
1
9

A
v
e
r
a
g
e

o
f

m
a
l
e

a
n
d

fe
m
a
l
e

d
a
t
a

f
r
o
m

Bo
n
n
e
v
i
l
l
e

B
a
s
i
n
,

U
t
a
h
,

in

M
a
r
t
i
n

a
n
d

C
a
r
l
s
o
n
,

19
9
8

0.
0
1
9
7

N
a
g
y
,

2
0
0
1

1

-
-

-
-

A
s
s
u
m
e
d

(
8
7

p
e
r
c
e
n
t

p
l
a
n
t
s

an
d

1
3

p
e
r
c
e
n
t

in
v
e
r
t
e
b
r
a
t
e
s
—
w
i
n
t
e
r

d
i
e
t

i
n

Lo
w
e
r

C
o
l
o
r
a
d
o

r
i
v
e
r

re
p
o
r
t
e
d

i
n

M
a
r
t
i
n

a
n
d

Ca
r
l
s
o
n
,

1
9
9
8
)

0.
0
2

M
e
a
s
u
r
e

o
f

c
o
n
s
e
r
v
a
t
i
s
m

We
s
t
e
r
n

M
e
a
d
o
w
l
a
r
k

I
n
v
e
r
t
i
v
o
r
e

0
.
1
0
3

A
v
e
r
a
g
e

o
f

v
a
l
u
e
s

i
n

Sa
m
p
l
e

e
t

a
l
.
,

1
9
9
7

0.
0
1
1
6

N
a
g
y
,

2
0
0
1

-
-

1

-
-

A
s
s
u
m
e
d

1
0
0

p
e
r
c
e
n
t

(
9
8

pe
r
c
e
n
t

i
n
s
e
c
t
s

i
n

Ro
t
e
n
b
e
r
r
y
,

1
9
8
0
)

0.
0
2

M
e
a
s
u
r
e

o
f

c
o
n
s
e
r
v
a
t
i
s
m

Ma
m
m
a
l
s

Bl
a
c
k
-
t
a
i
l
e
d

J
a
c
k
r
a
b
b
i
t

H
e
r
b
i
v
o
r
e

2
.
1

G
o
o
d
w
i
n

a
n
d

C
u
r
r
i
e
,

19
6
5
,

i
n

S
a
m
p
l
e

e
t

a
l
.
,

19
9
7

0.
0
0
8
5

N
a
g
y
,

2
0
0
1

1

-
-

-
-

S
a
m
p
l
e

e
t

a
l
.
,

1
9
9
7

0
.
0
6
3

A
r
t
h
u
r

a
n
d

G
a
t
e
s

(
1
9
8
8
)

i
n

Sa
m
p
l
e

e
t

a
l
.
,

1
9
9
7

Co
y
o
t
e

C
a
r
n
i
v
o
r
e

1
0
.
3
3

A
v
e
r
a
g
e

o
f

v
a
l
u
e
s

f
r
o
m

Ca
l
i
f
o
r
n
i
a

a
n
d

A
r
i
z
o
n
a

pr
e
s
e
n
t
e
d

i
n

S
a
m
p
l
e

e
t

al
.
,

1
9
9
7

0.
0
0
0
3

N
a
g
y
,

2
0
0
1

-
-

-
-

1

A
s
s
u
m
e
d

(
9
9

p
e
r
c
e
n
t

ve
r
t
e
b
r
a
t
e

d
i
e
t

i
n

S
p
e
r
r
y
,

19
3
4
)

0.
0
2
8

U
s
e
d

R
e
d

F
o
x

D
a
t
a

f
r
o
m

Be
y
e
r

e
t

a
l
.
,

1
9
9
4

Gr
a
s
s
h
o
p
p
e
r

M
o
u
s
e

I
n
v
e
r
t
i
v
o
r
e

0
.
0
4
1

H
a
r
r
i
m
a
n
,

1
9
7
3

0
.
0
0
3
3

N
a
g
y
,

2
0
0
1

--

1

-
-

B
a
i
l
e
y

a
n
d

S
p
e
r
r
y
,

1
9
2
9

0
.
1
3

T
a
l
m
a
g
e

a
n
d

W
a
l
t
o
n
,

1
99
3

Or
d
'
s

K
a
n
g
a
r
o
o

R
a
t

H
e
r
b
i
v
o
r
e

0
.
0
5
2

J
o
n
e
s
,

1
9
8
5

0
.
0
0
3
1

N
a
g
y
,

2
0
0
1

1

-
-

-
-

G
a
r
r
i
s
o
n

a
n
d

B
e
s
t
,

1
9
9
0

0
.
0
2

M
e
a
s
u
r
e

o
f

c
o
n
s
e
r
v
a
t
i
s
m

Pr
o
n
g
h
o
r
n

H
e
r
b
i
v
o
r
e

4
9

S
m
i
t
h

a
n
d

B
e
a
l
e
,

1
9
7
4

0
.
0
0
2
6

N
a
g
y
,

2
0
0
1

1

--

-
-

B
e
a
l
e

a
n
d

S
m
i
t
h
,

1
9
7
0

0
.
0
2

M
e
a
s
u
r
e

o
f

c
o
n
s
e
r
v
a
t
i
s
m

To
w
n
s
e
n
d
'
s

G
r
o
u
n
d

S
q
u
i
r
r
e
l

H
e
r
b
i
v
o
r
e

0
.
3
2
5

R
i
c
k
a
r
t
,

1
9
8
7

0
.
0
0
2
0

N
a
gy
,

2
0
0
1

1

-
-

-
-

R
i
c
k
a
r
t
,

1
9
8
7

0
.
0
2

M
e
a
s
u
r
e

o
f

c
o
n
s
e
r
v
a
t
i
s
m

No
t
e
s
:

kg

=

k
i
l
o
g
r
a
m
(
s
)

kg
/
k
g
/
d

d
r
y

w
e
i
g
h
t

=

k
i
l
o
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

b
o
d
y

w
e
i
g
h
t

p
e
r

d
a
y

i
n

d
r
y

w
e
i
g
h
t

a
Na
g
y

(
2
0
0
1
)

f
o
o
d

i
n
t
a
k
e

r
e
g
r
e
s
s
i
o
n

e
q
u
a
t
i
o
n

b
a
s
e
d

o
n

d
r
y

m
a
t
t
e
r

-
-
-
>

F
I
(
k
g
fo
o
d
/k
g
bw
/d
a
y

=

a(g
r
a
m
s

b
o
d
y

w
e
i
g
h
t
)
b /
g
r
a
m
s

b
o
d
y

w
e
i
g
h
t

Gr
o
u
p

a
b

ca
r
n
i
v
o
r
o
u
s

b
i
r
d
s

bu
r
r
o
w
i
n
g

o
w
l

0.
8
4
9

0
.
6
6
3

pa
s
s
e
r
i
n
e

b
i
r
d
s

sp
a
r
r
o
w
,

m
e
a
d
o
w
l
a
r
k
,

sh
r
i
k
e

0.
6
3

0
.
6
8
3

ca
r
n
i
v
o
r
o
u
s

m
a
m
m
a
l
s

co
y
o
t
e

0.
1
5
3

0
.
8
3
4

he
r
b
i
v
o
r
o
u
s

m
a
m
m
a
l
s

ra
b
b
i
t
,

p
r
o
n
g
h
o
r
n

0.
8
5
9

0
.
6
2
8

ro
d
e
n
t
i
a

mo
u
s
e
,

r
a
t
,

s
q
u
i
r
r
e
l

0.
3
3
2

0
.
7
7
4

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3
-
1
7

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3-
1
8

TTable 3--99. RRisk Screening for Terrestrial Plants and Invertebrates
Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

20
1
9
-
2
0
2
1

D
a
t
a

T
e
r
r
e
s
t
r
i
a
l

P
l
a
n
t
s

T
e
r
r
e
s
t
r
i
a
l

I
n
v
e
r
t
e
b
r
a
t
e
s

Ch
e
m
i
c
a
l

G
r
o
u
p

A
n
a
l
y
t
e

Nu
m
b
e
r

o
f

De
t
e
c
t
s

Nu
m
b
e
r

o
f

Sa
m
p
l
e
s

Ma
x
i
m
u
m

De
t
e
c
t

(m
g
/
k
g
)

Pl
a
n
t

N
O
E
C

(m
g
/
k
g
)

P
l
a
n
t

H
Q

So
i
l

In
v
e
r
t
e
b
r
a
t
e

NO
E
C

(
m
g
/
k
g
)

So
i
l

I
n
v
e
r
t
e
b
r
a
t
e

HQ

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

2
1

<
1

1
3

1
.
2

No
t
e
s
:

--

=

n
o
t

a
v
a
i
l
a
b
l
e

HQ

=

h
a
z
a
r
d

q
u
o
t
i
e
n
t

mg
/
k
g

=

m
i
l
l
i
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

NO
E
C

=

n
o

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n

NS
V

=

n
o

s
c
r
e
e
n
i
n
g

v
a
l
u
e

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3
-
1
9

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3-
2
0

TTable 3--110. RRisk Screening EEvaluation for Birds and Mammals
Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

20
1
9
-
2
0
2
1

D
a
t
a

(m
g
/
k
g
)

Bi
o
a
c
c
u
m
u
l
a
t
i
o
n

F
a
c
t
o
r
s
/

Re
g
r
e
s
s
i
o
n

M
o
d
e
l
s

Es
t
i
m
a
t
e
d

C
o
n
c
e
n
t
r
a
t
i
o
n
s

i
n

Bi
o
t
a

(m
g
/
k
g

D
W
)

R
e
c
e
p
t
o
r

E
x
p
o
s
u
r
e

F
a
c
t
o
r
s

D
i
e
t
a
r
y

C
o
m
p
o
s
i
t
i
o
n

Da
i
l
y

D
o
s
a
g
e

Sc
r
e
e
n
i
n
g

R
i
s
k

Es
t
i
m
a
t
e

Pl
a
n
t

BA
F

In
v
e
r
t

BA
F

Ma
m
m
a
l

BA
F

Bo
d
y

We
i
g
h
t

(k
g
)

Fo
o
d

In
g
e
s
t
i
o
n

Ra
t
e

(k
g
/
k
g
/
d
)

To
t
a
l

Ex
p
o
s
u
r
e

Do
s
a
g
e

(m
g
/
k
g
/
d
)

NO
A
E
L

TR
V

N
O
A
E
L

H
Q

An
a
l
y
t
e

Ty
p
e

A
n
a
l
y
t
e

d
e
t

n

Ma
x
i
m
u
m

De
t
e
c
t

P
l
a
n
t

I
n
v
e
r
t

Sm
a
l
l

Ma
m
m
a
l

S
p
e
c
i
e
s

P
l
a
n
t

I
n
v
e
r
t

M
a
m
m
a
l

S
o
i
l

P
l
a
n
t

I
n
v
e
r
t

M
a
m
m
a
l

S
o
i
l

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

Bu
r
r
o
w
i
n
g

Ow
l

0.
1
5
7

0
.
0
1
6
3

--

-
-

1

0
.
0
5

--

-
-

2
.
8
E
-
0
2

8
.
1
E
-
0
4

2
.
9
E
-
0
2

NS
V

U
n
c
e
r
t
a
i
n
t
y

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

Lo
g
g
e
r
h
e
a
d

Sh
r
i
k
e

0.
0
4
7

0
.
0
1
4
8

--

1

-
-

0

--

7
.
7
E
-
0
2

-
-

0
.
0
E
+
0
0

7
.
7
E
-
0
2

NS
V

U
n
c
e
r
t
a
i
n
t
y

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

Sa
g
e

Sp
a
r
r
o
w

0.
0
1
9

0
.
0
1
9
7

1
-
-

-
-

0
.
0
2

3.
9
E
+
0
0

-
-

-
-

3
.
9
E
-
0
4

3
.
9
E
+
0
0

NS
V

U
n
c
e
r
t
a
i
n
t
y

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

We
s
t
e
r
n

Me
a
d
o
w
l
a
r
k

0.
1
0
3

0
.
0
1
1
6

--

1

-
-

0
.
0
2

--

6
.
0
E
-
0
2

-
-

2
.
3
E
-
0
4

6
.
1
E
-
0
2

NS
V

U
n
c
e
r
t
a
i
n
t
y

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

Bl
a
c
k
-
t
a
i
l
e
d

Ja
c
k
r
a
b
b
i
t

2.
1
0
0

0
.
0
0
8
5

1
-
-

-
-

0
.
0
6
3

1.
7
E
+
0
0

-
-

-
-

5
.
4
E
-
0
4

1
.
7
E
+
0
0

96
.
4

<
1

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

Co
y
o
t
e

1
0
.
3

0
.
0
0
0
3

--

-
-

1

0
.
0
2
8

--

-
-

5
.
7
E
-
0
4

9
.
2
E
-
0
6

5
.
8
E
-
0
4

96
.
4

<
1

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

Gr
a
s
s
h
o
p
p
e
r

Mo
u
s
e

0.
0
4
1

0
.
0
0
3
3

--

1

-
-

0
.
1
3

--

1
.
7
E
-
0
2

-
-

4
.
2
E
-
0
4

1
.
7
E
-
0
2

96
.
4

<
1

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

Or
d
'
s

Ka
n
g
a
r
o
o

Ra
t

0.
0
5
2

0
.
0
0
3
1

1
-
-

-
-

0
.
0
2

6.
2
E
-
0
1

-
-

-
-

6
.
2
E
-
0
5

6
.
2
E
-
0
1

96
.
4

<
1

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

13
.
3

0
.
3
4
7

0
.
1
1
6

2.
0
E
+
0
2

5
.
2
E
+
0
0

1
.
7
E
+
0
0

Pr
o
n
g
h
o
r
n

4
8
.
8

0
.
0
0
2
6

1
-
-

-
-

0
.
0
2

5.
3
E
-
0
1

-
-

-
-

5
.
3
E
-
0
5

5
.
3
E
-
0
1

96
.
4

<
1

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

3

1
4

1
5

1
3
.
3

0
.
3
4
7

0.
1
1
6

2
.
0
E
+
0
2

5
.
2
E
+
0
0
1
.
7
E
+
0
0

T
o
w
n
s
e
n
d
'
s

Gr
o
u
n
d

Sq
u
i
r
r
e
l

0.
3
2
5

0
.
0
0
2
0

1

-
-

-
-

0
.
0
2

4
.
1
E
-
0
1

-
-

-
-

4
.
1
E
-
0
5

4
.
1
E
-
0
1

9
6
.
4

<
1

No
t
e
s
:

BA
F

=

b
i
o
a
c
c
u
m
u
l
a
t
i
o
n

f
a
c
t
o
r

de
t

=

d
e
t
e
c
t
s

DW

=

d
r
y

w
e
i
g
h
t

HQ

=

h
a
z
a
r
d

q
u
o
t
i
e
n
t

kg

=

k
i
l
o
g
r
a
m
(
s
)

kg
-
b
w
/
d

d
r
y

w
e
i
g
h
t

=

k
i
l
o
g
r
a
m

p
e
r

b
o
d
y

w
e
i
g
h
t

p
e
r

d
a
y

d
r
y

w
e
i
g
h
t

mg
/
k
g

=

m
i
l
l
i
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

mg
/
k
g
/
d

=

m
i
l
l
i
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

p
e
r

d
a
y

n
=

n
u
m
b
e
r

o
f

s
a
m
p
l
e
s

N/
A

=

n
o
t

a
p
p
l
i
c
a
b
l
e

NO
A
E
L

=

n
o

o
b
s
e
r
v
e
d

a
d
v
e
r
s
e

e
f
f
e
c
t

l
e
v
e
l

NS
V

=

n
o

s
c
r
e
e
n
i
n
g

T
R
V

TR
V

=

t
o
x
i
c
i
t
y

r
e
f
e
r
e
n
c
e

v
a
l
u
e

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3
-
2
1

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3-
2
2

TTable 3--111. PPoint--bby--PPoint Risk Estimation for Soil Invertebrates

Th
e
r
m
a
l
Tr
e
a
t
m
e
n
t
Un
i
t
20
2
2
Ec
o
l
o
g
i
c
a
l
Ri
s
k
Sc
r
e
e
n
i
n
g
Ev
a
l
u
a
t
i
o
n

Sa
m
p
l
e

D
a
t
a

N
O
E
C

S
c
r
e
e
n

L
O
E
C

S
c
r
e
e
n

Ch
e
m
i
c
a
l

Gr
o
u
p

C
O
P
E
C

Sa
m
p
l
e

Ye
a
r

S
a
m
p
l
e

I
D

Sa
m
p
l
e

Ty
p
e

Re
s
u
l
t

(
m
g
/
k
g
)

Q
u
a
l
i
f
i
e
r

D
e
t
e
c
t

NO
E
C

(m
g
/
k
g
)

NO
E
C

HQ

LO
E
C

(m
g
/
k
g
)

LO
E
C

HQ

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
6
4
4
-
2
0
1
9

N

1
5

Y

13

1.
2

13
0

<
1

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
2
1

T
T
U
-
6
4
4
-
2
0
2
1

N

2
.
6

J

Y

13

<
1

13
0

<
1

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
5
2
0
-
2
0
1
9

N

2
.
3

Y

13

<
1

13
0

<
1

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
2
1

T
T
U
-
1
1
5
-
2
0
2
1

N

0
.
2
1

U
J

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
2
1
5
-
2
0
1
9

N

0
.
2
1

U

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
2
1
5
-
2
0
1
9
-
2

F
D

0
.
2
1

U

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
2
1
5
-
2
0
2
1

N

0
.
2
1

U
J

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
2
1

T
T
U
-
2
1
9
-
2
0
2
1

N

0
.
2
1

U
J

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
2
1

T
T
U
-
2
1
9
-
2
0
2
1
-
F
D

F
D

0
.
2
1

U
J

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
2
1

T
T
U
-
3
9
1
-
2
0
2
1

N

0
.
2
1

U
J

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
5
0
-
2
0
2
1

N

0
.
2
1

U
J

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
5
2
1
-
2
0
1
9

N

0
.
2
1

U

N

13

N
D

1
3
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
5
5
2
-
2
0
1
9

N

0
.
2
1

U

N

13

N
D

13
0

N
D

En
e
r
g
e
t
i
c

N
i
t
r
o
g
l
y
c
e
r
i
n

2
0
1
9

T
T
U
-
5
5
3
-
2
0
1
9

N

0
.
2
1

U

N

13

N
D

1
3
0

N
D

No
t
e
s
:

CO
P
E
C

=

c
h
e
m
i
c
a
l

o
f

p
o
t
e
n
t
i
a
l

e
c
o
l
o
g
i
c
a
l

c
o
n
c
e
r
n

HQ

=

h
a
z
a
r
d

q
u
o
t
i
e
n
t

LO
E
C

=

l
o
w
e
s
t

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n

mg
/
k
g

=

m
i
l
l
i
g
r
a
m
(
s
)

p
e
r

k
i
l
o
g
r
a
m

ND

=

n
o
t

d
e
t
e
c
t
e
d

i
n

t
h
i
s

s
a
m
p
l
e

NO
E
C

=

n
o

o
b
s
e
r
v
e
d

e
f
f
e
c
t

c
o
n
c
e
n
t
r
a
t
i
o
n

SE
C
T
I
O
N

3

–

R
E
S
U
L
T
S

PP
S
0
8
3
0
2
2
1
4
3
9
S
L
C

3
-
2
3

Th
i
s

p
a
g
e

i
n
t
e
n
t
i
o
n
a
l
l
y

l
e
f
t

b
l
a
n
k
.
SECTION 4
PPS0830221439SLC 4-1
Summary and Conclusions
4.0.0.1 Soil data from the 2019 and 2021 sampling events at the TTU were evaluated to determine the
current status of potential ecological risks. New data (2019 and 2021) were compared with previously
collected data to identify newly detected analytes, analytes with higher maximum concentrations than
previous sampling events, or exceeding background data, where applicable. Nitroglycerin in soil was
retained for further evaluation in this SLERA. No accumulations of surface water have been observed at
the site since 2013. Therefore, surface water was not evaluated in this 2022 SLERA. Methods and
parameters employed to perform the SLERA submitted in 2005 (CH2M HILL, 2005), updated as
appropriate, were applied to the 2019 and 2021 data. The results are as follows:
x Initial screen based on maximum concentrations and NOECs/NOAELs:
HQs exceeded 1 for nitroglycerin for terrestrial invertebrates only. This analyte/receptor pair
were retained for further evaluation in the refined screen.
NOAELs for birds were not available for nitroglycerin indicating some uncertainty in the
potential toxicity of this analyte. However, nitroglycerin is not considered toxic to birds in
environmental settings (Williams et al., 2015).
x Refined screen for terrestrial invertebrates based on point-by-point comparison against the NOEC
and LOEC.
HQs exceeded 1 at the NOEC for 1 of 14 samples.
HQs were less than 1 at the LOEC for all samples.
Only one sample had a nitroglycerin concentration exceeding previous data.
4.0.0.2 The 2019 and 2021 data do not indicate significant potential for site-related ecological risks at
the TTU. The maximum detected concentration of nitroglycerin exceeded the NOEC for terrestrial
invertebrates and was retained for further evaluation in the refined screen. Point-by-point evaluation
indicated that only 1 sample had a nitroglycerin concentration exceeding the NOEC. This was also the
only concentration exceeding the previous maximum detected concentration. There were no detections
exceeding the LOEC. Potential risks due to nitroglycerin are considered low. Nitroglycerin was not
retained as a chemical of environmental concern.
It should be noted that the sampling efforts after 2012 focused on metals and energetic compounds.
The 2005 SLERA identified TPH, acetone, and PAHs as potential risk and the 2009 SLERA identified
dioxin/furans as potential risk drivers. The absence of new data for these other analytes precludes any
new conclusions. Consequently, these analytes are still considered potential risk drivers. The overall
conclusion of the evaluation of 2019 and 2021 data is that current potential risks to ecological receptors
are not greater than those estimated previously for the TTU.
This page intentionally left blank.
PPS0830221439SLC 5-1
References
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Beale, D.M. and A.D. Smith. 1970. “Forage Use, Water Consumption, and Productivity of Pronghorn
Antelope in Western Utah.” Journal of Wildlife Management. Vol. 34. pp. 570–582.
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(Lanius ludovicianus) in Indiana. Indiana University, Bloomington: Master’s Thesis.
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Evaluation. Hill Air Force Base, Utah. August.
CH2M HILL, Inc. 2009. Utah Test and Training Range Thermal Treatment Unit 2009 Ecological Risk Screen
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CH2M HILL, Inc. 2011. Utah Test and Training Range Thermal Treatment Unit 2011 Ecological Risk Screen
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CH2M HILL, Inc. 2013. Utah Test and Training Range Thermal Treatment Unit 2013 Ecological Risk Screen
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^d/KEϰ 
SECTION 5 – REFERENCES
PPS0830221439SLC 5-2
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Rickart, E.A. 1987. “Spermophilus Townsendii.” Mammalian Species. No. 268. pp. 1–6.
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Estimation of the Exposure of Terrestrial Wildlife to Contaminants. Oak Ridge National
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