DSHW-2010-036140 - 0901a068801b038a

RECEIVED
JUL 2 6 2010
_ , UTAH DIVISIUIM UP
20 July 2010 SOLID & HAZARDOUS WASTE
8200-FYl 1-020 ZPIP.0ZM$
Mr. Brad Maulding, Manager
State of Utah Department of Environmental Quality
Division of Solid and Hazardous Waste
195N.19500 W.
P.O. Box 144880
Salt Lake City, Utah 84114-4880
Attention: JeffVandel
Re: ATK Launch Systems-Promontory EPA ID number UTD009081357
Preliminary Air Dispersion Modeling and Human Health Risk Assessment Report
for Open Bum and Open Detonation Treatment Units Thiokol Launch Systems
Brigham City, Utah (Draft Report) April 2009
Dear Mr.Vandel:
ATK appreciated the opportunity to meet on July 20, 2010 to discuss the permitting
process for our Open Burn and Open Detonation Treatment Units here at the Promontory
Utah facility. This letter accompanies a copy of the Preliminary Air Dispersion Modeling
and Human Health Risk Assessment Report for Open Bum and Open Detonation
Treatment Units at Thiokol Launch Systems Brigham City, Utah (Draft Report) April
2009. ATK expects that this document and data will be beneficial as we proceed to
permit these OBOD Treatment Units.
Please contact me if you have any questions conceming this report. My telephone
number is [phone] or you can contact Blair Palmer at [phone].
Sincerely
Paul V. Hancock, Manager
Environmental Remediation
RECEIVED
JUL 2 6 2010
UTAH DIVl6iui\i ut-
SOLIO & HAZARDOUS WASTE
ZDiD02M€
PRELIMINARY AIR DISPERSION MODELING
AND HUMAN HEALTH RISK ASSESSMENT
REPORT
FOR
OPEN BURN AND OPEN DETONATION
TREATMENT UNITS
THIOKOL LAUNCH SYSTEMS
BRIGHAM CITY, UTAH
DRAFT REPORT
APRIL 2009
DRAFT
APRIL 2009
TABLE OF CONTENTS
SECTION PAGE NO
1 0 INTRODUCTION 1-1
2 0 AIR DISPERSION MODELING PROTOCOL 2-1
TERRAIN AND SITE DESCRIPTION 2-1
TREATMENT LOCATIONS 2-1
M-136 Treatment Unit Descnption 2-1
M-225 Treatment Unit Descnption 2-2
AIR QUALITY DISPERSION MODEL SELECTION 2-2
LAND USE ANALYSIS 2-3
SURFACE ROUGHNESS HEIGHT 2-3
OB/OD SOURCE SCENARIOS 2-4
M-136 TREATMENT QUANTITY SCENARIOS 2-6
M-225 TREATMENT QUANTITY SCENARIOS 2-6
SOURCE PARAMETERS 2-6
OBODI Emissions Test and Emission Factors 2-7
OTHER MODELING ASSUMPTIONS FOR M-136 AND M-225 2-9
DEPOSITION MODELING 2-11
RECEPTOR NETWORKS 2-13
General Receptor Networks 2-13
Discrete Receptor Network 2-14
METEOROLOGICAL DATA 2-15
Surface Data 2-15
Upper Air Observations (Mixing Height Data) 2-16
Meteorological Preprocessor 2-16
OBODM POST-PROCESSING 2-17
POLLUTANT AVERAGING PERIODS 2-18
3 0 AIR DISPERSION MODELING RESULTS 3-1
3 1 MAXIMUM ON-SITE AND OFF-SITE RECEPTORS 3-1
3 2 COMPARISON TO NAAQS 3-1
3 3 ONSITE EXPOSURE CONCENTRATIONS 3-2
3 4 SUMMARY 3-2
4 0 HUMAN HEALTH RISK ASSESSMENT 4-1
41 METHODOLOGY 4-1
4 2 RESULTS OF PRELIMINARY HHRA 4-2
4 3 RECOMMENDATIONS FOR FINAL HHRA 4-4
REFERENCES R-1
APPENDIX
A HUMAN HEALTH RISK ASSESSMENT SUPPORTING DOCUMENTATION
2 1
2 2
2 2 1
2 22
2 3
2 4
2 5
2 6
2 7
2 8
2 9
2 9 1
2 10
2 11
2 12
2 12 1
2 122
2 13
2 13 1
2 132
2 133
2 14
2 15
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TABLES
NUMBER
1 M-136 Risk Assessment Source Area
2 M-225 Risk Assessment Source Areas
3 M-136 Open Burning Source Parameters
4 M-225 Open Buming and Open Detonation Source Parameters
5 Average and maximum Emission Factors Based on OBODI Emissions Testing
6 Summary of Deposition and Gravitational Settling Calculation Parameters
7 A Companson of Discrete Receptor 1-Hour Carbon Monoxide Concentrations to the National
Ambient Air Quality Standard Based on Average OBODI Emission Factor
8 A Companson of Discrete Receptor 1 -Hour Carbon Monoxide Concentrations to the National
Ambient Air Quality Standard Based on Maximum OBODI Emission Factor
9 A Companson of Discrete Receptor 8-Hour Carbon Monoxide Concentrations to the National
Ambient Air Quality Standard Based on Average OBODI Emission Factor
10 A Companson of Discrete Receptor 8-Hour Carbon Monoxide Concentrations to the National
Ambient Air Quality Standard Based on Maximum OBODI Emission Factor
11 A Companson of Discrete Receptor 24-Hour PM 2 5 Concentrations to the National Ambient Air
Quality Standard Based on Average OBODI Emission Factor
12 A Companson of Discrete Receptor 24-Hour PM 2 5 Concentrations to the National Ambient Air
Quality Standard Based on Maximum OBODI Emission Factor
13 A Companson of Discrete Receptor 24-Hour PM 10 Concentrations to the National Ambient Air
Quality Standard Based on Average OBODI Emission Factor
14 A Companson of Discrete Receptor 24-Hour PM 10 Concentrations to the National Ambient Air
Quality Standard Based on Maximum OBODI Emission Factor
15 A Companson of Discrete Receptor Annual PM 2 5 Concentrations to the National Ambient Air
Quality Standard Based on Average OBODI Emission Factor
16 A Companson of Discrete Receptor Annual PM 2 5 Concentrations to the National Ambient Air
Quality Standard Based on Maximum OBODI Emission Factor
17 A Companson of Discrete Receptor Annual PM 10 Concentrations to the National Ambient Air
Quality Standard Based on Average OBODI Emission Factor
18 A Companson of Discrete Receptor Annual PM 10 Concentrations to the National Ambient Air
Quality Standard Based on Maximum OBODI Emission Factor
19 A Companson of Maximum 8-Hour Onsite Concentrations to OSHA 8-Hour Time-Weighted
Concentrations as a Result of M-136 Operations Based on Average OBODI Emission Factors
20 A Companson of Maximum 8-Hour Onsite Concentrations to OSHA 8-Hour Time-Weighted
Concentrations as a Result of M-136 Operations Based on Maximum OBODI Emission Factors
21 A Companson of Maximum 8-Hour Onsite Concentrations to OSHA 8-Hour Time-Weighted
Concentrations as a Result of M-136 Operations Based on Maximum OBODI Emission Factors
22 A Companson of Maximum 8-Hour Onsite Concentrations to OSHA 8-Hour Time-Weighted
Concentrations as a Result of M-136 Operations Based on Maximum OBODI Emission Factors
23 Chemicals of Potential Concern Evaluated in Human Health Risk Assessment
24 Summary of Cancer Risks and Hazard Indices
25 Summary of Cancer Risks and Hazard Indices by Source
26 Cancer Risks and Hazard Indices
27 Risk by Exposure Pathway Adult Farmer from Source 225A at M225 On-Site maximum Gaseous
Location
28 Chemical-Specific Risks Adult Farmer from Source 225A (Open Burning) at M225 On-Site
Maximum Gaseous Location
29 Chemical-Specific Risks Child Farmer from Source 225A (Open Burning) at M225 On-Site
Maximum Gaseous Location
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TABLES (Continued)
NUMBER
30 Chemical-Specific Risks Adult Resident from source 225A (Open Burning) at M225 On-Site
Maximum Gaseous Location
31 Chemical-Specific Risks Child Resident from Source 225A (Open Burning) at M225 On-Site
Maximum Gaseous Location
32 Companson of Total One-Hour Air Concentrations (ug/m) to UDAQ Toxic Screening Levels -
Average Emission Rates
33 Companson of Total One-Hour Air Concentrations (ug/m) to UDAQ Toxic Screening Levels -
Maximum Emission Rates
34 Companson of Total 24-Hour Air Concentrations (ug/m) to UDAQ Toxic Screening Levels -
Average Emission Rates
35 Companson of Total 24-Hour Air Concentrations (ug/m) to UDAQ Toxic Screening Levels -
Maximum Emission Rates
FIGURES
NUMBER
1 M-136 Treatment Unit 3 kilometer General Receptor Gnd 100 Meter Increment
2 M-136 Treatment Unit 3 kilometer to 10 kilometer General Receptor Gnd 500 Meter Increment
3 M-225 Treatment Unit 3 kilometer General Receptor Gnd 100 Meter Increment
4 M-225 Treatment Unit 3 kilometer to 10 kilometer General Receptor Gnd 500 Meter increment
5 Preliminary Modeling Analysis Discrete Receptor Locations
6 1997 Onsite Wind Rose
7 Preliminary Analysis M-136 Maximum Onsite and Offsite Gas and Particulate Air Concentration
and Deposition Phase Receptors
8 Preliminary Analysis M-225 Maximum Onsite and Offsite Gas and Particulate Air Concentration
and Deposition Phase Receptors
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1 0 INTRODUCTION
ATK Launch Systems (ATK) Corporation, located in Bngham City, Utah currently operates open burning
(OB) and open detonation (OD) units for the treatment of hazardous waste propellants and propellant
contammated matenals These treatment units are identified as M-136 and M-225 and are subject to
RCRA 40 CFR 264 Subpart X permitting requirements for miscellaneous treatment units These units are
currently operating as intenm status facilities
The Utah Department of Environmental Quality Division of Solid and Hazardous Waste (UDSHW) is
requinng ATK to conduct new human health and ecological nsk assessments in support of a new Subpart
X permit application Before the human health and ecological nsk assessments can be conducted, an air
dispersion modeling analysis must be performed to evaluate the air quaiity impact of the M-136 and
M-225 treatment units The results of the air dispersion modeling analysis will be input into human health
and ecological nsk assessment models to determine the potential nsk and hazard from the OB/OD
treatment units
At the request of ATK, Tetra Tech NUS (TtNUS) has conducted a preliminary air dispersion modeling
analysis and human health nsk assessment to calculate the relative magnitude of air concentrations and
nsk that may be encountered in a full scale modeling analysis which will be conducted subsequent to
UDSHW's approval of the air dispersion modeling, human health nsk assessment and ecological nsk
assessment protocols This preliminary modeling analysis has been conducted using a draft air
dispersion modeling protocol which has been developed on the basis of information supplied by ATK
results of an initial meeting with UDSHW, follow-up comments from UDSHW on the draft air dispersion
modeling protocol, new emission charactenzation data for ATK Class 1 3 propellant waste streams, and
to the extent possible modeling guidance as defined in the Human Health Risk Assessment Protocol for
Hazardous Waste Combustion Facilities (HHF?AP) (September, 2005) This report presents the results of
the preliminary air dispersion modeling analysis and human health nsk assessment
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2 0 AIR DISPERSION MODELING PROTOCOL
The modeling methodology used in the preliminary modeling analysis is based on information supplied by
ATK, technical experts, discussions with and comments received from UDSHW, new emissions test data,
and guidance defined in the Human Health Risk Assessment Protocol for Hazardous Waste Combustion
Facilities (HHF^P) (September, 2005) Each aspect of the dispersion modeling protocol is discussed
beiow in Sections 2 1 through 2 15
2 1 TERRAIN AND SITE DESCRIPTION
The Thiokol facility is located in the Blue Spnng Valley which is bounded on the east and west by the
Blue Spnng Hills, and the Engineer, and Promontory Mountain ranges, respectively Within the Blue
Spnng Valley, the terrain is characterized by gentle topography that slopes down from the mountain crest
at an elevation of approximately 6,050 feet above mean sea level (AMSL) toward the center of the Blue
Creek Valley at an elevation of 4,250 feet AMSL As a result, the surrounding environment extending out
to 10 kilometers (km) from each treatment unit can be characterized as complex terrain
For air modeling purposes terrain is referred to as "complex' if the elevation ofthe surrounding land, with
the assessment area, is above the top of the emission release point Because ATK conducts OB and OD
treatment essentially at ground level in burn pans and uncovered pits, aii receptors having an elevation
greater than the treatment unit base elevation are considered complex terrain receptors Ali receptors at
or below the treatment unit base elevation are considered to be simple terrain receptors
2 2 TREATMENT LOCATIONS
OB and OD treatment of reactive wastes is conducted at two facilities The mam treatment facility is
M-136, which IS located centrally to the two mam manufactunng sites A second OB treatment facility is
M-225, which is located in a remote development location called Plant III The M-225 unit is located
about 9 km southeast of the M-136 unit A descnption of the treatment unit activities that are conducted
at each unit are descnbed in Sections 2 2 1 and 2 2 2
2 21 M-136 Treatment Unit Description
M-136 IS the primary treatment unit for conducting open burning at ATK The total annual quantity of
waste treated at the M-136 treatment unit is more than 300 times the annual quantity treated by OB at
M-225 The materials treated at M-136 include primary bulk waste propellant, 1 1 and 1 3, contaminated
waste, laboratory waste and obsolete Minute Man rocket motors
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APRIL 2009
The M-136 treatment unit consists of 14 burn stations OB is conducted at 13 burn stations in unlined or
lined (with clay soil) trays five days a week (Monday through Fnday) OB of obsolete Minute Man rocket
motors IS conducted at Bum Station 14 on a large pad used to support and secure the motors dunng
treatment OD of waste matenals is conducted at either Burn Station 13 or 14 Detonation pits are
prepared using augers, and then the reactive wastes are placed in the pit uncovered and detonated This
preliminary modeling analysis assumed that M-136 treatment can take place aii days of the week
(including Saturday and Sunday) between 1000 and 1800 hours to determine the potential worst-case
1-hour and annual air dispersion factors (ADFs) that may occur in an annual penod dunng potential
treatment hours
A detailed descnption of M-136 sources and treatment quantities assumed in this modeling analysis are
present in Section 2 6, 2 7, and 2 9
2 22 M-225 Treatment Unit Description
M-225 receives small amounts of the reactive waste matenals from the Plant III propellant development
area These reactive wastes are treated via open burning or open detonation Reactive wastes are
treated in burn pans and include pure double base (1 1) propellants and composite propellants (1 3), as
well as, reactive contaminated trash materials such as cloth and paper wipes, metal containers, plastics,
and propellant ingredients
The treatment activity at M-225 usually takes place about once per week and involves small quantities of
waste materials Open detonation treatment of 1 1 pure propellants is conducted at one location within
the M-225 fenced area Detonation pits are usually prepared using augers, and then the reactive wastes
are placed in the pit uncovered and detonated
A detailed descnption of M-136 sources and treatment quantities assumed in this modeling analysis are
present in Section 2 6 2 8, and 2 9
2 3 AIR QUALITY DISPERSION MODEL SELECTION
The HHRAP guidance recommends the use of the industrial Source Complex Short Term 3 (ISCST3)
dispersion model for nsk assessment evaluations However ISCST3 is geared toward sources
associated with industrial facilities rather than OB/OD treatment operations in the case of waste
treatment activities at ATK, a special dispersion model is needed to simulate the quasi-continuous and
instantaneous plume release, cloud nse, and dispersion of OB and OD sources OB treatment is typically
quasi-continuous source, whereas OD is considered to be instantaneous source
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APRIL 2009
The United States Environmental Protection Agency (U S EPA) maintains a Support Center for
Regulatory Air Models called SCFIAMS The only SCF^M model that is specific to OB and OD treatment
operations is the Open Burn/Open Detonation Dispersion Model (OBODM) (U S Army, February 1998,
U S Army, Apnl 1998) This model has also been identified by UDSHW as the model of choice for
conducting the ATK air dispersion modeling analysis in support of the human health nsk assessment
OBODM IS the preferred model for OB/OD sources and the latest version of the model (1 3 24) was used
in this analysis to calculate the air quality impact of emissions from M-136 and M-225 However, OBODM
IS limited in the number of receptors (100) it can address in a single model run, which necessitates
numerous model runs and significantly more post-processing time, particularly in the case of large
receptor networks requinng analysis with multiple years of meteorological data
OBODM is specifically designed to predict the air quality impact (air concentrations and deposition) from
OB and OD treatment Because the model is specifically designed for OB and OD treatment, it can
accommodate source-specific input data regarding treatment operations This allows the model to
provide greater detail regarding the spatial and temporal vanation of emissions and meteorological
conditions and enhances the model's ability to evaluate individual source impacts
2 4 LAND USE ANALYSIS
Land use information is necessary for the selection of certain air dispersion modeling vanables
(dispersion coefficients and surface roughness) The land use charactenstics surrounding a source of air
emission can be determined from United States Geological Survey (USGS) 7 5-minute topographic maps
aerial photographs, or visual surveys ofthe area The land use classification for the area surrounding the
M-136 and M-225 treatment units was detennined from the Thatcher Mountain 7 5-minute
(1 24,000 scale) quadrangle using the Auer method (Auer 1978), as descnbed in Section 3 3 2 1 of the
HHFJAP guidance (September 2005) Using this method, areas are defined as either "rural" or "urban "
A radius of 3 km beyond each treatment unit source was given a general inspected to define whether the
area withm 3 km is rural or urban according to Auer's (Auer, 1978) definitions This inspection resulted in
a rural classification for both treatment units The 3 km radius area was broken down into smaller areas
(100 meters by 100 meters) for a more detailed inspection Each small area was then either classified as
rural or urban Following the Auer method resulted in a rural designation for both treatment units
2 5 SURFACE ROUGHNESS HEIGHT
The surface roughness height (length) used in the preliminary modeling analysis is based on the
methodology given in Section 3 3 2 2 of the HHF^P guidance (U S EPA, 1998) The results of land use
classification described in Section 2 4 and the five-year wind rose data for the M-245 on-site
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DRAFT
APRIL 2009
meteorological momtonng station were used to calculate site-specific surface roughness heights for both
treatment units Based on HHRAP guidance methodology, all wind sectors were classified as desert
shrub land In this case, the annual site-specific surface roughness height for both treatment units was
calculated to be approximately 0 26 meters
2 6 OB/OD SOURCE SCENARIOS
In order to calculate the air quality impact of OB and OD treatment operations, OBODM requires specific
information regarding the charactenstics of the treatment source For example, OBODM requires input
data indicating the type of energetic matenal being treated, how it is being treated (OB or OD), the heat
content and burn rate of the matenal, the amount of material being treated, the source dimensions, and
the plume release height
The following OB/OD treatment source scenanos were evaluated in this preliminary air dispersion
modeling analysis for ATK treatment operations
• OB treatment of pure propellant and energetic-contaminated materials at M-136 and M-225
• OD treatment of energetic waste at M-136 and M-225
The source scenarios assumed for M-136 and M-225 are discussed below
M-136 Treatment Unit Source Scenario
The M-136 Unit has 14 burn stations Ali treatment is conducted in pans with the exception of Burn
Station 14, which consists of a large pad used for the OB of obsolete Minute Man rocket motors and
wastes that are treated in uncovered pits by OD at Stations 13 or 14 OD is conducted at one location
within the M-136 fenced area Detonation pits are usually prepared using augers, and then the reactive
wastes are placed in the pit uncovered and detonated The OD pits are not covered dunng OD treatment
Although the OBODM model has the capability to model multiple source scenanos and individual
locations in the same model run, computer resources (both computational and memory/output file size)
preclude modeling ali individual M-136 treatment stations As a result, certain treatment stations were
consolidated into a single source, where deemed applicable, and as recommended in modeling guidance,
in order to accommodate computer resources
U S EPA modeling guidance (U S EPA 1992) allows the merging of multiple emission points that are
located within close proximity to one another and if the emission points have similar release parameters
in the case of M-136, the 14 burn stations were consolidated into three separate sources with discrete
coordinates due to the separation distance between the burn station areas For example, in the case
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M-136 Burn Stations 1-12, aii stations are located m one general treatment area that measures
approximately 160 x 220 meters
The approximate separation distance from the Burn Station 1-12 area to Burn Station 13 is approximately
200 - 250 meters The estimated separation distance from Burn Station 13 to Burn Station 14 is about
500 meters As a result, it is recommended that these treatment locations be modeled as three separate
sources due to their respective treatment areas and separation distances The UTM coordinates selected
for each of these sources represent the center of the respective treatment operational areas
The four M-136 source areas used in this analysis include the following Burn Stations
• Source M-136A - representing Burn Stations 1-12 (OB of 1 1 13, and contaminated trash)
• Source M-136B - representing Burn Stations 13 (OB of 1 3 and igniters)
• Source M-136C - representing Burn Station 14 (OB of whole Minute Man motors)
• Source M-136D - representing Burn Station 13 (OD of waste energetics)
In order to provide a conservative (high bias) estimate of the air quality impact from OB and OD
treatment, the M-136 unit was modeled using short term (1-hour) treatment quantities, which are lower
than the maximum allowable short term quantities established by ATK for each source These lower
short term treatment quantities are designed to represent average daily treatment quantities for the
purpose of computing annual average air concentrations and total deposition in addition, per event
modeling at a lower treatment quantity will yield a conservative overestimate of air concentrations and
deposition due to lower plume nse as compared to modeling at the maximum allowable treatment
quantity (more heat, more plume nse, lower ground level concentrations and deposition)
This preliminary modeling analysis assumed that M-136 treatment could potentially be conducted once
per hour each day (including Saturday and Sunday) within the time interval 1000 to 1800 This interval
was selected to be the most likely period for OB and OD treatment based on information received from
ATK This methodology was used to determine the worst case 1-hour ADF that could potentially occur
over the daily operating period for a given annual penod An ADF is the concentration value based on a
unit emission factor of 1 0
M-225 Treatment Unit Source Scenano
The M-225 Unit has five burn stations (using burn pans) and one detonation pit OB is conducted in lined
burn pans OD is conducted at one location within the M-225 fenced area Detonation pits are usually
prepared usmg augers, and then the reactive wastes are placed in the pit uncovered and detonated The
OD pits are not covered dunng OD treatment
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The M-225 treatment unit was evaluated as two treatment sources in the preliminary modeling analysis
• Source M-225A - representing OB in pans (11,13, and contaminated trash)
• Source M-225B - representing OD in one pit (1 1 and 1 3 propellants)
Treatment was assumed to be conducted once per hour each day (including Saturday and Sunday) in the
time interval 1000 to 1800 local time in order to determine the worst-case 1-hour ADF for each source
Each source was modeled at a unit emission rate Due to the relative small size of the M-225 treatment
area, M-225A and M-225b were assigned the same location coordinate
2 7 M-136 TREATMENT QUANTITY SCENARIOS
The per event and maximum annual treatment quantity values used in the preliminary modeling analysis
were determined by ATK Table 1 presents a listing of the M-136 sources, waste categories, and ATK
established maximum daily and annual treatment quantities The single event treatment quantities used
in OBODM for each of the four M-136 treatment sources are shown in Table 1 in the column labeled
"Model Quantity" For example, the per event treatment quantities used in OBODM for sources M-136A,
M-136B, M-136c, and M-136D are 60,000, 2,000, 7,000, and 300 pounds (lbs) per event, respectively
The maximum daily and annual treatment quantities from Table 1 were then used in the post-processing
step to estimate maximum air concentrations and deposition values
2 8 M-225 TREATMENT QUANTITY SCENARIOS
In the case of the M-225 treatment unit, average and annual treatment quantities for OB and OD were
supplied by ATK Table 2 presents a listing of the M-225 sources, waste categories, and ATK established
maximum daily and annual treatment quantities The single event treatment quantities used in OBODM
for each of the two M-225 treatment sources are shown in Table 2 in the column labeled, "Model
Quantity" The per event treatment quantities used m OBODM for sources M-225A and M-225B were
600 and 300 pounds per event, respectively The maximum daily and annual treatment quantities from
Table 2 were then used in the post-processing step to estimate maximum air concentrations and
deposition values
2 9 SOURCE PARAMETERS
The selection of M-136 and M-225 source parameters used m OBODM is based on a visit to each
treatment unit, operations information provided by ATK and guidance associated with HHFJAP and ATK
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guidance A summary of the source parameters for the four M-136 and the two M-225 treatment sources
IS shown in Tables 3 and 4, respectively
All OB and OD sources were assumed to treat the same class of matenals as tested in the Open
Detonation Open Burning Improved (OBODI) test chamber from June 7 to 15, 2006 (URS, 2007) The
results of the OBODI tests produced a list of emission factors that were used in this analysis to compute
air concentrations and deposition rates Information regarding the testing program and the emission
factors used in this analysis is discussed in Section 2 9 1 A heat content value of 1,471 calones/gram
(cai/gm) was assumed for aii OB and OD sources in OBODM
2 91 OBODI Emissions Test and Emission Factors
Understanding emissions from OB/OD units is a necessary component for the nsk assessment process
The UDSHW has required ATK to conduct emissions testing of Class 1 3 matenals in order to establish
emission factors for the major class of propellants (Class 1 3) produced at the ATK facilities The goal of
the emission testing program was to identify and quantify emissions from OB of these Class 1 3
propellant waste (PW) matenals
The Open Detonation Open Burn Improved (ODOBI) test chamber was used to determine emission
factors for airborne compounds from three different compositions of ATK Class 1 3 PW matenals The
tests were conducted from June 7 to 15, 2006 (URS, 2007) Emissions were measured from the
simulated OB events ofthe following propellant waste test items
• Test Matenal 1 - PW100 100% ammonium perchlorate (AP) propellant
• Test Matenal 2 - PW85-15 85% AP propellant + 15% trash
• Test Matenal 3 - PW65-35 65% AP propellant + 35% trash
The airborne target compounds measured included
Carbon dioxide (C02),
Carbon monoxide (CO),
Carbonyis,
Dioxins/Furans,
Hydrogen chloride (HCI), chlonne (Ci2), and ammonia (NH3),
Hydrogen cyanide (HCN),
Metals
Nitrogen oxides (NOx),
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Particulate matter smaller than 2 5 microns (PM2 5),
Particulate matter smaller than 10 microns (PM10),
Perchlorates,
Semivolatile organic compounds (SVOCs),
Sulfur dioxide (S02),
Total suspended particulates (TSP),
Tracer compound sulfur hexafluonde (SF6), and
Volatile organic compounds (VOCs)
Three test items were studied The first matenal was 100% Class 1 3 propellant The other two test
matenals consisted of a mixture of Class 1 3 propellant blended with different percentages of matenals
such as cloth paper, paper wipes, plastics and cleaning items
Average emission factors were developed from the test results and are shown in Table 5 for each
detected compound after applying the "non-detect rules" ach emission factor represents the mass
produced per pound of the test item Since many of the compounds measured may be present in
ambient air, corrected emission factors were determined by subtracting the background concentrations
The emission factors were also adjusted to compensate for dilution that occurred dunng sampling A
listing of the average and maximum EFs used in this analysis are presented in Table 5 The OBODI
testing did not determine the size distnbution of particulate emissions A condense summary of the test
results are presented below
Particulate Matenal - Particulate matenal and inorganic gases were the pnmary emissions from ail items
The PW85-15 trash sample produced the highest particulate emissions PM2 5 constituted 30-40% ofthe
total particulate emissions from ali test items
Metals and Perchlorates - Aluminum was the predominant metal product in the air samples from each
test Aluminum was a constituent of each test item Other metals were found at lower levels The highest
metal emissions were produced by the PW85-15 sample Perchlorates were not detected in any of the
test samples
VOCs and SVOCs - SVOCs were emitted at low levels VOCs were generally measured at higher levels
than SVOCs The PW65-35 sample produced the highest concentration of VOCs Non-methane organic
compounds constituted the majority ofthe VOC emissions
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Dioxms/Furans - Most dioxin/furan isomers were reported at picogram levels Some isomers in the
PW85-15 and PW65-35 samples were reported at nanogram levels The highest emissions were
measured from the PW85-15 trash sample
Carbonyis - Carbonyis were generally measured at very low levels in most samples
HCi/CI2/NH3 and HCN - HCI concentrations were highest in the pure propellant sample Chlonne levels
were not high enough to be distinguished from the backgrounds and blanks Ammonia and cyanide were
found at low levels in some samples
Continuous Emissions Momtonng - The pnmary gas-phase compound from ali test items was C02 Very
little CO was produced in each test, indicating good combustion of the trash samples NOx was
measured at low levels in aii tests S02 was too low to be reliably measured
At the request of ATK, OB and OD operations at the M-136 and M-225 units were evaluated on the basis
ofthe average and maximum emission factors detemmned from the OBODI tests shown in Table 5
2 10 OTHER MODELING ASSUMPTIONS FOR M-136 AND M-225
The following assumptions were used in the preliminary modeling analysis for the M-136 and M-225
treatment units
M-136 Treatment Unit
• OB source release is quasi-continuous (volume source)
• OD source release is instantaneous (volume source)
• Assume the 4 source areas (A, B, C, and D) are at the same elevation as Burn Station 1-12, Elev =
4,587 feet above mean sea level (MSL) to consolidate gravitational settling modeling for all 3 sources
in a smgle model run The net elevation difference between the 3 source locations is only 36 feet
(11 meters)
• Setup source groups to give contnbution from each M-136 source
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• Source dimensions for OB at Ml 36 are based on average pan size for that treatment area
- Average dimension of pans in Bum Station 1-12 = 8' x 13'
- Average dimension of pans in Burn Station 13 = 6' x 9'
- Dimension of Burn Station 14 rocket motor assumed to 5' x 50'
• The release height for OB = 1 0 meters at Source 1 (Burn Station 1-12) and Source 2 (Burn
Station 13) The Source 3 (Burn Station 14) release height = 20 meters
• Release height for OD is calculated by the model based on 0 0 meter release
• Assume 1 5 meter diameter for OD pit
• Gas, particulate, particulate bound, and deposition phase modeling was conducted using a unit
emission factor of 1 0 lb/lb
• Default OBODM particulate and mass distnbutions for particulate and deposition modeling
M-225 Treatment Unit
• Both sources have the same coordinate and elevation, elevation = 4,597 feet above mean sea level
to consolidate gravitational settling modeling for both sources in a single model run
• Include both sources in single OBODM run
• Each source configuration based on average pan size
- Assume 1 5 meter diameter for OD Pit
- For OB at M225, average dimension of pans = 6' x 17'
• Release height for OB = 1 0 meters
• Release height for OD is calculated by the model based on 0 0 meter release
• OB source release quasi-continuous (volume source)
• OD source release instantaneous (volume source)
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• Gas, particulate, particulate bound, and deposition phase modeling was conducted using a unit
emission factor of 1 0 lb/lb
• Default OBODM particulate and mass distnbutions for particulate and deposition modeling
2 11 DEPOSITION MODELING
In addition to calculating 1-hour and annual average ADFs, OBODM also calculated total annual
deposition ADFs in support of the human health nsk assessment Due to the limitations of OBODM,
separate model runs were required for gas and particulate deposition phases The deposition
mechanisms applicable to the M-136 and M-225 treatment units included the following
• Gravitational settling of particulates
• Nongravitational dry deposition of particulates and gases
The sum of these two deposition mechanisms were assumed to represent total deposition
It IS important to note that wet deposition is not calculated by OBODM This deposition mechanism is not
applicable in the case of ATK because treatment operations are not conducted dunng precipitation
events
OBODM has the capability to calculate gravitational settling of particulates when run in the particulate
mode (e g , all emissions are assumed to be particulates) The input requirements for OBODM deposition
modeling include particle size and mass distnbutions, median particle size, and specific gravity for
calculatmg the gravitational settling velocity of a particle Unfortunately, such information is not directiy
available for the M-136 and M-225 treatment units In the absence of available particle size information
for ATK, alternate sources of particle size information were used to establish input parameters for
OBODM deposition modeling
A study conducted by the National Aeronautics and Space Administration (NASA, March 1973)
investigated the particle size distnbution (but no standard deviation) for aluminum oxide particles from
rocket propellants Aluminum oxides are a combustion product of the matenals treated at M-136 and
M-225 The results of the NASA study indicated a mean mass aluminum oxide particle size of
12 3 micrometers ([im)
In addition, a study conducted by the Department of Energy (DOE 1984) provided the following
information regarding particle diameter ranges for a vanety of particle types
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Oil smoke 0 03 to 1 pm
Fly ash 1 to 200 pm
Metallurgical dusts 0 001 to 100 pm
Carbon black 0 01 to 0 5 pm
Combustion nuclei 0 01 to 0 1 pm
The DOE study further indicated that the particle density of most combustion products of concern range
from 0 8 to 20 0 g/cm^ In addition, natural coagulation (contact of two or more particles while airborne)
will produce an aggregate particle that contains substantial void space, which would reduce the effective
density to 0 1 or less of the true density of particulate matter A typical density of energetics is 1 6 g/crrfi
By comparison, lead has a density of 11 3 g/cm^ However, if coagulation is considered, the effective
density of OB/OD particles (including metals) would be less than 2 0 g/cm^
Based on this available information, a simple but conservative approach for conducting the deposition
modeling was developed based on the following assumptions
• Assumed density of 2 7 g/cm^ for particulates, which is the density of aluminum Results from the
OBODI testing indicate aluminum to be the most abundant metal in the OB and OD emissions
• Assumed mass median particle diameter of 12 3 pm (based on NASA 1973)
• Assumed particle size standard deviation of 2 0 pm in order to account for a reasonable measure of
size distnbution vanability
• Utilize OBODM default logarithmic particle size and mass distnbution based on 10 particle size
categories for particulate modeling
• A separate particle bound mass distnbution was created using guidance found in Section 3 2 3 of the
HHRAP (U S EPA, 2005) in support of the human health nsk assessment
OBODM does not calculate the dry deposition (non-gravitational settling) of particulate and gaseous
emissions However, OBODM modeling results for the gas phase concentrations (e g , ali emissions are
in the gas phase) were used to estimate non-gravitationai deposition (e g , pg/m^) This calculation was
accomplished as follows
Nongravitational Dry Deposition (pg/m^) = Air Concentration (pg/m^) x Deposition Velocity (m/sec)
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This approach is consistent with HHF^P (U S EPA, September, 2005) and OBODM (U S Army, Apnl
1998) guidance, and is also considered to be conservative because the calculated air concentration is
based on a non-depleted plume (eg, no mass has been removed for the treatment plume) The
deposition velocity assumed in the preliminary modeling analysis for the calculation of non-gravitationai
dry deposition was 0 03 meters/second (m/sec), which is the default value specified in the HHRAP (U S
EPA, September 2005) guidance
Therefore, total annual deposition m this analysis is represented by the following
Total Deposition (pg/m^) = Gravitational Settling (pg/m^) + Non-gravitationai Dry Deposition (pg/m^)
Table 6 provides a summary of the dry deposition and gravitational settling parameters that were used to
evaluate M-136 and M-225 treatment unit emissions in OBODM
2 12 RECEPTOR NETWORKS
All receptors used in this preliminary modeling analysis are based on a Cartesian grid system (x y) Two
types of receptor networks were used in the analysis general and discrete A general receptor network is
designed to determine the maximum short term and long term ground level concentrations for a source
Separate general receptor grids were developed for each ATK treatment unit due to their separation
distance (approximately 9 km) Each receptor is assigned a Universal Transverse Medcator (UTM)
northing and easting coordinate, and terrain elevation This data was obtained from USGS Digital
Elevation Maps (DEM) grids of 1 24,000 at a resolution of 1 meter
The discrete receptor network consisted of special human health receptors that are of concern to
UDSHW' and were evaluated in the human health nsk assessment
2 12 1 General Receptor Networks
The general receptor network for each treatment unit extended out to 10 km and is made up of two
separate sub-networks that have different receptor spacing increments For example, the receptor grid
spacing from the source out to a distance of 3 kilometers is 100 meters The receptor spacing from 3 km
out to 10 km IS 500 meters
There were no general gnd receptors located beyond 10 km because modeling expenence with OB/OD
sources has shown that the maximum short term and long term impacts occur well within 10 km (usually
within 3 km) of the source Due to the large separation distance between the M-136 and M-225 treatment
units, separate general gnd systems were established for M-136 and M-225 treatment units The
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proposed 0-3 and 3-10 km general gnd networks for the M-136 and M-225 treatment units are shown in
Figures 1 through 4
It IS important to note that the general gnd extending from the M-136 and M-225 treatment areas out to
3 km includes on-site receptors At the request of UDSHW, these receptors were used to evaluate on-
site worker exposure for non-OB/OD workers located outside of the quantity-distance (Q-D) areas
imposed by ATK
2 12 2 Discrete Receptor Network
Discrete receptors are defined as special receptors that exist withm and beyond the ATK boundary
These locations include the facility boundary, nearby residential dwellings, a local dairy farm, the closest
population centers and worker exposure at an offsite commercial businesses (AutoLiv)
The following is a list of discrete receptors that were evaluated in this preliminary modeling analysis
• The Adam's Ranch, which is the closest domestic dwelling to M-136 and is located approximately
3 km south-southwest of M-136
• The Holmgren Ranch Pond, which is the closest domestic dwelling to the M-225 and is located
approximately 2 km east-southeast of M-225
• Four facility boundary receptors that were selected based on the annual prevailing wind directions
that were measured over a five-year penod (1997 through 2001) at the M-245 meteorological
momtonng station
• AutoLiv Facility This is the offsite commercial business that is located between the M-136 and
M-225 treatment units
• Chnstensen Residence This residential dwelling is located due north of ATK On-site observations
by ATK personnel indicate that M-136 plume frequently travel in this direction
• Blue Creek perennial stream, which runs along the western boundary of M-136
• The Thiokol Ranch Pond, which is located approximately 14 km southwest of M-225, and
• Howe Dairy Farm located approximately 8 km due north of the ATK property boundary
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Ali discrete receptors listed above are shown in Figure 5
2 13 METEOROLOGICAL DATA
The meteorological data requirements for OBODM are histoncal hourly averages of wind speed and wind
direction atmosphenc stability class, air temperature, and urban or rural mixing height These
meteorological parameters represent a combination of surface and upper air data and are available from
several different sources including the National Weather Service (NWS), military installations or as part of
an on-site measurement program
The meteorological data used in an air dispersion modeling analysis should be selected based on spatial
and climatological representativeness, as well as, the ability of the data to characterize the transport and
dispersion in the area of concern Spatial and geographical representativeness is best achieved by using
validated on-site meteorological data As a result, site-specific measured data is therefore preferred as
modeling input (U S EPA, September 2000), provided appropriate instrumentation and quaiity assurance
procedures are followed and the data is compatible with the requirements of the dispersion model
2 13 1 Surface Data
One year (1997) of on-site meteorological data collected at the ATK M-245 meteorological momtonng
station was used in the preliminary dispersion modeling analysis ATK operates the on-site monitoring
station approximately 1 5 km southwest of the M-225 treatment unit at an elevation of about 5,000 feet
amsi The momtonng station is operated in accordance with the U S EPA momtonng guidance for the
collection of on-site meteorological data (U S EPA, 2000)
The monitoring station consists of a 10-meter tower that collects the following data at the 10-meter level
Wind speed
Wind direction
The standard deviation of the horizontal wind (sigma theta)
Temperature
Relative humidity
Barometnc pressure, and
Solar radiation
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The meteorological parameters used by the OBODM are wind speed, wind direction, and air temperature
The data recovery for these parameters in 1997, after validation, were 94 percent or above which
exceeds the U S EPA recommended minimum cntena for an annual meteorological database
A wind rose showing the frequency distnbution of wind direction for 1997 at the M-245 meteorological
momtonng station is presented in Figure 6
2 13 2 Upper Air Observations (Mixing Height Data)
Upper air data, also known as mixing height data, is required to run OBODM Twice daily mixing heights
available from upper air sounding stations are used by the meteorological preprocessor program
(PCRAMMET) to calculate hourty rural or urban mixing height for input into OBODM Upper air sounding
data IS typically obtained from NWS upper air reporting stations The number of upper air reporting
stations in the United States is limited due to operational requirements and budgetary constraints, which
play a key role in determining where and how many stations are operated As a result, this condition can
severely limit the availability of upper air reporting stations near a source
The closest NWS upper air reporting station to ATK is located in Salt Lake City, which is about 60 miles
south of ATK The next closest NWS upper air reporting station is located in Lander, Wyoming, which is
about 190 miles northeast of ATK Although considerable site-to-site vanability is possible for
measurements taken close to the surface as compared to upper air measurements, the upper air
sounding measurements from Salt Lake City are considered generally representative of a much larger
spatial domain, which includes the northern Utah valley
2 13 3 Meteorological Preprocessor
The surface observation and mixing height data files for the 1997 annual penod were preprocessed for
input into OBODM using the PCRAMMET meteorological program, as recommended in the HHRAP
guidance (US EPA, July 1998 and August 1999) The format of the PCF5AMMET output file is
compatible for use with OBODM The input requirements for PCRAMMET include hourly surface
observations of year, month, day, hour, ceiling height, wind speed wind direction, dry bulb temperature,
and opaque cloud cover in CD144 format PCRAMMET requires data for ali input vanables and will not
run if data is missing withm an hourly record As a result substitution data must be used to fill data gaps
In the case of the M-245, opaque cloud cover and ceiling height are not measured As a result, additional
meteorological data had to be acquired from a representative, local source
The first class reporting station located at Ogden Air Force Base in Ogden, Utah was selected as the
local source of missing data This reporting station is considered to be the closest, most representative
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and readily available site for providing substitute data based on its location relative to ATK, climatology,
valley location relative to surrounding terrain and similar land use The Ogden reporting station is
located approximately 25 miles south of ATK within the northern Utah valley Observations missing in
1997 from the M-245 momtonng station were substituted in accordance with U S EPA data substitution
guidance (U S EPA 1992) The rural mixing heights were used in this modeling analysis
2 14 OBODM POST-PROCESSING
All OBODM output flies required post-processing to review the model input/output, determine the
maximum impacted on-site and off-site receptors associated with each treatment unit, and summarize the
results The post-processing involved the following steps
• Review of aii output files to venfy input data and model results
• Determine the flat and complex terrain general grid receptors having the maximum on-site and off-
site, 1-hour and annual average air concentrations, as well as the maximum offsite deposition values
for each treatment unit
• Transformation of receptor 1-hour and annual average concentration and deposition values based on
OBODM assumed treatment quantity scenarios versus the allowable maximum 1-hour and annual
treatment quantities For example, suppose the maximum OBODM annual air concentration for
Receptor A was calculated to be 25 pg/m^ based on an OBODM modeled annual treatment quantity
of 1,000,000 pounds If in reality the source has a maximum allowable treatment quantity of only
750,000 pounds per year, then the transformed maximum air concentration would be equal to
Transformed air concentration = (25 pg/m^) x (750,000/1,000,000) = 18 75 pg/m^
• Convert transformed maximum 1-hour concentrations to averaging periods regulated by the National
Ambient Air Quality Standards (NAAQS) and Occupational Safety and Health Administration (OSHA)
worker exposure limits
• Create gas, particulate, particulate bound, and deposition ADF files for input into the Lakes
Environmental IRAP-h® nsk assessment model based on the OBODM results for short term and long
term concentrations, and long term total deposition at maximum and discrete receptors
• Evaluate air impacts on the basis of average and maximum emission factors
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2 15 POLLUTANT AVERAGING PERIODS
OBODM calculated air concentrations for 1-hour and annual average penods The 1-hour air
concentrations were used to estimate air concentrations for longer averaging penods that are associated
with applicable air quaiity standards The relevant air quaiity standards are the criteria pollutants that
were included in the contaminants of potential concern (COPC) list for OB and OD emission factors,
which are discussed in Section 3 0 In the case of both OB and OD, the applicable cntena pollutants
were carbon monoxide, nitrogen oxides (as nitrogen dioxide), inhalabie particulate matter (PM10) and
respirabie particulate matter (PM 2 5) The air quaiity standards associated with these cntena pollutants
include 1-hour, 8-hour 24-hour, and annual averaging penods It is important to note that these ambient
air quaiity standards are only applicable at and beyond the facility boundary
In the case of on-site air concentrations 2008 OSHA time-weighted-average exposure concentration
values were used to evaluate on-site worker exposure at the predicted maximum on-site receptor for
each treatment unit These time-weighted average (TWA) values are based on an 8-hour exposure
penod
OBODM 1-hour air concentrations were used to calculate air concentrations for longer averaging periods
usmg the assumption that only one treatment event occurs dunng an 8-hour or 24-hour averaging penod
For example, if the OBODM 1-hour PM10 concentration at a receptor was calculated to be 120 pg/m^,
then the corresponding 8-hour and 24-hour concentrations would be 15 0 (120/8) and 5 0 (120/24) pg/m^
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3 0 AIR DISPERSION MODELING RESULTS
The results of the OBODM preliminary air dispersion modeling analysis were used to support the human
health nsk assessments, as well as, evaluate the modeling results in companson to NAAQS and worker
exposure cntena established by OSHA
The State of Utah has adopted the NAAQS The receptors addressed in the analysis included discrete
human health receptors, as well as a general receptor network for determining the maximum on-site and
off-site receptors associated with each treatment unit These receptors are identified in Section 2 12
This section discusses the results of the preliminary dispersion modeling analysis relative to the
identification of maximum on-site and off-site receptor locations, a companson of treatment unit air quaiity
impacts to NAAQS and OSHA worker exposure cntena, and the worst case meteorological conditions that
were associated with the maximum, 1-hour on-site and off-site receptor locations A discussion of the
human health nsk assessment is presented in Section 4 0
3 1 MAXIMUM ON-SITE AND OFF-SITE RECEPTORS
The location of the maximum 1-hour and annual on-site and off-site receptors for gas, particulate, and
deposition phase emissions for the M-136 and M-225 treatment units are shown in Figures 7 and 8,
respectively
3 2 COMPARISON TO NAAQS
The results of the OBODM analysis using average and maximum OBODI emission factors were
compared to the NAAQS for ali discrete and off-site maximum receptors The results of this companson
are shown in Tables 7 through 20 for each individual treatment unit source and the combined total of
individual sources per treatment unit and for both treatment units The pollutant and averaging penod
address in each Table is summanzed below
• Tables 7 and 8 1-hour carbon monoxide concentrations based on average and maximum EFs,
respectively
• Tables 9 and 10 8-hour carbon monoxide concentrations based on average and maximum EFs,
respectively
• Tables 11 and 12 24-hour PM 2 5 concentrations based on average and maximum EFs, respectively
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• Tables 13 and 14 24-hour PM 10 concentrations based on average and maximum EFs respectively
• Tables 15 and 16 Annual PM 2 5 concentrations based on average and maximum EFs, respectively
• Tables 17 and 18 Annual PM 10 concentrations based on average and maximum EFs, respectively
The companson to NAAQS conservatively assumed that aii treatment unit sources were operating
simultaneously and impacted the receptor within the applicable averaging penod In reality, it is highly
unlikely that ali sources would operate simultaneously and that meteorological conditions would be such
to transport ali treatment unit emissions directly to the same receptor within the exposure penod
Tables 7 to 10, respectively, indicate that the maximum 1-hour and 8-hour carbon monoxide
concentrations contnbuted by M-136 and M-225 do not cause an excursion of the 1-hour and 8-hour
NAAQS
Tables 11 through 18 indicate no excursions of the 24-hour or annual PM2 5 and PM 10 NAAQS
3 3 ONSITE EXPOSURE CONCENTRATIONS
The OBODM calculated employee exposure concentrations for the M-136 and M-225 treatment units are
shown in Tables 20 through 23 The exposure concentrations calculated by OBODM were compared to
OSHA 2008 8-hour TWA concentration values The 8-hour concentration results for ATK OB/OD
operations from both individual and combined source impacts to respective on-site maximum receptors
were well below all TWA values
3 4 SUMMARY
in general, the results of the preliminary modeling analysis indicate no senous air quaiity problems
relative to NAAQS or OSHA cntena, based on the protocol and average and maximum OBODI emission
factors used in the analysis These results indicate the combined impact of Ml36 and M225 sources to
discrete and maximum impact receptors are well below NAAQSs and OSHA cntena for onsite ATK
workers
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4 0 HUMAN HEALTH RISK ASSESSMENT
This section presents the results of the human health nsk assessment (HHF?A) prepared based on air
emissions modeling conducted in support of a RCRA Subpart X (S-X) permit application for two open
burning/open detonation (OB/OD) units at Thiokol Propulsion, inc, (Thiokol) Bngham City, Utah The
HHRA was requested by Thiokol to provide a preliminary evaluation of the nsks that may be associated
with the OB/OD operations at two source areas (M-225 and M-136) In the air dispersion modeling the
M-225 source area was modeled as 2 emission sources and the M-136 source area was modeled as 4
emission sources Additionally, the preliminary evaluation was conducted to identify cntical air modeling
and nsk assessment assumptions impacting nsk assessment results The results of the preliminary
modeling and HHRA will be used to refine the formal, comprehensive HHRA that will be prepared as part
of the support documentation for the RCRA S-X permit This evaluation is an update of the evaluation
that was performed in Apnl 2003
4 1 METHODOLOGY
The previous 2003 evaluation was conducted per the guidelines established in the U S EPA guidance
document titled. Human Healtli Risk Assessment Protocol for Hazardous Waste Combustion Facilities
(USEPA July 1998) This guidance was updated in September 2005 The major changes in the
updated guidance involved the methodology for dispersion modeling, evaluation of mercury, and new
methodology for estimating the bio-uptake parameters used in the food chain modeling This current
evaluation follows the 2005 guidance
As with the previous 2003 evaluation, nsk estimates were produced using commercially available
software provided by Lakes Environmental, Industrial Risk Assessment Program -Human Health for the
U S EPA OSW Human Health Risk Assessment Protocol (HHRAP), referred to as \RAP-h View At the
request of Thiokol the preliminary HHRA was conducted using the conservative, default assumptions
presented in the guidance and the following site-specific information required by the model
Parameter Value
Ev, Average annual evapotranspiration (cm/yr) 40
1, Average annual irngation (cm/yr) 70
P, Average annual precipitation (cm/yr) 20
RO, Runoff (cm/yr) 2 54
Annual Average Wind Speed (m/s) 4 1
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The site-specific values were obtained from Review and Analysis of Parameters and Assessing Transport
of Environmentally Released Radionuclides through Agriculture by Baes and others (1984) The annual
average wind speed is based on the M245 meteorological station data collected from 1997 to 2002
With the exception of the subsistence fisher and the subsistence fisher child aii receptors specified in the
guidance document were evaluated (e g, child and adult farmers, child and adult residents)
Subsistence fisherman and their children were not evaluated because of the general poor surface water
quality and the intermittent flow of surface water in the vicinity of the treatment units In addition,
subsistence fisherman do not currently exist within the study area and are not expected to be in the study
area in the future Consequently, ingestion of fish and ingestion of surface water (as dnnking water) were
not evaluated At the request of the State of Utah, one receptor not specified in the guidance document,
the mdustnal worker, was also evaluated in the preliminary HHRA The mdustnal worker was assumed to
be located at the AutoLiv Plant incremental lifetime cancer nsks (ILCRs) and hazard indices (His) for the
industrial worker were calculated following U S EPA's Supplemental Guidance for Inhalation Risk
Assessment (U S EPA, January 2009) using U S EPA standard default exposure assumptions (U S
EPA, December, 2002) It was assumed that the mdustnal worker would be exposed 8 hours/day,
250 days/year for 25 years Air concentrations for the industrial worker were calculated with IRAP-h
View
At the request of Thiokol and the State of Utah, chronic and acute nsks (i e, cancer nsks and hazard
indices) were estimated for the discrete receptor locations shown in Figure 5 The discrete receptors
used in the analysis are descnbed in Section 2 12 In general, the discrete receptor locations included
the facility boundary, nearby residential dwellings, the closest population center or town, worker exposure
at the AutoLiv Plant, and maximum 1-hour and annual average on-site and off-site receptor locations
associated with the sources
The toxicity information (i e cancer slope factors [CSFs] and reference doses [RfDs]) presented in IRAP-
h View were reviewed and updated as necessary pnor to nsk estimation Surrogates were used for
chemicals without toxicity cntena Chemicals of potential concern (COPCs) and unit emission rates were
determined for the preliminary HHF^ as descnbed in Section 2 9 Table 23 presents the COPCs
evaluated in this analysis Risks estimates were calculated using both average and maximum emission
rates
4 2 RESULTS OF PRELIMINARY HHRA
The results of the preliminary HHFIA for OB/OD source areas M-225 and M-136 are summanzed in
Tables 24 through 31, and in Appendix A Table 24 presents the overall maximum ILCRs and His for the
selected discrete receptor locations assuming that the sources at both treatment units are operating
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concurrently as planned over time HHF?A results are presented on a source area/unit basis for the
subsistence adult and child farmer, and the child and adult resident on Table 425 These are the
receptors of concern specified in the guidance document ILCRs and His are presented for the mdustnal
worker at the AutoLiv Plant in Table 26 Table 27 presents the nsks by exposure pathway and Tables 28
through 31 presents the chemical-specific nsks for ail the receptors exposed to air emissions from 225A
(OB Treatment) at the M-225 Maximum On-site Gaseous Phase Concentration location Tables 32 and
33 present a companson of 1-hour air concentrations to Utah Department of Air Quality (UDAQ) acute
Toxic Screening Levels (TSLs) for average and maximum emission rates, respectively Tables 34 and 35
present a companson of 24-hour air concentrations to UDAQ chronic/carcinogenic TSLs for average and
maximum emission rates, respectively Appendix A presents the hazard quotient (HQ) calculated for
each COPC and the total HI calculated for the acute inhalation nsk evaluation for average and maximum
emission rates, respectively The following items summanze the results of the preliminary HHRA
• Risk estimates associated with emissions from the source area M-225 Unit A exceeded those
calculated for other source areas The lowest nsk estimates were associated with emissions from the
source area M-136 Unit D In the previous 2003 evaluation, nsk estimates were highest for emissions
from the source area M-225 Unit A and lowest with emissions for the source area M-136 Unit B
Source area M-136 Unit D was not evaluated in the previous evaluation
• With the exception of nsk estimates developed for maximum or average emissions hypothetically
impacting future residents or farmers at the M-225 Unit A Maximum On-site Gaseous Phase
Concentration location, ILCRs do not exceed the U S EPA 10"^ to 10"^ target cancer nsk range (i e , a
one-in-one ten thousand to one-in-one million additional chance of developing cancer) typically used
to evaluate the need for environmental remediation or action In the previous 2003 evaluation, the
maximum ILCR was also associated with the M-225 Unit A maximum on-site location Ail HQs and
His for both the average and maximum emission rates are less than 1 indicating that adverse non-
carcinogenic health effects are not anticipated under the conditions established in the nsk
assessment
• The ILCRs based on maximum emission rates for receptors at the M-225 Unit A Maximum On-site
Gaseous Phase Concentration location were 6 3 x 10"® for the adult farmer, 2 2 x 10® for the child
farmer, 3 1 x 10® for the adult resident, and 1 5 x 10"® for the child resident The ILCRs based on
average emission rates for receptors at the M-225 Unit A Maximum On-site Gaseous Phase
Concentration location were 3 7 x 10 ® for the adult farmer, 1 3 x 10 ® for the child farmer, 1 8 x 10 ® for
the adult resident, and 8 6 x 10^ for the child resident However, the on-site farmers and on-site
residents were evaluated for informational purposes only Currently, the site is not used for farming
or residential purposes nor is it expected to be used for farming or residential purposed in the future
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In addition, if the site was developed for farming or residential purposes in the future then most likely
the source areas would be removed, therefore potential nsks to child and adult farmers and child and
adult residents would be less than those estimated in this analysis Ingestion of
3,3'-dimethylbenzidine and benzidine in home grown produce were the major contnbutors to the ICLR
for the receptors at the M-225 Maximum On-site Gaseous Phase Concentration location In the
previous evaluation, dioxms/furans were the major contnbutors to the ILCRs ILCRs for
dioxins/furans were lower in this evaluation as compared to the previous evaluation
• Estimated ILCRs were highest for the adult farmer and lowest for the child resident Estimated His
were highest for the child farmer and child resident and lowest for the adult farmer and adult resident
• Concentrations of all chemicals were less than the UDAQ acute and chronic/carcmogemc TSLs
• Estimated ILCRs and His for mdustnal workers at the AutoLiv Plant were within acceptable levels
4 3 RECOMMENDATIONS FOR FINAL HHRA
Based on the results of the preliminary HHRA the following is recommended for the Final HHRA
• With the exception of nsk estimates for receptors at the M-225 Maximum On-site Gaseous Phase
Concentration receptor location the results of this preliminary evaluation indicate that ILCRs and His
are less than U S EPA acceptable levels when the conservative default assumptions presented in
the combustion guidance are evaluated However, as discussed above, this receptor is not a
plausible receptor under current and expected future site usage Additionally, if the site was to be
developed for farming or residential purposes in the future, it is likely that the source areas would be
removed Therefore, it is recommended that nsk estimates for hypothetical future residents/farmers at
on-site receptor locations (eg, M-136 Maximum On-site locations, M-225 Maximum On-site
locations, and AutoLiv receptor locations) be presented in the uncertainty section of the Final HHRA
prepared for the Thiokol Propulsion, Inc project
• Risk estimates for the boundary and off-site receptor locations may be evaluated using the default
receptors (i e , child and adult farmers, child and adult residents) and conservative default exposure
assumptions presented in the combustion guidance Although some of the default assumptions
presented in the guidance are very conservative, the use of such assumptions in this preliminary
evaluation did not result in nsk estimates exceeding U S EPA or State of Utah benchmarks (except as
noted above) Consequently, negotiation of alternative (potentially more reasonable) values is not
necessary However, the Uncertainty Analysis of the nsk assessment should provide the nsk
040911/P 4-4
DRAFT
APRIL 2009
managers with a quaiitative/semi-quantitative understanding of the degree to which the use of
conservative modeling or exposure assumptions impact the resulting nsk estimates
Risk estimates for mdustnal workers located at the AutoLiv facility may be developed using the same
exposure assumptions that were used in this evaluation
040911/P 4-5
DRAFT
APRIL 2009
REFERENCES
Auer 1978 "Correlation of Land Use and Cover with Meteorological Anomalies" Journal of Applied
Meteorology, Volume 17, May 1978
Baes, CF,RD Sharp AL Sjoreen, and R W Shor 1984 "Review and Analysis of Parameters and
Assessing Transport of Environmentally Released Radionuclides Through Agncuiture" Oak Ridge
National Laboratory Oak Ridge, Tennessee
NASA 1973 "NASA/MSFC Multilayer Diffusion Models and Computer Program for Operational
Prediction of Toxic Fuel Hazards", Dumbald, R K , Bjorkiund, J R HE Cramer Company for the National
Aeronautics and Space Administration, Marshall Space Flight Center, Alabama
DOE 1984 "The Toxicological Effects of Non-nuclear Pollutants", Section 17-17, Particulates,
Department of Energy Publication "Atmosphenc Science and Power Production Office of Scientific and
Technical information. United States Department of Energy
URS Group Inc, 2007 "Sampling Results for Emission Charactenzation of Open Burning Waste
Propellant Matenals', prepared for ATK Launch Systems under contract with U S Army Dugway Proving
Ground Draft, August, 2007
U S Army, 1997 Open Burn/Open Detonation Dispersion Model (OBODM) User's Guide", H E Cramer
Company Sandy, Utah 84091-0411, and West Desert Test Center, U S Army Dugway Proving Ground,
Dugway, Utah, DPG Document No DPG-TR-96-008a, July 1997
U S EPA (U S Environmental Protection Agency) July 1988 Human Health Risk Assessment Protocol
for Hazardous Waste Combustion Facilities EPA530-D-98-001 Office of Solid Waste and Emergency
Response, Washington, D C
US EPA 1992 "Screening Procedures for Estimating the Air Quality Impact of Stationary Sources,
Revised Office of Air and Radiation, EPA-454/R-92-019
U S EPA 1995a "User's Guide for The Industnal Source Complex Dispersion Models, Volumes I and
11" Office of Air Quality Planning, and Standards Emissions, Momtonng, and Analysis Division,
Research Tnangle Park, North Carolina EPA-454/B-95-003a
040911/P R-1
DRAFT
APRIL 2009
USEPA 1995b "PCFJAMMET User's Guide" Office of Air Quality Planning and Standards
Emissions, Momtonng, and Analysis Division Research Tnangle Park, North Carolina October
U S EPA 1996 "Guideline on Air Quaiity Models , Title 40, Code of Federal Regulations Part 51,
Appendix W September 1996
U S EPA 2000 ' Meteorological Momtonng Guidance for Regulatory Modeling Applications, Final" EPA-
530-R-05-006, September, Office of Air Quaiity Planning and Standards Research Tnangle Park, North
Carolina
U S EPA, December 2002 Supplemental Guidance for Developing Soil Screening Levels for Superfund
Sites OSWER 9355 4-24
U S EPA 2005 "Human Health Risk Assessment Protocol for Hazardous Waste Combustion Facilities",
Office of Solid Waste and Emergency Response, EPA530-D-98-001A, July 1998
U S EPA, September 2005 Human Health Risk Assessment Protocol for Hazardous Waste Combustion
Facilities EPA530-R-05-006 Office of Emergency and Remedial Response, Washington, D C,
September
U S EPA January 2009 Risk Assessment Guidance for Superfund, Volume I Human Health Evaluation
Manual (Part F, Supplemental Guidance for Inhalation Risk Assessment), Final Office of Superfund
Remediation and Technology Innovation, Washington, DC 20460 EPA-540-R-070-002, OSWER
9285 7-82
040911/P R-2
DRAFT
Table 1
M-136 Risk Assessment Source Area
Wastes Treated, Treatment Limits, and Model Quantity
Model
Sources
Burn Stations Reactive Waste
Categories that
are treated
Model
Quantity
ATK Established Daily Quantity
Limits
ATK Total
Annual Burn
Limit (lbs)
Source 1 123456789
10 11 12
A, B C D E F G
H
60 000 lbs 106,500 lbs per day consisting of
• 1 1 pure
propellant/contaminated
matenal from all burn stations
or
• 1 3 pure
propellant/contaminated
matenal from all burn stations
or
• HMX/RDX*
propellant/contaminated
matenal from all burn stations
8 500 000 106,500 lbs per day consisting of
• 1 1 pure
propellant/contaminated
matenal from all burn stations
or
• 1 3 pure
propellant/contaminated
matenal from all burn stations
or
• HMX/RDX*
propellant/contaminated
matenal from all burn stations
106,500 lbs per day consisting of
• 1 1 pure
propellant/contaminated
matenal from all burn stations
or
• 1 3 pure
propellant/contaminated
matenal from all burn stations
or
• HMX/RDX*
propellant/contaminated
matenal from all burn stations
Source 2 13 A B C D E F G
H
2 000 lbs 4 000 lbs per day consisting of 500 000 A B C D E F G
H
• 1 1 pure
propellant/contam i nated
material for one burn station
or
• 1 3 pure
propellant/contaminated
matenal for one burn station
or
• HMX/RDX*
propellant/contaminated
matenal for one burn station
• 1 1 pure
propellant/contam i nated
material for one burn station
or
• 1 3 pure
propellant/contaminated
matenal for one burn station
or
• HMX/RDX*
propellant/contaminated
matenal for one burn station
• 1 1 pure
propellant/contam i nated
material for one burn station
or
• 1 3 pure
propellant/contaminated
matenal for one burn station
or
• HMX/RDX*
propellant/contaminated
matenal for one burn station
Source 3 14 A B C D 7 000 lbs 15 000 lbs per day consisting of 1 000 000
• 1 1 rocket motor
or
• 13 rocket motor
• 1 1 rocket motor
or
• 13 rocket motor
iVI136 Maximum Daily and Annual Treatment Quantities 106 500 lbs 10 000 000 lbs
'Assumes HMX/RDX matenals do not need a separate set of EFs and can use either 1 1 or 1 3 emission factors
M136 conducts one treatment event per day
Model quantity represents a typical or average treatment quantity for a source area Maximum treatment quantities will be addressed by
multiplying the air dispersion factors (ADFs) from OBODM by the ratio of the maximum/modeled treatment quantity For example, if the OBODM
ADF for the 1-hour averaging penod is 1 0 for a modeling quantity of 60,000 lbs and the maximum allowed quantity is 100, 000 lbs, then the
maximum 1-hour ADF = 1 0 (1-hour ADFmodeied) x (100,000/60,000) = 1 66667
DRAFT
Table 2
M-225 Risk Assessment Source Areas
Wastes Treated, Treatment Limits, and Model Quantities
Model
Sources
Burn
Stations
Reactive Waste
Categories that
are treated
Model
Quantity
ATK Established Daily
Quantity Limits
ATK Total
Annual
Burn Limit
(lbs)
Source 1*
Open
Burning
1.2,3,4 A, B, C, D, E, F,
G, H
600
lbs/day
2,000 lbs/day consisting of
• 500 lbs/ tray of 1 1 or
1 3 pure propellants
(1 tray/burn station)
or
• 1,000 lbs/tray of 1 1 or
1 3 pure propellant and
contaminated matenal
(1 tray/burn station)
8,000 lbs
Source 2
Open
Detonation
1 D and G 200
lbs/day
500 lbs/day consisting of
• Reactive Waste Profile
Numbers PR 20, PR
44, PR 48, PR 49, and
PR 53
2,400 lbs
M225 Maximum Daily and Annual Treatment Quantities 2,500 lbs 10,400 lbs
* Assumes Source 1 will use same 1 1 and 1 3 emission factors used at Ml36
M225 conducts treatment once per month
Model quantity represents a typical or average treatment quantity for a source area Maximum treatment
quantities will be addressed by multiplying the air dispersion factors (ADFs) from OBODM by the ratio of
the maximum/modeled treatment quantity For example, if the OBODM ADF for the 1-hour averaging
penod IS 1 0 for a modeling quantity of 60,000 lbs and the maximum allowed quantity is 100, 000 lbs, then
the maximum 1-hour ADF is 1 0 (1-hour ADFmodeied) x (100,000/60,000) = 1 66667
TABLE 3
M-136 OPEN BURNING SOURCE PARAMETERS
ATK
BRIGHAM CITY, UTAH
Source Parameter M-136 Source A-M-136 Source B -M-136 Source C -M-136 Source
OB OB OB CD-OD
Treatment Operations OB in Pans OB in Pans OB m Pans OD in Pits
Burn Stations 1 -Burn Station 13 Burn Stations 14 Burn Stations 13
12^ or 14
Location Center of Bum Center of Burn Center of Burn Center of Burn
Station Area Station Station Station
Number of sources 1 1 1 1
Source Release Type Quasi-continuous Quasi-continuous Quasi-continuous Instantaneous
Burn/Release 300 seconds 300 seconds 300 seconds 25
Duration (OBODM
calculated based on
source type)
Source Configuration Volume Volume Volume Volume
Effective Release 1 meter 1 meter 1 meter 0 meters
Height (m)
Heat Content 1,471 cai/g 1,471 cal/g 1,471 cai/g 1,471 cai/g
Number of treatment 1 per hour 1 per hour 1 per hour 1 per hour
events (per day) between 1000 between 1000 between 1000 between 1000
and 1800 hours and 1800 hours and 1800 hours and 1800 hours
Number of treatment
days (per year)
365 days 365 days 365 days 365 days
Unit emission factor 1 0 1 0 1 0 1 0
TABLE 4
M-225 OPEN BURNING AND OPEN DETONATION
SOURE PARAMETERS
ATK
BRIGHAM CITY, UTAH
Source Parameter M-225 Source A - OB M-225 Source B - OD
Treatment Operations OB in Pans OD in an Uncovered Pit
Location Center of M-225 Unit Center of M-225 Unit
Number of sources 1 1
Source Release Type Quasi-continuous Instantaneous
Burn/Release Duration
(OBODM calculated based
on source type)
300 seconds 2 5 seconds
Source Configuration Volume Volume
Effective Release Height
(m)
1 meter Calculated by OBODM
Source Diameter NA 1 5 meters
Heat Content 1,471 cal/g 1,471 cai/g
Number of treatment
events (per day)
1 per hour between
1000 and 1800 hours
1 per hour between
1000 and 1800 hours
Number of treatment days
(per year)
All Ail
Unit emission factor 1 0 1 0
Table 5
Average and Meucimum Emission Factors Based on
OBODI Emissions Testing
ATK
Bngham City, Utah
Page 1 of 7
Target Analyte Average EF
(lb/lb)
Maximum EF
(lb/lb)
Particulates
TSP 9 5E-02 1 3E-01
TSP(M201A) 7 6E 02 1 OE-01
PM10 6 7E-02 9 3E-02
PM2 5 3 4E 02 4 8E-02
Metals
Aluminum 2 7E 02 3 8E-02
Antimony 1 2E-05 2 3E-05
Arsenic 1 7E 07 2 5E-07
Banum 2 5E-06 3 3E 06
Beryllium 5 7E-08 7 5E 08
Cadmium 1 6E-07 2 IE 07
Chromium 9 7E-06 1 2E-05
Cobalt 1 7E-07 2 1E-07
Copper 8 OE-06 1 5E-05
Lead 1 OE 05 2 3E-05
Magnesium 9 3E 06 1 7E-05
Manganese 2 5E 05 5 OE-05
Mercury 2 OE-08 2 5E-08
Nickel 1 8E-05 2 2E-05
Phosphorus 6 9E-05 9 7E-05
Selenium 8 2E-07 1 1E-06
Sliver 3 9E-07 5 6E 07
Thallium 1 1E-06 1 4E 06
Zinc 7 2E-06 1 7E-05
Perchlorates 1 3E 07 1 7E-07
Table 5
Average and Maximum Emission Factors Based on
OBODI Emissions Testing
ATK
Brigham City, Utah
Page 2 of 7
Target Analyte Average EF
(lb/lb)
Maximum EF
(lb/lb)
SVOCs
1 2 4 5 Tetrachlorobenzene 1 4E-07 1 8E 07
1 2 4-Tnchlorobenzene 1 7E-07 2 2E-07
1 2-Dichlorobenzene 1 5E 07 1 9E-07
1 2 Diphenylhydrazine 1 4E-07 1 8E-07
1 3 5-Tnnitrobenzene 1 4E 07 1 8E-07
1 3-Dichlorobenzene 1 6E-07 2 1E-07
1 3 Dinitrobenzene 1 5E-07 1 9E 07
1 4-Dichlorobenzene 1 5E 07 2 OE-07
1 -Chloronaphthalene 1 5E-07 2 1E-07
1 Naphthylamine 2 9E-06 3 7E-06
2 3 4 6-Tetrachlorophenol 1 9E-07 2 4E-07
2 4 5-Tnchlorophenol 3 7E 07 4 8E-07
2 4 6-Tnchlorophenol 5 4E-07 8 1E-07
2 4 Dichiorophenol 3 5E-07 5 2E-07
2 4-Dimethylphenol 1 8E-06 2 3E-06
2 4 Dinitrophenol 6 3E-06 8 1E-06
2 4-Dinitrotoluene 1 5E 07 1 8E-07
2 6-Dichlorophenol 2 4E 07 3 IE 07
2 6-Dinitrotoluene 2 2E-07 3 4E-07
2 Acetylaminofluorene 1 4E 07 1 8E-07
2 Chloronaphthalene 1 4E-07 1 8E-07
2-Chlorophenol 8 7E-07 1 4E-06
2-Methylnaphthalene 1 4E 06 2 6E 06
2-Methylphenol 8 6E-07 1 1E-06
2-Naphthylamine 2 9E-06 3 7E-06
2-Nitroaniline 1 4E-07 1 8E-07
2-Nitrophenol 1 7E-07 2 7E-07
3 3 -Dichlorobenzidine 2 1E-06 2 7E-06
3 3 -Dimethylbenzidine 1 4E-05 1 8E-05
3 Methylcholanthrene 1 4E-07 1 8E-07
3 Methylphenol & 4-Methylphenol 5 8E-07 7 4E-07
3-Nitroaniline 5 8E-07 7 4E-07
4 6 Dinitro-2 methylphenol 2 5E-06 3 2E 06
4 Aminobiphenyl 2 9E 06 3 7E-06
4-Bromophenyl phenyl ether 1 4E-07 1 8E-07
4-Chloro-3-methylphenol 1 8E-07 2 3E 07
4 Chloroaniline 1 7E 06 2 2E-06
4-Chlorophenyl phenyl ether 1 4E-07 1 8E-07
4-Nitroaniline 5 8E-07 7 4E-07
4 Nitrophenol 9 5E 07 1 2E 06
7 12-Dimethylbenz(a)anthracene 1 5E-07 1 9E-07
Acenaphthene 1 4E-07 1 8E-07
Acenaphthylene 1 4E-07 1 8E 07
Acetophenone 1 2E 06 2 2E-06
Aniline 2 1E-06 2 7E-06
Anthracene 1 4E-07 1 8E-07
Benzidine 1 5E-05 1 9E-05
Benzo(a)anthracene 1 7E-07 2 1E-07
Benzo(a)pyrene 1 4E-07 1 8E-07
Benzo(b)fluoranthene 3 2E-07 41E-07
Benzo(ghi)perylene 1 8E 07 2 3E-07
Benzo(k)fluonanthene 4 6E 07 5 9E-07
Table 5
Average and Maximum Emission Factors Based on
OBODI Emissions Testing
ATK
Brigham City, Utah
Page 3 of 7
Target Analyte Average EF
(lb/lb)
Maximum EF
(lb/lb)
Benzoic acid 2 7E-05 41E-05
Benzyl alcohol 1 OE-05 1 3E 05
bis(2 Chloroethoxy)methane 1 4E-07 1 8E-07
bis(2-Chloroethyl) ether 1 6E-07 2 1E-07
bis(2-Chloroisopropyl) ether 2 2E-07 2 8E-07
bis(2-Ethylhexyl) phthalate 2 9E-06 3 7E-06
Butyl benzyl phthalate 1 8E 07 2 3E-07
Carbazole 1 7E-07 2 4E-07
Chrysene 1 8E-07 2 4E 07
CS 2 9E-07 3 7E 07
Dibenz(a h)anthracene 1 7E-07 2 2E 07
Dibenzoftjran 1 5E-07 1 8E-07
Diethyl phthalate 2 2E-07 2 7E-07
Dimethyl phthalate 1 4E 07 1 8E-07
Di-n-butyl phthalate 2 9E 06 3 7E-06
DI n-octyl phthalate 1 2E-06 2 2E-06
Dinoseb 2 8E-07 3 7E 07
Diphenylamine 1 4E-07 1 8E 07
Ethyl methanesulfonate 1 4E-07 1 8E-07
Fluoranthene 2 3E-07 3 2E-07
Fluorene 2 1E 07 3 OE-07
Hexachlorobenzene 1 7E 06 3 5E-06
Hexachlorobutadiene 2 1E-07 2 7E-07
Hexachlorocyclopentadiene 2 9E-06 3 7E 06
Hexa chloroethane 1 6E-07 2 OE-07
Hexachloropropene 2 5E-07 2 7E-07
lndeno(1 2 3-cd)pyrene 1 6E-07 2 OE-07
Isophorone 1 4E 07 1 8E-07
Isosafrole 1 4E-07 1 8E 07
Methyl methanesulfonate 1 6E-07 2 0E 07
Naphthalene 6 OE-06 1 1E-05
Nitrobenzene 1 6E-07 2 1E-07
N-Nitro-o-toiuidine 2 3E-06 3 OE-06
N Nitrosodiethylamine 1 4E 07 1 8E-07
N-Nitrosodimethylamine 1 4E-07 1 8E 07
N-Nitrosodi-n-butylamine 1 4E 07 1 8E-07
N-Nitrosodi-n-propylamine 1 4E-07 1 8E-07
N Nitrosodiphenylamine 2 5E 07 3 2E 07
N-Nitrosomethylethylamine 2 4E 07 31E-07
N-Nitrosomoipholine 1 4E-07 1 8E-07
N Nitrosopipendine 1 4E-07 1 8E-07
N-Nitrosopyrrolidine 1 4E 07 1 8E-07
0 Toluidine 1 8E-06 2 4E-06
p-Dimethylaminoazobenzene 1 4E-07 1 8E-07
Penta chlorobenzene 2 IE 07 2 4E-07
Penta chloroethane 1 4E-07 1 8E 07
Penta chloronitrobenzene 1 4E-07 1 8E-07
Pentachlorophenol 7 2E-06 9 2E-06
Phenacebn 1 4E 07 1 8E-07
Phenanthrene 3 OE-07 5 IE 07
Phenol 1 OE-06 1 6E-06
Pyrene 1 5E-07 2 OE-07
Pyndine 2 1E-07 2 7E-07
Safrole 1 4E-07 1 8E-07
Table 5
Average and Maximum Emission Factors Based on
OBODI Emissions Testing
ATK
Brigham City, Utah
Page 4 of 7
Target Analyte Average EF
(lb/lb)
Maximum EF
(lb/lb)
Dioxins/Furans
2 3 7 8-TCDD 5 8E-13 7 9E-13
1 2 3 7 8 PeCDD 2 0E 12 4 2E-12
1 2 3 4 7 8 HxCDD 1 3E-12 2 4E 12
1 2 3 6 7 8-HxCDD 2 1E-12 4 8E-12
1 2 3 7 8 9-HxCDD 1 7E-12 3 5E-12
1 2 3 4 6 7 8-HpCDD 7 8E 12 1 8E-11
OCDD 1 1E-11 2 2E 11
2 3 7 8-TCDF 1 6E-11 3 2E-11
1 2 3 7 8-PeCDF 3 2E-11 6 5E-11
2 3 4 7 8 PeCDF 6 3E 11 1 4E-10
1 2 3 4 7 8-HxCDF 1 2E 10 2 3E-10
1 2 3 6 7 8-HxCDF 6 9E-11 1 4E-10
2 3 4 6 7 8-HxCDF 7 7E-11 1 6E-10
1 2 3 7 8 9 HxCDF 5 2E-11 1 1E-10
1 2 3 4 6 7 8-HpCDF 3 6E 10 7 0E 10
1 2 3 4 7 8 9-HpCDF 9 2E-11 1 8E-10
OCDF 2 6E-10 4 8E-10
TEQ 7 3E-11 1 5E-10
Carbonyis
2 5-Dimethylbenzaldehyde 7 2E 06 9 4E-06
Acetaldehyde 2 9E-05 5 OE-05
Acetone 6 5E-06 7 9E-06
Benzaldehyde 4 3E-06 5 3E 06
Crotonaldehyde 3 6E-06 4 7E-06
Formaldehyde 1 1E-05 2 2E-05
Hexanal 4 6E-06 5 6E-06
Isopentanal 3 6E-06 4 7E 06
m p Tolualdehyde 3 6E-06 4 7E-06
MEK/Butyraldehydes 7 2E-06 1 OE-05
o-Tolualdehyde 1 3E-05 2 OE-05
Penta nal 5 5E-06 8 5E-06
Propanal 1 4E 05 2 2E 05
HCI/CI2/NH3
HCI 81E-03 1 1E-02
CI2 3 3E-04 9 8E-04
NH3 1 3E 05 1 7E-05
HCN 6 5E-06 7 7E-06
Table 5
Average and Meiximum Emission Factors Based on
OBODI Emissions Testing
ATK
Brigham City Utah
Page 5 of 7
Target Analyte Average EF
(lb/lb)
Maximum EF
(lb/lb)
VOCs
TNMOC 3 8E-04 6 7E-04
1 1 1-Tnchloroethane 2 3E-07 3 OE-07
1 1 2 2-Tetrachloroethane 1 1E-07 1 4E-07
1 1 2-Tnchloroethane 1 8E-07 2 4E-07
1 1-Dichloroethane 8 0E 08 1 IE 07
1 1-Dichloroethene 1 1E-07 1 4E-07
1 2 3-Tnmethylbenzene 1 1E-07 1 4E-07
1 2 4-Tnchlorobenzene 3 2E 07 4 2E-07
12 4 Tnmethylbenzene 2 1E 06 3 7E-06
1 2-Dibromoethane (EDB) 2 2E 07 3 OE-07
1 2-Dichlorobenzene 1 2E-07 1 6E 07
1 2 Dichloroethane 1 4E-07 1 8E-07
1 2-Dichloropropane 9 2E-08 1 2E-07
1 3 5-Tnmethylbenzene 6 4E-07 1 4E 06
1 3-Butadiene 4 7E-06 1 IE 05
1 3 Dichlorobenzene 1 IE 07 1 5E-07
1 3 Diethylbenzene 1 3E-07 1 7E-07
1 4 Dichlorobenzene 1 8E-07 2 4E-07
1 4 Diethylbenzene 1 7E-07 2 2E-07
1 4-Dioxane 1 6E 07 2 1E-07
1 Butene 9 OE-06 1 9E-05
1 Hexene 8 2E-06 1 7E-05
1-Pentene 5 1E-06 1 OE 05
2 2 4 Tnmethylpentane 5 5E 07 1 1E-06
2 2-Dimethylbutane 2 2E-07 2 9E-07
2 3 4 Tnmethylpentane 7 3E-08 9 5E-08
2 3-Dimethylbutane 7 6E-07 1 5E-06
2 3-Dimethylpentav\e 7 9E07 1 8E-06
2 4-Dimethylpentane 2 8E 07 3 6E-07
2 Butanone (MEK) 2 2E 06 3 6E 06
2 Ethyltoluene 1 1E-07 1 5E 07
2 Hexanone 2 2E-07 2 9E-07
2 Methylheptane 5 0E 07 1 OE-06
2-Methylhexane 8 9E 07 2 2E 06
2-Methylpentane 3 2E-06 6 8E 06
2 Nitropropane 7 OE-07 1 4E-06
2-Propanol 7 5E 08 9 9E 08
3-Chforopropene 2 3E-06 4 OE-06
3 Ethyltoluene 1 OE-06 2 8E-06
3 Methylheptane 5 5E 07 1 2E 06
3-Methylhexane 1 IE 06 3 0E 06
3-Methylpentane 2 OE-06 4 4E-06
4-Ethyltoluene 1 9E 06 3 6E-06
4-Methyl-2-pentanone 1 8E 07 2 3E 07
Acetone 8 9E-06 1 2E-05
Acetonitnle 4 3E-06 7 6E-06
Acetylene 3 1E-05 6 5E-05
Acrylonitnle 3 9E-06 6 9E-06
alpha-Chlorotoluene 1 4E 07 1 9E 07
Benzene 2 2E-05 3 7E 05
Bromodichloromethane 2 OE-07 2 6E-07
Bromoform 3 2E-07 4 2E-07
Bromomethane 1 6E-07 2 1E-07
Butane 81E-06 1 6E-05
Table 5
Average and Maximum Emission Factors Based on
OBODI Emissions Testing
ATK
Brigham City Utah
Page 6 of 7
Target Analyte Average EF
(lb/lb)
Maximum EF
(lb/lb)
Carbon Disulfide 4 OE-06 7 5E-06
Carbon Tetrachlonde 8 6E-06 1 3E-05
Chloroacetonitnle 2 9E-07 3 8E-07
Chlorobenzene 1 0E06 2 1E-06
Chloroethane 6 4E 08 8 5E-08
Chlorofonn 3 1E-06 5 OE-06
Chloromethane 7 2E-06 1 3E 05
cis-1 2-Dichloroethene 1 2E-07 1 5E-07
CIS-1 3-Dichloropropene 3 IE 07 7 7E-07
as 2-Butene 6 5E-07 1 OE-06
cis-2-Pentene 8 3E-08 1 1E-07
Cumene 1 1E-07 1 4E-07
Cyclohexane 7 7E-07 1 5E-06
Cyclopentane 4 8E-07 7 4E-07
Decane 7 2E-06 1 2E-05
Dibromochloromethane 2 2E-07 2 9E 07
Ethane 9 3E-06 1 6E-05
Ethanol 5 2E-07 9 6E-07
Ethene 6 6E 05 1 4E-04
Ethyl Benzene 1 3E-06 2 4E-06
Ethyl Ether 6 3E-07 8 3E 07
Ethyl Methacrylate 4 OE-07 5 3E-07
Freon 11 1 2E-07 1 6E-07
Freon 113 2 6E-D7 3 4E-07
Freon 114 3 8E-07 5 OE-07
Freon 12 6 1E-08 8 OE-08
Heptane 2 9E-06 5 6E 06
Hexachlorobutadiene 4 3E 07 5 6E-07
Hexane 3 6E-06 7 3E-06
Isobutane 6 3E-07 1 1E 06
Isopentane 7 1E-06 1 5E 05
Isoprene 1 OE-07 1 4E-07
m p Xylene 4 4E-06 8 6E-06
Methacryionitnle 1 4E 06 1 9E-06
Methyl Acrylate 3 OE-07 4 OE-07
Methyl Methacrylate 3 9E-07 5 3E 07
Methyl tert-butyl ether 1 OE-07 1 4E-07
Methylcyclohexane 2 OE-06 4 OE-06
Methylcyclopentane 1 4E-06 3 5E-06
Methylene Chlonde 3 7E-06 6 1E-06
n-Butylchlonde 2 9E-06 3 8E 06
Nonane 5 1E-06 1 1E-05
Octane 3 3E-06 6 8E-06
o-Xylene 1 7E-06 2 9E-06
Pentane 8 4E 06 1 6E-05
Propane 4 1E-06 8 1E-06
Propylbenzene 3 OE-07 6 OE-07
Propylene 2 1E-05 3 9E-05
Styrene 2 7E-07 3 8E-07
Tetrachloroethene 1 IE 06 1 9E-06
Tetrahydrofuran 3 4E-07 5 7E07
Toluene 8 8E-06 1 7E-05
trans-1 2-Dichloroethene 1 8E-07 2 4E-07
trans-1 3-Dichloropropene 1 5E-07 2 OE-07
trans 2 butene 3 4E 06 5 8E-06
trans-2 Pentene 2 7E-07 6 2E 07
Tnchloroethene 31E-07 4 9E 07
Undecane 4 6E-06 9 OE-06
Vinyl Chlonde 2 2E-06 4 4E-06
Table 5
Average and Maximum Emission Factors Based on
OBODI Emissions Testing
ATK
Brigham City, Utah
Page 7 of 7
Target Analyte Average EF
(lb/lb)
Maximum EF
(lb/lb)
CEM
C02 5 7E-01 6 2E-01
CO 1 8E-03 4 0E-03
HCI 6 1E-05 1 OE-04
NOX 2 6E-03 3 8E-03
S02 1 2E-04 1 7E-04
TABLE 6
SUMMARY OF DEPOSITION AND
GRAVITATIONAL SETTLING CALCULATION PARAMETERS
ATK
BRIGHAM CITY, UTAH
Parameter Gas Phase OBODM Run Particulate Phase OBODM Run
Emission Surrogate COa Aluminum (density of 2 7 g/cm"')
Emission Factor 1 0 1 0
Non-gravitationai dry deposition Yes (computed in post-
processing step)
No
Gravitational settling No Yes
Mean particle diameter -12 3 pm
Particle size standard deviation -20
Number of particle size classes -10
Cloud depletion No Yes
OBODM Output Air concentration (pg/m") Deposition rate (pg/m'')
TABLE 7
A COMPARISON OF DISCRETE RECEPTOR
1-HOUR CARBON MONOXIDE CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARD
BASED ON AVERAGE OBODI EMISSION FACTOR
NAAQS 1 HOUR STANDARD = 40 000 ug/m' (PRIMARY STANDARD) 1 1 1 1 1 1 1
1 HOUR AIR CONCENTRATIONS (u q/m')
Receptor
X (Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 OB
Source A
M136 OB
Source B
M136 OB
Source C
M136 OD
Source D M136 Total M225 OB
Source A
M225 OD
Source B M225 Total M136 and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599749 1291 6 83E 03 5 55E 04 3 92E 04 5 33E 06 7 78E 03 2 58E 01 3 10E 02 2 89E 01 03 NO
Boundary #2 379669 4612480 1321 3 18E 03 3 46E 03 1 99E 03 3 50E 05 8 66E 03 3 75E 01 6 10E 02 4 36E 01 04 NO
Adams Ranch 379672 4612966 1327 3 44E 03 3 97E 03 2 02E 03 4 10E 05 9 47E 03 3 40E 01 5 53E 02 3 96E 01 04 NO
Blue Creek 379972 4615666 1341 1 36E 02 8 30E 03 5 83E 03 9 40E 05 2 79E 02 3 12E 01 5 52E 02 3 67E 01 04 NO
Howe Dairy 380309 4627652 1388 7 01E 04 9 84E 04 7 48E 04 1 59E 05 2 45E 03 1 16E 01 1 96E 02 1 36E 01 0 1 NO
Chnstensen Ranch 381372 4622166 1371 1 38E-03 1 31E-03 9 44E 04 2 05E 05 3 65E 03 2 10E 01 3 07E 02 2 41E 01 02 NO
Autoliv 381872 4610166 1335 1 12E 03 1 73E 03 1 14E 03 1 65E 05 4 01E 03 6 27E 01 1 87E 01 8 14E 01 08 NO
Boundary #4 386872 4608166 1295 7 99E 05 1 38E 03 7 66E 04 2 16E 05 2 25E 03 1 05E+00 2 48E 01 1 30E+00 1 3 NO
Boundary #3 387872 4610166 1385 1 19E 03 2 01E 03 1 24E 02 1 78E 05 1 56E 02 1 62E+00 9 74E 01 2 60E+00 26 NO
Holmgren Ranch Pond 388372 4608666 1295 8 02E 04 1 32E 03 7 88E 04 2 76E 05 2 93E 03 1 06E+00 3 16E 01 1 38E+00 1 4 NO
Boundary #1 (complex terrain) 382669 4616480 1542 1 12E 02 2 50E 02 1 94E 02 3 29E 04 5 58E 02 4 02E 01 6 58E 02 4 67E 01 05 NO
M 136 Onsite Max 380472 4615866 1367 1 91E 02 5 92E 02 2 OOE 02 9 45E 04 9 93E 02 3 35E 01 6 11E 02 3 96E 01 05 NO
M 136 Offsite Max 379872 4615966 1346 5 77E 02 8 84E 02 5 95E 02 1 12E 03 2 07E 01 3 01E 01 1 34E 01 4 35E 01 06 NO
M 225 Onsite Max 386268 4609480 1445 1 06E 03 1 78E 03 1 25E 02 2 27E 05 1 54E 02 1 07E+00 5 55E+00 6 62E+00 66 NO
M 225 Offsite Max 387369 4610480 1403 1 13E 03 1 99E 03 1 20E 03 1 80E 05 4 34E 03 1 10E+01 1 98E+00 1 29E+01 129 NO
* NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 8
A COMPARISON OF DISCRETE RECEPTOR
1-HOUR CARBON MONOXIDE CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARD
BASED ON MAXIMUM OBODI EMISSION FACTOR
NAAQS 1 HOUR STANDARD = 40 000 ug/m' (PRIMARY STANDARD) 1 1 1 1 1 1 1 1
1 HOUR AIR CONCENTRATIONS (u q/m')
Receptor
X (Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 0B
Source A
M136 0B
Source B
M136 OB
Source C
M136 OD
Source D M136 Total M225 OB
Source A
M225 OD
Source B M225 Total M136 and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599749 1291 1 54E 02 1 25E 03 8 86E 04 1 20E 05 1 76E 02 5 82E 01 7 01E 02 6 52E 01 0 7 NO
Boundary #2 379669 4612480 1321 7 18E 03 7 82E 03 4 50E 03 7 90E 05 1 96E 02 8 49E 01 1 38E 01 9 87E 01 1 0 NO
Adams Ranch 379672 4612966 1327 7 77E 03 8 98E 03 4 58E 03 9 27E 05 214E 02 7 69E 01 1 25E 01 8 94E 01 09 NO
Blue Creek 379972 4615666 1341 3 08E 02 1 88E 02 1 32E 02 2 13E 04 6 30E 02 7 06E 01 1 25E 01 8 31E 01 09 NO
Howe Dairy 380309 4627652 1388 1 59E 03 2 23E 03 1 69E 03 3 59E 05 5 54E 03 2 63E 01 4 43E-02 3 07E 01 03 NO
Chnstensen Ranch 381372 4622166 1371 3 11E 03 2 95E 03 2 13E 03 4 63E 05 8 25E 03 4 75E 01 6 94E 02 5 44E 01 06 NO
Autoliv 381872 4610166 1335 2 54E 03 3 91E 03 2 58E 03 3 74E 05 9 06E 03 1 42E+00 4 22E 01 1 84E+00 1 8 NO
Boundary #4 386872 4608166 1295 1 81E 04 312E 03 1 73E 03 4 87E 05 5 08E 03 2 38E+00 5 60E 01 2 94E+00 2 9 NO
Boundary #3 387872 4610166 1385 2 68E 03 4 55E 03 2 80E 02 4 03E 05 3 53E 02 3 67E+00 2 20E+00 5 87E+00 59 NO
Holmgren Ranch Pond 388372 4608666 1295 1 81E 03 2 98E 03 1 78E 03 6 23E 05 6 63E 03 2 40E+00 7 14E 01 312E+00 3 1 NO
Boundary #1 (complex terrain) 382669 4616480 1542 2 53E 02 5 64E 02 4 37E 02 7 44E 04 1 26E 01 9 08E 01 1 49E 01 1 06E+00 1 2 NO
M 136 Onsite Max 380472 4615866 1367 4 32E 02 1 34E 01 4 52E 02 2 14E 03 2 24E 01 7 58E 01 1 38E 01 8 96E 01 1 1 NO
M 136 Offsite Max 379872 4615966 1346 1 31E 01 2 OOE 01 1 35E 01 2 53E 03 4 67E 01 6 80E 01 3 04E 01 9 84E 01 1 5 NO
M 225 Onsite Max 386268 4609480 1445 2 40E 03 4 02E 03 2 83E 02 5 12E 05 3 48E 02 2 42E+00 1 26E+01 1 50E+01 150 NO
M 225 Offsite Max 387369 4610480 1403 2 55E 03 4 50E 03 2 71E 03 4 07E 05 9 81E03 2 48E+01 4 48E+00 2 93E+01 29 3 NO
* NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 9
A COMPARISON OF DISCRETE RECEPTOR
8-HOUR CARBON MONOXIDE CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARDS
BASED ON AVERAGE OBODI EMISSION FACTOR
NAAQS 8 HOUR STANDARD = 10 000 ug/m'( PRIMARY STANDARD) 1 1 1 1 1 1 1 1
8 HOUR AIR CONCENTRATIONS (u dim')
Receptor
y.
(Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 0B
Source A
M136 OB
Source B
M136 OB
Source C
M136 0D
Source D Ml 36 Total M225 0B
Source A
mis OD
Source B M225 Total M136and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599749 1291 8 88E 04 7 21E 05 5 10E 05 6 93E 07 1 01E 03 3 35E 02 4 03E 03 4 03E 03 5 04E 03 NO
Boundary #2 379669 4612480 1321 4 13E 04 4 49E 04 2 59E 04 4 54E 06 1 13E 03 4 88E 02 7 93E 03 7 93E 03 9 06E 03 NO
Adams Ranch 379672 4612966 1327 4 47E 04 5 17E 04 2 63E 04 5 33E 06 1 23E 03 4 42E 02 7 19E 03 7 19E 03 8 42E 03 NO
Blue Creek 379972 4615666 1341 1 77E 03 1 08E 03 7 58E 04 1 22E 05 3 62E 03 4 06E 02 7 17E 03 7 17E 03 1 08E 02 NO
Howe Dairy 380309 4627652 1388 9 12E 05 1 28E 04 9 72E 05 2 07E 06 3 18E 04 1 51E 02 2 55E 03 2 55E 03 2 87E 03 NO
Chnstensen Ranch 381372 4622166 1371 1 79E 04 1 70E 04 1 23E 04 2 66E 06 4 74E 04 2 73E 02 3 99E 03 3 99E 03 4 46E 03 NO
Autoliv 381872 4610166 1335 1 46E 04 2 25E 04 1 49E 04 2 15E 06 5 21E 04 8 15E 02 2 43E 02 2 43E 02 2 48E 02 NO
Boundary #4 386872 4608166 1295 1 04E 05 1 79E 04 9 96E 05 2 80E 06 2 92E 04 1 37E 01 3 22E 02 3 22E 02 3 25E 02 NO
Boundary #3 387872 4610166 1385 1 54E 04 2 61E 04 1 61E03 2 32E 06 2 03E 03 2 11E 01 1 27E 01 1 27E 01 1 29E 01 NO
Holmgren Ranch Pond 388372 4608666 1295 1 04E 04 1 71E 04 1 02E 04 3 58E 06 3 82E 04 1 38E 01 4 11E 02 4 11E 02 4 15E 02 NO
Boundary #1 (complex terrain) 382669 4616480 1542 1 45E 03 3 25E 03 2 52E 03 4 28E 05 7 26E 03 5 22E 02 8 56E 03 8 56E 03 1 58E 02 NO
M 136 Onsite Max 380472 4615866 1367 2 49E 03 7 70E 03 2 60E 03 1 23E 04 1 29E 02 4 36E 02 7 94E 03 7 94E 03 2 08E 02 NO
M 136 Offsite Max 379872 4615966 1346 7 50E 03 1 15E 02 7 73E 03 1 45E 04 2 69E 02 3 91E02 1 75E 02 1 75E 02 4 43E 02 NO
M 225 Onsite Max 386268 4609480 1445 1 38E 04 2 31E 04 1 63E 03 2 95E 06 2 OOE 03 1 39E 01 7 22E 01 7 22E 01 7 24E 01 NO
M 225 Offsite Max 387369 4610480 1403 1 47E 04 2 59E 04 1 56E 04 2 34E 06 5 64E 04 1 43E+00 2 57E 01 2 57E 01 2 58E 01 NO
NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 10
A COMPARISON OF DISCRETE RECEPTOR
8-HOUR CARBON MONOXIDE CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARDS
BASED ON MAXIMUM OBODI EMISSION FACTOR
NAAQS 8 HOUR STANDARD = 10 000 ug/m'(PRIMARY STANDARD) 1 1 1 1 1 1 I
8 HOUR AIR CONCENTRATIONS (u q/m')
Receptor
x
(Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 OB
Source A
M136 0B
Source B
M136 0B
Source C
M136 0D
Source D Ml 36 Total M225 0B
Source A
M225 OD
Source B M225 Total M136 and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599749 1291 2 01E 03 1 63E 04 1 15E 04 1 57E 06 2 29E 03 7 57E 02 1 26E 01 4 03E 03 6 32E 03 NO
Boundary #2 379669 4612480 1321 9 34E 04 1 02E 03 5 85E 04 1 03E 05 2 54E 03 1 10E 01 2 49E 01 7 93E 03 1 05E 02 NO
Adams Ranch 379672 4612966 1327 1 01E 03 1 17E 03 5 95E 04 1 21E 05 2 78E 03 1 OOE 01 2 26E 01 7 19E 03 9 98E 03 NO
Blue Creek 379972 4615666 1341 4 01E 03 2 44E 03 1 71E 03 2 76E 05 8 19E 03 9 18E 02 2 25E 01 7 17E 03 1 54E 02 NO
Howe Dairy 380309 4627652 1388 2 06E 04 2 89E 04 2 20E 04 4 67E 06 7 20E 04 3 42E 02 7 99E 02 2 55E 03 3 27E 03 NO
Chnstensen Ranch 381372 4622166 1371 4 04E 04 3 84E 04 2 78E 04 6 02E 06 1 07E 03 6 17E 02 1 25E 01 3 99E 03 5 06E 03 NO
Autoliv 381872 4610166 1335 3 30E 04 5 08E 04 3 36E 04 4 86E 06 1 18E 03 1 84E 01 761E 01 2 43E 02 2 54E 02 NO
Boundary #4 386872 4608166 1295 2 35E 05 4 05E 04 2 25E 04 6 34E 06 6 60E 04 3 10E 01 1 01E+00 3 22E 02 3 28E 02 NO
Boundary #3 387872 4610166 1385 3 48E 04 5 91E04 3 65E 03 5 25E 06 4 59E 03 4 77E 01 3 97E+00 1 27E 01 1 31E 01 NO
Holmgren Ranch Pond 388372 4608666 1295 2 36E 04 3 87E 04 2 32E 04 8 10E 06 8 63E 04 3 12E 01 1 29E+00 41 IE 02 4 19E 02 NO
Boundary #1 (complex terrain) 382669 4616480 1542 3 29E 03 7 34E 03 5 69E 03 9 67E 05 1 64E 02 1 18E 01 2 69E 01 8 56E 03 2 50E 02 NO
M 136 Onsite Max 380472 4615866 1367 5 62E 03 1 74E 02 5 88E 03 2 78E 04 2 92E 02 9 85E 02 2 49E 01 7 94E 03 3 71E 02 NO
M 136 Offsite Max 379872 4615966 1346 1 70E 02 2 60E 02 1 75E 02 3 29E 04 6 08E 02 8 84E 02 5 48E 01 1 75E 02 7 82E 02 NO
M 225 Onsite Max 386268 4609480 1445 3 13E 04 5 23E 04 3 68E 03 6 66E 06 4 52E 03 3 15E 01 2 26E+01 7 22E 01 7 26E 01 NO
M 225 Offsite Max 387369 4610480 1403 3 32E 04 5 86E 04 3 52E 04 5 29E 06 1 27E 03 3 22E+00 8 08E+00 2 57E 01 2 59E 01 NO
NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 11
A COMPARISON OF DISCRETE RECEPTOR
24-HOUR PM 2 5 CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARDS
BASED ON AVERAGE OBODI EMISSION FACTOR
NAAQS PM 2 5 24 HOUR STANDARD = 35 ug/m3 (PRIMARY AND SECONDARY STANDARD)
r 24 HOUR AIR CONCENTRATIONS (ug/m')
Receptor
X
(Easting)
meters
y
(Northing)
meters
Elevations
(meters)
M136 0B
Source A
M136 0B
Source B
M136 0B
Source C
M136 OD
Source D M136 Total M225 OB
Source A
M22S OD
Source B M225 Total M136 andM225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599479 1291 4 39E 04 2 91E 04 2 60E 04 2 37E 06 9 92E 04 5 85E 02 1 08E 02 6 93E 02 7 03E 02 NO
Boundary #2 382669 4599480 1321 2 45E 03 2 OOE 03 1 20E 03 2 19E 05 5 67E 03 1 10E 01 3 18E 02 1 42E 01 1 48E 01 NO
Adams Ranch 386872 4608166 1327 2 61E 03 2 04E 03 9 97E 04 2 OOE 05 5 66E 03 9 20E 02 2 53E 02 1 17E 01 1 23E 01 NO
Blue Creek 388372 4608666 1341 8 53E 03 5 77E 03 3 62E 03 5 94E 05 1 80E 02 8 86E 02 2 37E 02 1 12E 01 1 30E 01 NO
Howe Dairy 380309 4627652 1388 4 63E 04 4 57E 04 4 15E 04 5 91E 06 1 34E 03 2 74E 02 7 01E 03 3 44E 02 3 57E 02 NO
Chnstensen Ranch 381872 4610166 1371 1 01E 03 7 13E 04 5 93E 04 7 18E 06 2 33E 03 4 90E 02 1 25E 02 615E 02 6 39E 02 NO
Autoliv 387872 4610166 1335 6 37E 04 9 90E 04 6 37E 04 9 37E 06 2 27E 03 2 87E 01 8 47E 02 3 72E 01 3 74E 01 NO
Boundary #4 395169 4611480 1295 5 03E 04 5 95E 04 3 49E 04 9 44E 06 1 46E 03 4 17E 01 1 31E 01 5 48E 01 5 49E 01 NO
Boundary #3 379669 4612480 1385 8 38E 04 1 11E 03 6 69E 04 1 OOE 05 2 63E 03 1 02E+00 2 37E 01 1 26E+00 1 26E+00 NO
Holmgren Ranch Pond 379672 4612966 1295 5 35E 04 7 15E 04 4 19E 04 6 85E 06 1 68E 03 4 24E 01 1 32E 01 5 55E 01 5 57E 01 NO
M 136 Onsite Max 379972 4615666 1368 3 56E 02 3 53E 02 1 13E 02 1 04E 03 8 33E 02 8 87E 02 5 19E 02 1 41E 01 2 24E 01 NO
M 136 Offsite Max 381372 4622166 1346 9 16E 03 1 22E 02 6 17E 03 1 39E 04 2 76E 02 8 34E 02 4 53E 02 1 29E 01 1 56E 01 NO
M 225 Onsite Max 382669 4616480 1401 8 24E 04 1 88E 03 6 40E 04 1 01E 06 3 34E 03 1 01E+01 1 20E+00 1 13E+01 1 13E+01 NO
M 225 Offsite Max 382572 4616766 1381 5 95E 04 6 95E 04 4 04E 04 7 25E 06 1 70E 03 1 42E+00 3 43E 01 1 76E+00 1 76E+00 NO
NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 12
A COMPARISON OF DISCRETE RECEPTOR
24-HOUR PM 2 5 CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARDS
BASED ON MAXIMUM OBODI EMISSION FACTOR
NAAQS PM 2 5 24-HOUR STANDARD = 35 uglmZ (PRIMARY AND SECONDARY STANDARD)
24-HOUR AIR CONCENTRATIONS (ug/m')
Receptor
X
(Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 0B
Source A
M136 OB
Source B
M136 OB
Source C
M136 OD
Source D Ml 36 Total M22S OB
Source A
M225 OD
Source B M225 Total M136 and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599479 1291 6 21E 04 4 11E 04 3 69E 04 3 35E 06 1 40E 03 8 28E 02 1 53E 02 9 81E 02 9 95E 02 NO
Boundary #2 382869 4599480 1321 3 47E 03 2 83E 03 1 69E 03 3 10E 05 8 02E 03 1 56E 01 4 50E 02 2 01E 01 2 OOE 01 NO
Adams Ranch 386872 4608166 1327 3 69E 03 2 89E 03 1 41E 03 2 96E 05 8 02E 03 1 30E 01 3 58E 02 1 66E 01 1 74E 01 NO
Blue Creek 388372 4608666 1341 1 21E 02 8 16E 03 5 13E 03 8 40E 05 2 55E 02 1 25E-01 3 35E-02 1 59E 01 1 84E 01 NO
Howe Dairy 380309 4627652 1388 6 55E 04 6 47E 04 5 87E 04 8 37E 06 1 90E 03 3 87E 02 9 92E 03 4 87E 02 5 06E 02 NO
Chnstensen Ranch 381872 4610166 1371 1 43E 03 1 01E 03 8 40E 04 1 02E 05 3 29E 03 6 94E 02 1 77E 02 8 71E 02 9 04E 02 NO
Autoliv 387872 4610166 1335 9 02E 04 1 40E 03 9 01E 04 1 33E 05 3 22E 03 4 06E 01 1 20E 01 5 26E 01 5 29E 01 NO
Boundary #4 395169 4611480 1295 7 12E 04 8 42E 04 4 94E 04 1 34E 05 2 06E 03 5 90E 01 1 85E 01 7 75E01 7 77E 01 NO
Boundary #3 379669 4612480 1385 1 19E 03 1 57E 03 9 47E 04 1 42E 05 3 72E 03 1 44E+00 3 35E 01 1 78E+00 1 78E+00 NO
Holmgren Ranch Pond 379672 4612966 1295 7 58E 04 1 01E 03 5 94E 04 9 69E 06 2 37E 03 5 99E 01 1 86E 01 7 86E 01 7 88E 01 NO
M 136 Onsite Max 379972 4615666 1368 5 04E 02 5 OOE 02 1 61E 02 1 48E 03 1 18E 01 1 26E 01 7 34E 02 1 99E 01 3 17E 01 NO
M 136 Offsite Max 381372 4622166 1346 1 30E 02 1 72E 02 8 74E 03 1 97E 04 3 91E 02 1 18E 01 6 42E 02 1 82E 01 2 21E 01 NO
M 225 Onsite Max 382669 4616480 1401 1 17E 03 2 66E 03 9 06E 04 1 44E 06 4 73E 03 1 43E+01 1 70E+00 1 60E+01 1 60E+01 NO
M 225 Offsite Max 382572 4616766 1381 8 42E 04 9 84E 04 5 72E 04 1 03E 05 2 41E 03 2 01E+00 4 86E 01 2 49E+00 2 49E+00 NO
NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 13
A COMPARISON OF DISCRETE RECEPTOR
24-HOUR PM 10 CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARDS
BASED ON AVERAGE OBODI EMISSION FACTOR
NAAQS PM 10 24 HOUR STANDARD = 150 ug/m' (PRIMARY AND SECONDARY STANDARD)
24 HOUR AIR CONCENTRATIONS (ug/m')
Receptor
X
(Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 OB
Source A
M136 OB
Source B
M136 0B
Source C
M136 OD
Source D M136 Total M225 OB
Source A
M225 OD
Source B M225 Total M136and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599479 1291 8 60E 04 5 69E 04 5 10E 04 4 63E 06 1 94E 03 0 1 00 0 1 01 NO
Boundary #2 382669 4599480 1321 4 80E 03 3 91E 03 2 34E 03 4 29E 05 1 11E 02 02 0 1 03 03 NO
Adams Ranch 386872 4608166 1327 5 10E 03 4 OOE 03 1 95E 03 4 10E 05 1 11E02 02 00 02 02 NO
Blue Creek 388372 4608666 1341 1 67E 02 1 13E 02 7 10E 03 1 16E 04 3 52E 02 02 00 02 03 NO
Howe Dairy 380309 4627652 1388 9 06E 04 8 96E 04 8 12E 04 1 16E 05 2 63E 03 0 1 00 0 1 0 1 NO
Chnstensen Ranch 381872 4610166 1371 1 98E 03 1 40E 03 1 16E 03 1 41E 05 4 56E 03 0 1 00 01 0 1 NO
Autoliv 387872 4610166 1335 1 25E 03 1 94E 03 1 25E 03 1 84E 05 4 45E 03 06 02 07 07 NO
Boundary #4 395169 4611480 1295 9 86E 04 1 17E 03 6 84E 04 1 85E 05 2 85E 03 08 03 1 1 1 1 NO
Boundary #3 379669 4612480 1385 1 64E 03 2 18E 03 1 31E 03 1 97E 05 5 15E 03 2 0 05 25 25 NO
Holmgren Ranch Pond 379672 4612966 1295 1 05E 03 1 40E 03 8 21E04 1 34E 05 3 28E 03 08 03 1 1 1 1 NO
M 136 Onsite Max 379972 4615666 1368 6 97E 02 6 92E 02 2 22E 02 2 04E 03 1 63E 01 02 0 1 03 04 NO
M 136 Offsite Max 381372 4622166 1346 1 79E 02 2 38E 02 1 21E 02 2 72E 04 5 41E02 02 0 1 03 03 NO
M 225 Onsite Max 382669 4616480 1401 1 61E 03 3 68E 03 1 25E 03 1 99E 06 6 55E 03 197 24 22 1 22 1 NO
M 225 Offsite Max 382572 4616766 1381 1 17E 03 1 36E 03 7 91E04 1 42E 05 3 33E 03 2 8 07 34 35 NO
NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 14
A COMPARISON OF DISCRETE RECEPTOR
24-HOUR PM 10 CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARDS
BASED ON MAXIMUM OBODI EMISSION FACTOR
NAAQS PM 10 24 HOUR STANDARD = 150 ug/m' (PRIMARY AND SECONDARY STANDARD)
24-HOUR AIR CONCENTRATIONS (ug/m^
Receptor
X
(Easting)
meters
V
(Northing)
meters
Elevations
(meters)
M136 0B
Source A
M136 OB
Source B
Ml 36 OB
Source C
M136 OD
Source D M136 Total M225 OB
Source A
M225 OD
Source B M225 Total Ml 36 andM225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599479 1291 1 19E 03 7 89E 04 7 07E 04 6 42E06 2 69E-03 02 00 02 02 NO
Boundary #2 382669 4599460 1321 6 66E 03 5 42E 03 3 25E 03 5 94E 05 1 54E 02 03 0 1 04 04 NO
Adams Ranch 386872 4608166 1327 7 07E 03 5 54E 03 2 71E-03 5 68E 05 1 54E 02 02 0 1 03 03 NO
Blue Creek 388372 4608666 1341 2 32E 02 1 57E 02 9 84E 03 1 61E 04 4 88E 02 02 0 1 03 04 NO
Howe Dairy 380309 4627652 1388 1 26E 03 1 24E 03 1 13E 03 1 61E 05 3 64E-03 0 1 00 0 1 0 1 NO
Chnstensen Ranch 381872 4610166 1371 2 75E 03 1 94E 03 1 61E 03 1 95E 05 6 32E 03 0 1 00 02 02 NO
Autoliv 387872 4610166 1335 1 73E 03 2 69E 03 1 73E 03 2 54E 05 617E 03 08 02 1 0 1 0 NO
Boundary #4 395169 4611480 1295 1 37E 03 1 62E 03 9 49E 04 2 56E 05 3 96E 03 1 1 04 1 5 1 5 NO
Boundary #3 379669 4612480 1385 2 28E 03 3 02E 03 1 82E-03 2 73E 05 7 14E 03 28 06 34 34 NO
Holmgren Ranch Pond 379672 4612966 1295 1 45E 03 1 94E 03 1 14E 03 1 86E 05 4 55E 03 1 2 04 1 5 1 5 NO
M 136 Onsite Max 379972 4615666 1368 9 67E 02 9 59E 02 3 08E 02 2 83E 03 2 26E 01 02 01 04 06 NO
M 136 Offsite Max 381372 4622166 1346 2 49E 02 3 30E-02 1 68E-02 3 78E 04 7 50E 02 02 0 1 03 04 NO
M 225 Onsite Max 382669 4616480 1401 2 24E 03 5 10E 03 1 74E 03 2 75E 06 9 08E-03 27 4 33 30 6 30 6 NO
M 225 Offsite Max 382572 4616766 1381 1 62E 03 1 89E 03 1 10E 03 1 97E 05 4 62E 03 38 09 48 48 NO
NOT APPLICABLE TO ONSITE LOCATIONS
The State o< Utah has adopted the National Ambient Air Quality Standards
TABLE 15
A COMPARISON OF DISCRETE RECEPTOR
ANNUAL PM 2 5 CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARD
BASED ON AVERAGE OBODI EMISSION FACTOR
NAAQS PM 10 ANNUAL STANDARD = 15 ug/m'(PRIMARY AND SECONDARY STANDARD) Illllll
ANNUAL AIR CONCENTRAnONS (ug/m')
Receptor
X
(Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 OB
Source A
M136 OB
Source B
M136 OB
Source C
M136 0D
Source D Ml 36 Total M225 OB
Source A
M225 OD
Source B M225 Total M136 and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599749 1291 4 17E 07 1 30e 09 801E-09 1 47E 10 4 27E 07 7 30E 06 1 30E 06 8 60E 06 9 03E 06 NO
Boundary #4 379669 4612480 1321 2 96E 06 8 38E 09 5 12E 08 9 72E 10 3 02E 06 4 41E 05 9 16E-06 5 32E 05 5 62E 05 NO
Holmgren Ranch Pond 379672 4612966 1327 341E06 9 40E 09 5 82E-08 1 10E 09 3 48E 06 4 13E05 8 61E 06 4 99E-05 5 34E 05 NO
Howe Dairy Farm 379972 4615666 1341 6 39E 05 1 27E 07 7 88E 07 1 42E 08 6 48E 05 3 44E 05 7 21E06 4 16E-05 1 06E 04 NO
Autoliv 380309 4627652 1388 3 44E 06 1 05E 08 6 95E 08 1 22E 09 3 52E 06 1 09E 05 2 30E 06 1 32E-05 1 67E 05 NO
Boundary #3 381372 4622166 1371 6 72E-06 8 78E 08 1 31E 07 2 19E 09 6 94E 06 1 97E 05 4 12E 06 2 39E-05 3 08E-05 NO
Boundary #2 381872 4610166 1335 2 67E 06 8 33E-08 5 17E-08 8 52E 10 2 80E 06 8 28E 05 1 71E 05 9 99E-05 1 03E-04 NO
Adams Ranch 386872 4608166 1295 1 68E-06 6 OOE 09 3 76E-08 6 65E 10 1 72E06 4 04E 05 1 04E 05 5 08E 05 5 26E 05 NO
Blue Creek 387872 4610166 1385 1 60E 06 6 03E 09 3 73E 08 6 96E 10 1 64E 06 1 03E 04 2 29E 05 1 26E 04 1 27E 04 NO
Chnstensen Ranch 388372 4608666 1295 1 45E 06 5 32E 09 3 29E 08 6 07E 10 1 48E06 5 68E 05 1 23E 05 6 91E05 7 06E 05 NO
M 136 Meiximum Off site Annual 380472 4615866 1368 2 24E 04 4 74E 07 1 69E 04 6 81E 07 3 94E 04 3 60E 05 7 55E 07 3 67E 05 4 31E 04 NO
M 136 Maximum On site Annual 379872 4615966 1346 7 37E 05 1 51E 07 8 69E 07 1 79E-08 7 47E 05 3 22E 05 6 76E 06 3 90E 05 1 14E 04 NO
M 225 Maximum Off site Annual 386769 4609480 1401 1 BOE 06 6 54E 09 4 09E 06 7 42E-10 1 85E06 8 31E04 1 54E 04 9 85E 04 9 87E 04 NO
M 225 Maximum Onsite Annual 387369 4610080 1381 1 74E 06 6 37E 09 3 96E 08 7 35E-10 1 78E 06 1 30E 04 3 17E 05 1 62E 04 1 63E 04 NO
* NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 16
A COMPARISON OF DISCRETE RECEPTOR
ANNUAL PM 2 5 CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARD
BASED ON MAXIMUM OBODI EMISSION FACTOR
NAAQS PM 10 ANNUAL STANDARD = 15 ug/m'(PRIMARY AND SECONDARY STANDARD) 1 1 1 1 1 j 1
ANNUAL AIR CONCENTRATIONS (ug/m')
Receptor
(Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 OB
Source A
M136 0B
Source B
M136 OB
Source C
M136 OD
Source D M136 Total M225 OB
Source A
M225 OD
Source B M225 Total M136and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599749 1291 5 91E 07 1 83E 09 1 13E 08 2 08E 10 6 04E 07 1 03E 05 1 84E 06 1 22E 05 1 28E 05 NO
Boundary #4 379669 4612480 1321 4 19E 06 1 19E 08 7 24E 08 1 38E 09 4 27E 06 6 24E 05 1 30E 05 7 53E 05 7 96E 05 NO
Holmgren Ranch Pond 379672 4612966 1327 4 83E 06 1 33E 08 8 24E 08 1 56E 09 4 93E 06 5 84E 05 1 22E 05 7 06E 05 7 55E 05 NO
Howe Dairy Farm 379972 4615666 1341 9 04E 05 1 80E 07 1 12E 06 2 01E 08 9 18E 05 4 87E 05 1 02E 05 5 89E 05 1 51E 04 NO
Autoliv 380309 4627652 1388 4 87E 06 1 49E 08 9 e4E 08 1 73E 09 4 98E 06 1 54E 05 3 26E 06 1 87E 05 2 37E 05 NO
Boundary #3 381372 4622166 1371 9 51E 06 1 24E 07 1 86E 07 3 11E 09 9 82E 06 2 79E 05 5 84E 06 3 38E 05 4 36E 05 NO
Boundary #2 381872 4610166 1335 3 77E 06 1 18E 07 7 31E 08 1 21E 09 3 97E 06 1 17E 04 2 42E 05 1 41E 04 1 45E 04 NO
Adams Ranch 386872 4608166 1295 2 37E 06 8 49E 09 5 32E 08 9 42E 10 2 43E 06 5 72E 05 1 47E 05 7 20E 05 7 44E 05 NO
Blue Creek 387872 4610166 1385 2 26E 06 8 54E 09 5 27E 08 9 85E 10 2 33E 06 1 45E 04 3 25E 05 1 78E 04 1 80E 04 NO
Chnstensen Ranch 388372 4608666 1295 2 05E 06 7 53E 09 4 65E 08 8 59E 10 2 10E 06 8 04E 05 1 75E 05 9 78E 05 9 99E 05 NO
M 136 Maximum Off site Annual 380472 4615866 1368 3 17E 04 6 71E 07 2 40E 04 9 64E 07 5 58E 04 5 09E 05 1 07E 06 5 20E 05 6 10E 04 NO
M 136 Maximum On site Annual 379872 4615966 1346 1 04E 04 2 14E 07 1 23E 06 2 54E 08 1 06E 04 4 56E 05 9 56E 06 5 52E 05 1 61E 04 NO
M 225 Maximum Off site Annual 386769 4609480 1401 2 55E 06 9 26E 09 5 79E 08 1 05E 09 2 62E 06 1 18E 03 2 18E 04 1 39E 03 1 40E 03 NO
M 225 Maximum Onsite Annual 387369 4610080 1381 2 46E 06 9 02E 09 5 60E 08 1 04E 09 2 53E 06 1 84E 04 4 49E 05 2 29E 04 2 31E 04 NO
* NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 17
A COMPARISON OF DISCRETE RECEPTOR
ANNUAL PM 10 CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARD
BASED ON AVERAGE OBODI EMISSION FACTORS
NAAQS PM 10 ANNUAL STANDARD = 50 ug/m" (PRIMARY AND SECONDARY)
ANNUAL AIR CONCENTRATIONS (u $l/m')
Receptor
X
(Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 OB
Source A
M136 OB
Source B
M136 0B
Source C
M136 OD
Source D M136 Total M225 OB
Source A
M225 OD
Source B M225 Total M136 and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599749 1291 8 17E 07 2 54E 09 1 57E 08 2 88E 10 8 36E 07 1 43E 05 2 55E 06 1 68E 05 1 77E 05 NO
Boundary #4 379669 4612480 1321 5 79E 06 1 64E 06 1 OOE 07 1 90E 09 5 91E06 8 63E 05 1 79E 05 1 04E 04 1 10E 04 NO
Holmgren Ranch Pond 379672 4612966 1327 6 68E 06 1 84E 08 1 14E 07 2 15E 09 6 82E 06 8 09E 05 1 69E 05 9 77E 05 1 05E 04 NO
Howe Dairy Farm 379972 4615666 1341 1 25E 04 2 49E 07 1 54E 06 2 78E 08 1 27E 04 6 74E 05 1 41E 05 8 16E 05 2 09E 04 NO
Autoliv 380309 4627652 1388 6 73E 06 2 06E 08 1 36E 07 2 39E 09 6 89E 06 2 13E 05 4 51E06 2 58E 05 3 27E 05 NO
Boundary #3 381372 4622166 1371 1 32E 05 1 72E 07 2 57E 07 4 30E 09 1 36E 05 3 87E 05 8 08E 06 4 67E 05 6 03E 05 NO
Boundary #2 381872 4610166 1335 5 22E 06 1 63E 07 1 01E 07 1 67E 09 5 49E 06 1 62E 04 3 34E 05 1 96E 04 2 01E 04 NO
Adams Ranch 386872 4608166 1295 3 28E 06 1 17E 08 7 36E 08 1 30E 09 3 37E 06 7 92E 05 2 04E 05 9 96E 05 1 03E 04 NO
Blue Creek 387872 4610166 1385 3 13E 06 1 18E 08 7 30E 08 1 36E 09 3 22E 06 2 01E 04 4 49E 05 2 46E 04 2 49E 04 NO
Chnstensen Ranch 388372 4608666 1295 2 83E 06 1 04E 08 6 44E 08 1 19E 09 2 91E 06 1 11E 04 2 42E 05 1 35E 04 1 38E 04 NO
M 136 Maximum Off site Annual 380472 4615866 1368 4 38E 04 9 28E 07 3 32E 04 1 33E 06 7 72E 04 7 04E 05 1 48E 06 7 19E 05 8 44E 04 NO
M 136 Maximum On site Annual 379872 4615966 1346 1 44E 04 2 96E 07 1 70E 06 3 51E08 1 46E 04 6 32E 05 1 32E 05 7 64E 05 2 23E 04 NO
M 225 Maximum Off site Annual 386769 4609480 1401 3 53E 06 1 28E 08 8 01E 08 1 45E 09 3 62E 06 1 63E 03 3 02E 04 1 93E 03 1 93E 03 NO
M 225 Maximum Onsite Annual 387369 4610080 1381 3 40E 06 1 25E 08 7 75E 08 1 44E 09 3 50E 06 2 54E 04 6 22E 05 3 17E 04 3 20E 04 NO
NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 18
A COMPARISON OF DISCRETE RECEPTOR
ANNUAL PM 10 CONCENTRATIONS
TO THE NATIONAL AMBIENT AIR QUALITY STANDARD
BASED ON MAXIMUM OBODI EMISSION FACTORS
NAAQS PM 10 ANNUAL STANDARD = 50 ug/m' (PRIMARY AND SECONDARY)
ANNUAL AIR CONCENTRATIONS (ug/m')
Receptor
X
(Easting)
meters
Y
(Northing)
meters
Elevations
(meters)
M136 OB
Source A
M136 OB
Source B
M136 0B
Source C
M136 0D
Source D M136 Total M225 OB
Source A
M225 OD
Source B M225 Total M136 and M225
Combined Total
NAAQS
Exceedance
Thiokol Ranch Pond 376670 4599749 1291 1 13E 06 3 52E 09 2 18E 08 3 99E 10 1 16E 06 1 98E 05 3 54E 06 2 34E 05 2 45E 05 NO
Boundary #4 379669 4612480 1321 8 03E 06 2 28E 08 1 39E 07 2 64E 09 8 19E 06 1 20E 04 2 49E 05 1 45E 04 1 53E 04 NO
Holmgren Ranch Pond 379672 4612966 1327 9 26E 06 2 55E 08 1 58E 07 2 99E 09 9 45E 06 1 12E 04 2 34E 05 1 35E 04 1 45E 04 NO
Howe Dairy Farm 379972 4615666 1341 1 74E 04 3 45E 07 2 14E 06 3 86E 08 1 76E 04 9 35E 05 1 96E 05 1 13E 04 2 89E 04 NO
Autoliv 380309 4627652 1388 9 33E 06 2 85E 08 1 89E 07 3 32E 09 9 55E 06 2 96E 05 6 25E 06 3 58E 05 4 54E 05 NO
Boundary #3 381372 4622166 1371 1 82E 05 2 38E 07 3 57E 07 5 96E 09 1 88E 05 5 36E 05 1 12E 05 6 48E 05 8 37E 05 NO
Boundary #2 381872 4610166 1335 7 24E 06 2 26E 07 1 40E 07 2 31E 09 7 61E 06 2 25E 04 4 64E 05 2 71E 04 2 79E 04 NO
Adams Ranch 386872 4608166 1295 4 55E 06 1 63E 08 1 02E 07 1 81E 09 4 67E 06 1 10E 04 2 83E 05 1 38E 04 1 43E 04 NO
Blue Creek 387872 4610166 1385 4 34E 06 1 64E 08 1 01E 07 1 89E 09 4 46E 06 2 79E 04 6 23E 06 3 41E 04 3 46E 04 NO
Chnstensen Ranch 388372 4608666 1295 3 92E 06 1 45E 08 8 93E 08 1 65E 09 4 03E 06 1 54E 04 3 35E 05 1 88E 04 1 92E 04 NO
M 136 Maximum Off site Annual 380472 4615866 1368 6 07E 04 1 29E 06 4 60E 04 1 85E 06 1 07E 03 9 76E 05 2 05E 06 9 97E 05 1 17E 03 NO
M 136 Maximum On site Annual 379872 4615966 1346 2 OOE 04 410E 07 2 36E 06 4 87E 08 2 03E 04 8 76E 05 1 83E 05 1 06E 04 3 09E 04 NO
M 225 Maximum Off site Annual 386769 4609480 1401 4 89E 06 1 78E 08 1 11E 07 2 02E 09 5 02E 06 2 26E 03 4 19E 04 2 67E 03 2 68E 03 NO
M 225 Maximum Onsite Annual 387369 4610080 1381 4 72E 06 1 73E 08 1 07E 07 2 OOE 09 4 85E 06 3 53E 04 8 62E 05 4 39E 04 4 44E 04 NO
NOT APPLICABLE TO ONSITE LOCATIONS
The State of Utah has adopted the National Ambient Air Quality Standards
TABLE 19
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON AVERAGE OBODI EMISSION FACTORS
Page 1 of 3
Maximum Onsite Receptor for M 135
UTM East I 380472 | UTM North | 4615866
Chemical M136 Source A Ml 36 Source B M136 Source C M136 Source D OSHA TWA^ Exceedance Chemical
8 hour Air Concentration (pg/m') (pg/m')
Exceedance
Metals
Aluminum 3 69E 02 1 56E-01 2 22E 01 1 49E-02 1 OOE+03 NO
Antimony 1 58E 05 6 66E 05 9 50E 05 6 40E 06 5 OOE+02 NO
Arsenic 2 26E-07 9 53E 07 1 36E 06 9 15E 08 1 OOE+01 NO
Banum 3 39E 06 1 43E 05 2 04E 05 1 38E 06 5 OOE+02 NO
Beryllium 7 73E 08 3 26E 07 4 65E 07 3 13E 08 2 OOE+00 NO
Cadmium 2 15E 07 9 07E 07 1 29E 06 8 70E 08 1 OOE+01 NO
Chromium 1 32E 05 5 57E-05 7 95E 05 5 35E 06 5 OOE+02 NO
Cobalt 2 25E 07 9 51E 07 1 35E 06 9 13E 08 2 OOE+01 NO
Copper 1 09E 05 4 61E 05 6 57E 05 4 43E 06 1 OOE+03 NO
Lead 1 42E-05 5 98E 05 8 53E 05 5 75E 06 5 OOE+01 NO
Magnesium 1 27E-05 5 35E 05 7 63E-05 5 14E 06 1 OOE+04 NO
Manganese 3 36E 05 1 42E 04 2 02E 04 1 36E 05 2 OOE+02 NO
Mercury 2 76E 08 1 16E 07 1 66E 07 1 12E-08 2 50E+01 NO
Nickel 2 51E 05 1 06E-04 1 51E 04 1 02E-05 1 50E+03 NO
Phosphorus 9 35E 05 3 95E-04 5 63E 04 3 79E 05 1 OOE+02 NO
Selenium 1 12E 06 4 74E 06 6 75E-06 4 55E 07 2 OOE+02 NO
Silver 5 33E 07 2 25E 06 3 21E 06 2 16E 07 1 OOE+02 NO
Thallium 1 50E 06 6 35E 06 9 05E 06 6 09E 07 1 OOE+02 NO
Zinc 9 78E 06 4 13E 05 5 89E 05 3 97E-06 2 OOE+03 NO
SVOCs
1 2 Dichlorobenzene 2 OOE 07 8 45E 07 1 21E-06 8 12E-08 6 OOE+04 NO
1 3 Dinitrobenzene 2 04E-07 8 62E 07 1 23E 06 8 28E-08 1 03E+03 NO
2 Methylnaphthalene 1 89E 06 7 96E 06 1 14E 05 7 65E 07 2 90E+03 NO
Acetophenone 1 70E 06 7 19E-06 1 02E 05 6 OOE 07 4 90E+04 NO
Aniline 2 87E 06 1 21E 05 1 73E 05 1 16E 06 7 60E+03 NO
Diethyl phthalate 2 99E 07 1 26E 06 1 80E 06 1 21E 07 5 OOE+03 NO
Dimethyl phthalate 1 96E 07 8 29E 07 1 18E 06 7 96E 08 5 OOE+03 NO
Diphenylamine 1 96E 07 8 29E 07 1 18E 06 7 96E 08 1 OOE+04 NO
Hexachlorobenzene 2 28E 06 9 64E 06 1 37E 05 9 25E 07 2 OOE+00 NO
Hexachlorobutadiene 2 91E 07 1 23E 06 1 75E 06 1 18E 07 2 OOE+01 NO
Hexachlorocyclopentadiene 3 93E 06 1 66E 05 2 36E-05 1 59E-06 1 OOE+01 NO
Hexachloroethane 2 12E-07 8 95E 07 1 28E 06 8 59E 08 1 OOE+03 NO
Naphthalene 8 17E 06 3 45E 05 4 91E 05 3 31E 06 5 23E+04 NO
Nitrobenzene 2 24E 07 9 45E 07 1 35E 06 9 07E 08 5 02E+03 NO
0 Toluidine 2 51E 06 1 06E-05 1 51E-05 1 02E 06 8 75E+03 NO
Pentachloronitrobenzene 1 96E 07 8 29E 07 1 18E 06 7 96E 08 5 OOE+02 NO
Pentachlorophenol 9 82E 06 4 14E 05 5 91E05 3 98E 06 5 OOE+02 NO
Phenol 1 41E 06 5 94E-06 8 47E 06 5 70E-07 1 92E+04 NO
Pyndine 2 91E-07 1 23E 06 1 75E 06 1 18E 07 3 23E+03 NO
Carbonyis
Acetone 8 87E 06 3 75E 05 5 34E 05 3 60E 06 1 18E+06 NO
HCI/CI2/NH3
NH3 1 77E 05 7 47E 05 1 06E-04 7 17E 06 1 74E+04 NO
HCN 8 90E 06 3 76E 05 5 36E 05 3 61E 06 519E+03 NO
TABLE 19
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON AVERAGE OBODI EMISSION FACTORS
Page 2 of 3
Maximum Onsite Receptor for M 135
UTM East I 380472 | UTM North | 4615866
Chemical M136 Source A M136 Source B Ml 36 Source C M136 Source D OSHA TWA^
(Mg/m') Exceedance Chemical
8 hour Air Concentration (pg/m')
OSHA TWA^
(Mg/m') Exceedance
VOCs
112 2 Tetrachloroethane 1 46E 07 6 17E-07 8 80E-07 5 93E 08 6 85E+03 NO
1 1-Dichloroethane 1 10E 07 4 63E 07 6 59E 07 4 44E-08 4 04E+05 NO
1 3 Butadiene 6 46E 06 2 73E 05 3 89E 05 2 62E 06 4 42E+03 NO
1 4 Dioxane 2 20E 07 9 29E-07 1 32E-06 8 92E 08 719E+04 NO
1 Butene 1 23E 05 5 20E 05 7 42E-05 4 99E 06 5 73E+05 NO
1 Hexene 1 11E 05 4 71E-05 6 71E-05 4 52E 06 1 72E+05 NO
2 Nitropropane 9 55E 07 4 03E 06 5 75E 06 3 87E 07 3 64E+04 NO
2 Propanol 1 03E 07 4 34E 07 6 19E-07 417E08 4 91E+05 NO
Acetone 1 22E-05 5 14E-05 7 32E-05 4 93E 06 1 18E+06 NO
Acetonitnle 5 90E 06 2 49E 05 3 55E 05 2 39E-06 3 35E+04 NO
Acrylonitnle 5 38E 06 2 27E 05 3 24E-05 2 18E-06 4 33E+03 NO
Benzene 2 94E-05 1 24E 04 1 77E 04 1 19E 05 1 59E+03 NO
Bromoform 4 33E 07 1 83E 06 2 61E 06 1 76E 07 516E+03 NO
Carbon Disulfide 5 47E 06 2 31E 05 3 29E-05 2 22E-06 311E+03 NO
Carbon Tetrachlonde 1 17E-05 4 96E-05 7 06E 05 4 76E 06 314E+04 NO
Chlorobenzene 1 43E 06 6 03E 06 8 60E-06 5 79E 07 4 59E+04 NO
Chloroform 4 23E 06 1 79E 05 2 54E-05 1 71E-06 4 87E+04 NO
cis-1 2-Dichloroethene 1 58E-07 6 66E 07 9 49E 07 6 39E 08 7 91E+05 NO
CIS 1 3 Dichloropropene 4 28E 07 1 81E 06 2 57E 06 1 73E 07 4 53E+03 NO
Cumene 1 43E 07 6 05E 07 8 63E 07 5 81E-08 2 45E+05 NO
Cyclohexane 1 05E-06 4 42E-06 6 29E 06 4 24E 07 3 44E+05 NO
Cyclopentane 6 61E 07 2 79E 06 3 98E-06 2 68E 07 1 72E+06 NO
Ethanol 7 16E 07 3 02E 06 4 31E-06 2 90E 07 1 88E+06 NO
Ethene 9 06E-05 3 83E 04 5 45E 04 3 67E 05 2 29E+05 NO
Ethyl Benzene 1 74E 06 7 36E 06 1 05E 05 7 06E 07 4 33E+05 NO
Ethyl Ether 8 53E 07 3 60E 06 5 13E-06 3 46E 07 1 21E+06 NO
Heptane 4 01E 06 1 69E-05 2 42E 05 1 63E 06 1 64E+06 NO
Hexachlorobutadiene 5 85E-07 2 47E-06 3 52E 06 2 37E 07 213E+02 NO
Hexane 4 89E 06 2 07E 05 2 94E 05 1 98E 06 1 76E+06 NO
m p Xylene 6 02E 06 2 54E 05 3 62E-05 2 44E 06 4 33E+05 NO
Methacryionitnle 1 94E-06 8 21E-06 1 17E 05 7 88E 07 2 74E+03 NO
Methyl Acrylate 4 16E 07 1 76E 06 2 50E 06 1 68E 07 7 03E+03 NO
Methyl Methacrylate 5 37E 07 2 27E 06 3 23E-06 2 18E-07 2 04E+05 NO
Methylcyclohexane 2 67E-06 1 13E 05 1 61E 05 1 08E 06 1 60E+06 NO
Nonane 6 92E 06 2 92E 05 4 17E 05 2 81E 06 1 05E+06 NO
Octane 4 50E 06 1 90E 05 2 71E 05 1 83E-06 1 40E+06 NO
0 Xylene 2 29E 06 9 66E 06 1 38E 05 9 27E 07 4 33E+05 NO
Pentane 1 14E 05 4 81E 05 6 86E-05 4 62E 06 1 77E+06 NO
Propylene 2 82E 05 1 19E 04 1 70E 04 1 14E-05 8 59E+05 NO
Styrene 3 65E 07 1 54E-06 2 20E 06 1 48E 07 8 50E+04 NO
Tetrachloroethene 1 55E-06 6 56E 06 9 34E 06 6 29E 07 1 69E+05 NO
Tetrahydrofuran 4 58E 07 1 93E 06 2 76E 06 1 86E 07 1 47E+05 NO
Toluene 1 20E 05 5 06E-05 7 21E 05 4 86E 06 7 52E+04 NO
trans 1 2 Dichloroethene 2 51E-07 1 06E-06 1 51E 06 1 02E 07 7 91E+05 NO
trans 1 3 Dichloropropene 2 10E 07 8 86E 07 1 26E 06 8 50E 08 4 53E+03 NO
trans 2 butene 4 57E 06 1 93E 05 2 75E-05 1 85E 06 5 73E+05 NO
Tnchloroethene 4 29E 07 1 81E 06 2 58E 06 1 74E 07 5 36E+04 NO
Vinyl Chlonde 2 96E 06 1 25E-05 1 78E 05 1 20E 06 2 55E+03 NO
TABLE 19
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON AVERAGE OBODI EMISSION FACTORS
Page 3 of 3
Maximum Onsite Receptor for M 135
UTM East I 380472 | UTM North | 4615866
Chemical M136 Source A M136 Source B M136 Source C M136 Source D OSHA TWA^
(pg/m') Exceedance Chemical
8 hour Air Concentration {\iglm')
OSHA TWA^
(pg/m') Exceedance
CEM
C02 7 76E 01 3 28E+00 4 67E+00 3 14E-01 8 98E+06 NO
CO 2 39E 03 1 01E 02 1 44E 02 9 69E-04 2 86E+04 NO
NOX 3 53E 03 1 49E 02 2 13E 02 1 43E 03 8 98E+04 NO
S02 1 62E 04 6 85E 04 9 76E 04 6 58E 05 5 23E+03 NO
1 Source 2008 TLVs for Chemical Substances and Physical Agents Amencan Council of Government Industnal Hygienists (ACGIH)
TABLE 20
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 1 of 3
Maximum Onsite Receptor for M 135
UTM East I 380472 | UTM North | 4615866"
Maximum M136 Source M136 M136 Source M136 Source
OSHA TWA^ Chemical OBODI A Source B C D OSHA TWA^ Exceedance Chemical Emission
Factor (lb/lb) 8 hour Air Concentration (pg/m') (Mg/m')
Exceedance
Metals
Aluminum 3 8E 02 5 25E 02 2 22E 01 3 16E 01 2 13E 02 1 OOE+03 NO
Antimony 2 3E 05 3 20E 05 1 35E 04 1 93E 04 1 30E-05 5 OOE+02 NO
Arsenic 2 5E 07 3 44E 07 1 45E 06 2 07E-06 1 39E 07 1 OOE+01 NO
Banum 3 3E-06 4 53E 06 1 91E 05 2 73E 05 1 84E 06 5 OOE+02 NO
Beryllium 7 5E 08 1 02E-07 4 29E 07 6 12E 07 4 12E-08 2 OOE+00 NO
Cadmium 2 IE 07 2 82E 07 1 19E-06 1 70E 06 1 14E 07 1 OOE+01 NO
Chromium 1 2E-05 1 70E 05 7 17E 05 1 02E 04 6 88E 06 5 OOE+02 NO
Cobalt 2 1E-07 2 82E 07 1 19E-06 1 70E 06 1 14E 07 2 OOE+01 NO
Copper 1 5E 05 211E05 8 89E 05 1 27E-04 8 54E 06 1 OOE+03 NO
Lead 2 3E 05 3 16E 05 1 33E 04 1 90E 04 1 28E 05 5 OOE+01 NO
Magnesium 1 7E 05 2 36E 05 9 95E 05 1 42E 04 9 56E 06 1 OOE+04 NO
Manganese 5 0E 05 6 84E-05 2 89E 04 4 12E 04 2 77E 05 2 OOE+02 NO
Mercury 2 5E-08 3 39E 08 1 43E 07 2 04E-07 1 37E 08 2 50E+01 NO
Nickel 2 2E 05 2 98E-05 1 26E 04 1 79E 04 1 21 E-05 1 50E+03 NO
Phosphorus 9 7E 05 1 32E-04 5 59E 04 7 97E-04 5 37E 05 1 OOE+02 NO
Selenium 1 1E-06 1 49E 06 6 31E 06 8 99E 06 6 06E 07 2 OOE+02 NO
Silver 5 6E 07 7 64E-07 3 23E 06 4 60E 06 3 10E 07 1 OOE+02 NO
Thallium 1 4E 06 1 98E-06 8 35E 06 1 19E-05 8 01E 07 1 OOE+02 NO
Zinc 1 7E-05 2 26E 05 9 53E 05 1 36E 04 9 15E 06 2 OOE+03 NO
SVOCs
1 2-Dichlorobenzene 1 9E 07 2 57E 07 1 09E 06 1 55E 06 1 04E 07 6 OOE+04 NO
1 3 Dinitrobenzene 1 9E-07 2 62E 07 1 11E 06 1 58E 06 1 06E 07 1 03E+03 NO
2 Methylnaphthalene 2 6E 06 3 57E 06 1 51E 05 2 15E-05 1 45E-06 2 90E+03 NO
Acetophenone 2 2E 06 3 01E 06 1 27E-05 1 81E 05 1 22E 06 4 90E+04 NO
Aniline 2 7E 06 3 68E 06 1 55E 05 2 21E 05 1 49E 06 7 60E+03 NO
Diethyl phthalate 2 7E 07 3 68E 07 1 55E-06 2 21E 06 1 49E-07 5 OOE+03 NO
Dimethyl phthalate 1 8E-07 2 52E 07 1 06E 06 1 52E 06 1 02E 07 5 OOE+03 NO
Diphenylamine 1 8E 07 2 52E-07 1 06E 06 1 52E 06 1 02E 07 1 OOE+04 NO
Hexachlorobenzene 3 5E 06 4 78E 06 2 02E-05 2 88E 05 1 94E 06 2 OOE+00 NO
Hexachlorobutadiene 2 7E 07 3 73E 07 1 58E 06 2 25E-06 1 51E 07 2 OOE+01 NO
Hexachlorocyclopentadiene 3 7E 06 5 04E 06 2 13E-05 3 03E 05 2 04E 06 1 OOE+01 NO
Hexachloroethane 2 OE-07 2 72E 07 1 15E 06 1 64E-06 1 10E-07 1 OOE+03 NO
Naphthalene 1 1E 05 1 47E 05 6 20E 05 8 84E-05 5 96E 06 5 23E+04 NO
Nitrobenzene 2 1E-07 2 87E-07 1 21E 06 1 73E 06 1 16E-07 5 02E+03 NO
o-Toluidine 2 4E-06 3 23E 06 1 36E 05 1 94E 05 1 31E-06 8 75E+03 NO
Pentachloronitrobenzene 1 8E 07 2 52E-07 1 06E 06 1 52E 06 1 02E 07 5 OOE+02 NO
Pentachlorophenol 9 2E 06 1 26E-05 5 32E 05 7 59E 05 511E06 5 OOE+02 NO
Phenol 1 6E-06 2 19E 06 9 26E 06 1 32E 05 8 89E-07 1 92E+04 NO
Pyndine 2 7E 07 3 73E 07 1 58E-06 2 25E-06 1 51E 07 3 23E+03 NO
Carbonyis
Acetone 7 9E 06 1 07E-05 4 53E 05 6 45E 05 4 34E 06 1 18E+06 NO
HCI/CI2/NH3
NHS 1 7E 05 2 30E 05 9 71E-05 1 38E 04 9 32E 06 1 74E+04 NO
HCN 7 7E 06 1 06E 05 4 46E 05 6 36E 05 4 28E-06 519E+03 NO
TABLE 20
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 2 of 3
Maximum Onsite Receptor for M 135
UTM East I 380472 | UTM North | 4615866
Maximum M136 Source Ml 36 M136 Source M136 Source
Chemical OBODI A Source B C D OSHA TWA' Exceedance Chemical Emission
Factor (lb/lb) 8 hour Air Concentration {\iglm') (pg/m')
Exceedance
VOCs
112 2 Tetrachloroethane 1 4E 07 1 91E-07 8 06E 07 1 15E 06 7 74E 08 6 85E+03 NO
1 1 Dichloroethane 1 IE 07 1 45E-07 6 13E 07 8 73E-07 5 88E 08 4 04E+05 NO
1 3 Butadiene 1 IE 05 1 53E-05 6 47E 05 9 23E-05 6 21E 06 4 42E+03 NO
1 4 Dioxane 2 IE 07 2 89E 07 1 22E 06 1 74E 06 1 17E 07 719E+04 NO
1 Butene 1 9E 05 2 53E 05 1 07E-04 1 52E 04 1 03E-05 5 73E+05 NO
1 Hexene 1 7E 05 2 26E 05 9 55E-05 1 36E 04 9 17E-06 1 72E+05 NO
2 Nitropropane 1 4E 06 1 87E 06 7 91E06 1 13E 05 7 59E 07 3 64E+04 NO
2-Propanol 9 9E-08 1 35E 07 5 72E 07 8 15E 07 5 49E-08 4 91E+05 NO
Acetone 1 2E 05 1 59E-05 6 70E 05 9 56E 05 6 44E 06 1 18E+06 NO
Acetonitnle 7 6E 06 1 04E 05 4 40E 05 6 28E 05 4 23E 06 3 35E+04 NO
Acrylonitnle 6 9E 06 9 40E 06 3 97E-05 5 66E 05 3 81E-06 4 33E+03 NO
Benzene 3 7E 05 5 03E 05 2 12E-04 3 03E-04 2 04E 05 1 59E+03 NO
Bromofonn 4 2E 07 5 70E-07 2 41E 06 3 43E-06 2 31E 07 516E+03 NO
Carbon Disulfide 7 5E-06 1 02E 05 4 31E 05 6 15E-05 4 14E 06 311E+03 NO
Carbon Tetrachloride 1 3E 05 1 75E-05 7 39E-05 1 05E 04 7 10E-06 314E+04 NO
Chlorobenzene 2 IE 06 2 83E 06 1 19E 05 1 70E 05 1 15E-06 4 59E+04 NO
Chloroform 5 0E 06 6 84E 06 2 89E-05 4 11E 05 2 77E 06 4 87E+04 NO
CIS 1 2 Dichloroethene 1 5E-07 2 08E 07 8 77E 07 1 25E 06 8 42E 08 7 91E+05 NO
CIS 1 3-Dichioropropene 7 7E-07 1 04E-06 4 41E 06 6 29E 06 4 23E 07 4 53E+03 NO
Cumene 1 4E 07 1 OOE 07 8 01E 07 1 14E 06 7 69E 08 2 45E+05 NO
Cyclohexane 1 5E-06 1 99E 06 8 41E 06 1 20E 05 8 08E 07 3 44E+05 NO
Cyclopentane 7 4E 07 1 01E 06 4 26E-06 6 07E-06 4 09E 07 1 72E+06 NO
Ethanol 9 6E 07 1 32E 06 5 55E 06 7 92E-06 5 33E 07 1 88E+06 NO
Ethene 1 4E 04 1 87E-04 7 91E-04 1 13E 03 7 59E-05 2 29E+05 NO
Ethyl Benzene 2 4E 06 3 26E-06 1 38E 05 1 96E 05 1 32E-06 4 33E+05 NO
Ethyl Ether 8 3E 07 1 13E 06 4 77E-06 6 79E 06 4 58E 07 1 21E+06 NO
Heptane 5 6E 06 7 62E-06 3 22E 05 4 59E 05 3 09E 06 1 64E+06 NO
Hexachlorobutadiene 5 6E-07 7 69E 07 3 25E 06 4 63E 06 3 12E 07 213E+02 NO
Hexane 7 3E-06 9 90E 06 4 18E 05 5 96E 05 4 01E06 1 76E+06 NO
m p-Xylene 8 6E-06 1 17E 05 4 93E 05 7 02E 05 4 73E 06 4 33E+05 NO
Methacryionitnle 1 9E 06 2 63E 06 1 11E 05 1 58E-05 1 06E 06 2 74E+03 NO
Methyl Acrylate 4 0E 07 5 44E 07 2 30E 06 3 28E 06 2 21E-07 7 03E+03 NO
Methyl Methacrylate 5 3E-07 7 19E 07 3 04E 06 4 33E 06 2 91E07 2 04E+05 NO
Methylcyclohexane 4 0E 06 5 40E-06 2 28E 05 3 25E 05 2 19E 06 1 60E+06 NO
Nonane 1 IE 05 1 46E-05 6 17E 05 8 79E 05 5 92E 06 1 05E+06 NO
Octane 6 8E 06 9 26E 06 3 91E 05 5 57E 05 3 75E 06 1 40E+06 NO
0 Xylene 2 9E-06 4 02E 06 1 70E 05 2 42E 05 1 63E 06 4 33E+05 NO
Pentane 1 6E 05 2 13E-05 9 01E 05 1 28E 04 8 65E 06 1 77E+06 NO
Propylene 3 9E 05 5 32E 05 2 25E 04 3 20E-04 2 16E-05 8 59E+05 NO
Styrene 3 8E 07 5 17E 07 2 18E 06 3 11E 06 2 10E 07 8 50E+04 NO
Tetrachloroethene 1 9E 06 2 57E-06 1 09E 05 1 55E 05 1 04E 06 1 69E+05 NO
Tetrahydrofuran 5 7E 07 7 77E 07 3 28E 06 4 67E 06 3 15E 07 1 47E+05 NO
Toluene 1 7E 05 2 28E 05 9 65E 05 1 37E 04 9 26E-06 7 52E+04 NO
trans 1 2 Dichloroethene 2 4E-07 3 29E 07 1 39E 06 1 98E 06 1 33E 07 7 91E+05 NO
trans 1 3 Dichloropropene 2 0E 07 2 76E 07 1 17E 06 1 66E-06 1 12E-07 4 53E+03 NO
trans 2 butene 5 8E 06 7 89E 06 3 33E 05 4 75E 05 3 20E-06 5 73E+05 NO
Tnchloroethene 4 9E 07 6 68E 07 2 82E 06 4 02E 06 2 71E 07 5 36E+04 NO
Vinyl Chlonde 4 4E 06 6 03E-06 2 55E 05 3 63E 05 2 44E 06 2 55E+03 NO
TABLE 20
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M-136 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 3 of 3
Maximum Onsite Receptor for M 135
UTM East I 380472 | UTM North | 4615866
Chemical
Maximum
OBODI
Emission
Factor (lb/lb)
M136 Source
A
M136
Source B
M136 Source
C
M136 Source
D OSHA TWA^
(pg/m') Exceedance Chemical
Maximum
OBODI
Emission
Factor (lb/lb) 8 hour Air Concentration (pg/m')
OSHA TWA^
(pg/m') Exceedance
CEM
C02 6 2E 01 8 47E 01 3 58E+00 510E+00 3 43E-01 8 98E+06 NO
CO 4 0E 03 5 41E 03 2 28E-02 3 25E 02 2 19E 03 2 86E+04 NO
NOX 3 8E-03 5 16E 03 2 18E 02 3 11E 02 2 09E 03 8 98E+04 NO
S02 1 7E 04 2 33E 04 9 82E 04 1 40E 03 9 43E-05 5 23E+03 NO
1 Source 2008 TLVs for Chemical Substances and Physical Agents Amencan Council of Government Industnal Hygienists (ACGIH)
TABLE 21
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 1 of 3
Maximum Onsite Receptor for M 225
UTM East I 386268 | UTM North | 4609480"
M225 M225 OBODI M22S M225 Source
Chemical Source A Source B Average Source A B OSHA TWA' Exceedance Chemical 1 Hour Air Dispersion Emission 8 hour Air Concentration (pg/m') Exceedance
Factor (p/m' lb/lb) Factor (lb/lb) iv g/m')
(pg/m')
Metals
Aluminum 171 6 76 7 2 7E 02 5 80E 01 2 59E 01 1 OOE+03 No
Antimony 171 6 76 7 1 2E 05 2 48E 04 1 11E 04 5 OOE+02 No
Arsenic 171 6 76 7 1 7E 07 3 55E 06 1 59E 06 1 OOE+01 No
Banum 171 6 76 7 2 5E 06 5 34E 05 2 39E 05 5 OOE+02 No
Beryllium 171 6 76 7 5 7E 08 1 22E 06 5 43E 07 2 OOE+00 No
Cadmium 171 6 76 7 1 6E 07 3 38E 06 1 51E 06 1 OOE+01 No
Chromium 171 6 76 7 9 7E 06 2 08E 04 9 27E 05 5 OOE+02 No
Cobalt 171 6 76 7 1 7E 07 3 54E 06 1 58E 06 2 OOE+01 No
Copper 171 6 76 7 8 0E 06 1 72E 04 7 67E 05 1 OOE+03 No
Lead 171 6 76 7 1 OE 05 2 23E 04 9 96E 05 5 OOE+01 No
Magnesium 171 6 76 7 9 3E 06 1 99E 04 8 90E 05 1 OOE+04 No
Manganese 171 6 76 7 2 5E 05 5 28E 04 2 36E 04 2 OOE+02 No
Mercury 171 6 76 7 2 0E 08 4 34E 07 1 94E 07 2 50E+01 No
Nickel 171 6 76 7 1 8E 05 3 95E 04 1 77E 04 1 50E+03 No
Phosphorus 171 6 76 7 6 9E 05 1 47E 03 6 57E 04 1 OOE+02 No
Selenium 171 6 76 7 8 2E 07 1 76E 05 7 88E 06 2 OOE+02 No
Silver 171 6 76 7 3 9E 07 8 39E 06 3 75E 06 1 OOE+02 No
Thallium 171 6 76 7 1 IE 06 2 36E 05 1 06E 05 1 OOE+02 No
Zinc 171 6 76 7 7 2E 06 1 54E 04 6 87E 05 2 OOE+03 No
SVOCs
1 2 Dichlorobenzene 171 6 76 7 1 5E 07 3 15E 06 1 41E 06 6 OOE+04 No
1 3 Dinitrobenzene 171 6 76 7 1 5E 07 3 21E 06 1 43E 06 1 03E+03 No
2 Methylnaphthalene 171 6 76 7 1 4E 06 2 97E 05 1 33E 05 2 90E+03 No
Acetophenone 171 6 76 7 1 2E 06 2 68E 05 1 20E 05 4 90E+04 No
Aniline 171 6 76 7 2 IE 06 4 51E 05 2 01E 05 7 60E+03 No
Diethyl phthalate 171 6 76 7 2 2E 07 4 70E 06 2 10E 06 5 OOE+03 No
Dimethyl phthalate 171 6 76 7 1 4E 07 3 09E 06 1 38E 06 5 OOE+03 No
Diphenylamine 171 6 76 7 1 4E 07 3 09E 06 1 38E 06 1 OOE+04 No
Hexachlorobenzene 171 6 76 7 1 7E 06 3 59E 05 1 60E 05 2 OOE+00 No
Hexachlorobutadiene 171 6 76 7 2 IE 07 4 57E 06 2 04E 06 2 OOE+01 No
Hexachlorocyclopentadiene 171 6 76 7 2 9E 06 6 17E 05 2 76E 05 1 OOE+01 No
Hexachloroethane 171 6 76 7 1 6E 07 3 33E 06 1 49E 06 1 OOE+03 No
Naphthalene 171 6 76 7 6 0E 06 1 28E 04 5 74E 05 5 23E+04 No
Nitrobenzene 171 6 76 7 1 6E 07 3 52E 06 1 57E 06 5 02E+03 No
0 Toluidine 171 6 76 7 1 8E 06 3 95E 05 1 77E 05 8 75E+03 No
Pentachloronitrobenzene 171 6 76 7 1 4E 07 3 09E 06 1 38E 06 5 OOE+02 No
Pentachlorophenol 171 6 76 7 7 2E 06 1 54E 04 6 90E 05 5 OOE+02 No
Phenol 171 6 76 7 1 OE 06 2 21E05 9 89E 06 1 92E+04 No
Pyndine 171 6 76 7 2 IE 07 4 57E 06 2 04E 06 3 23E+03 No
Carbonyis
Acetone 171 6 76 7 6 5E 06 1 39E 04 6 23E 05 1 18E+06 No
TABLE 21
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 138 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 2 of 3
Maximum Onsite Receptor for M 225
UTM East I 386268 | UTM North | 4609480"
M225 M225 OBODI M225 M225 Source
Chemical Source A Source B Average Source A B OSHA TWA^ Exceedance Chemical 1 Hour Air Dispersion Emission 8 hour Air Concentration (pg/m') Exceedance
Factor (p/m' lb/lb) Factor (lb/lb) (P q/m')
(pg/m')
HCI/CI2/NH3
NH3 171 6 76 7 1 3E 05 2 78E 04 1 24E 04 1 74E+04 No
HCN 171 6 76 7 6 5E06 1 40E 04 6 25E 05 519E+03 No
VOCs
112 2 Tetrachloroethane 171 6 76 7 1 1E 07 2 30E 06 1 03E 06 6 85E+03 No
1 1 Dichloroethane 171 6 76 7 8 0E 08 1 72E 06 7 70E 07 4 04E+05 No
1 3 Butadiene 171 6 76 7 4 7E06 1 02E 04 4 54E 05 4 42E+03 No
1 4 Dioxane 171 6 76 7 1 6E 07 3 46E 06 1 55E 06 719E+04 No
1 Butene 171 6 76 7 OOE 06 1 94E 04 8 66E 05 5 73E+05 No
1 Hexene 171 6 76 7 8 2E 06 1 75E 04 7 83E 05 1 72E+05 No
2 Nitropropane 171 6 76 7 7 0E 07 1 50E 05 6 71E 06 3 64E+04 No
2 Propanol 171 6 76 7 7 5E 08 1 62E 06 7 22E 07 4 91E+05 No
Acetone 171 6 76 7 8 9E 06 1 91E 04 8 55E 05 1 18E+06 No
Acetonitnle 171 6 76 7 4 3E 06 9 27E 05 414E 05 3 35E+04 No
Acrylonitnle 171 6 76 7 3 9E 06 8 46E 05 3 78E 05 4 33E+03 No
Benzene 171 6 76 7 2 2E 05 4 63E 04 2 07E 04 1 59E+03 No
Bromoform 171 6 76 7 3 2E 07 6 81E06 3 04E 06 516E+03 No
Carbon Disulfide 171 6 76 7 4 0E 06 8 59E 05 3 84E 05 311E+03 No
Carbon Tetrachlonde 171 6 76 7 8 6E 06 1 85E 04 8 25E 05 314E+04 No
Chlorobenzene 171 6 76 7 1 OE 06 2 25E 05 1 OOE 05 4 59E+04 No
Chlorofomi 171 6 76 7 3 IE 06 6 65E 05 2 97E 05 4 87E+04 No
CIS 1 2 Dichloroethene 171 6 76 7 1 2E 07 2 48E 06 1 11E 06 7 91E+05 No
CIS 1 3 Dichloropropene 171 6 76 7 3 IE 07 6 72E 06 3 OOE 06 4 53E+03 No
Cumene 171 6 76 7 1 IE 07 2 25E 06 1 01E 06 2 45E+05 No
Cyclohexane 171 6 76 7 7 7E 07 1 64E 05 7 35E 06 3 44E+05 No
Cyclopentane 171 6 76 7 4 8E 07 1 04E 05 4 64E 06 1 72E+06 No
Ethanol 171 6 76 7 5 2E 07 1 13E 05 5 03E 06 1 88E+06 No
Ethene 171 6 76 7 6 6E 05 1 42E 03 6 37E 04 2 29E+05 No
Ethyl Benzene 171 6 76 7 1 3E 06 2 74E 05 1 22E 05 4 33E+05 No
Ethyl Ether 171 6 76 7 6 3E 07 1 34E 05 5 99E 06 1 21E+06 No
Heptane 171 6 76 7 2 9E 06 6 31E 05 2 82E 05 1 64E+06 No
Hexachlorobutadiene 171 6 76 7 4 3E 07 9 19E 06 4 11E 06 213E+02 No
Hexane 171 6 76 7 3 6E 06 7 69E 05 3 44E 05 1 76E+06 No
m p Xylene 171 6 76 7 4 4E06 9 47E 05 4 23E 05 4 33E+05 No
Methacryionitnle 171 6 76 7 1 4E 06 3 06E 05 1 37E 05 2 74E+03 No
Methyl Acrylate 171 6 76 7 3 0E 07 6 54E 06 2 92E 06 7 03E+03 No
Methyl Methacrylate 171 6 76 7 3 9E 07 8 44E 06 3 77E 06 2 04E+05 No
Methylcyclohexane 171 6 76 7 2 0E 06 4 20E 05 1 88E 05 1 60E+06 No
Nonane 171 6 76 7 5 IE 06 1 OOE 04 4 87E 05 1 05E+06 No
Octane 171 6 76 7 3 3E 06 7 08E 05 3 16E 05 1 40E+06 No
0 Xylene 171 6 76 7 1 7E 06 3 60E 05 1 61E 05 4 33E+05 No
Pentane 171 6 76 7 8 4E 06 1 79E 04 8 01E 05 1 77E+06 No
Propylene 171 6 76 7 2 IE 05 4 44E 04 1 98E 04 8 59E+05 No
Styrene 171 6 76 7 2 7E 07 5 74E 06 2 56E 06 8 50E+04 No
Tetrachloroethene 171 6 76 7 1 1E 06 2 44E 05 1 09E 05 1 69E+05 No
Tetrahydrofuran 171 6 76 7 3 4E 07 7 20E 06 3 22E 06 1 47E+05 No
Toluene 171 6 76 7 8 8E 06 1 88E 04 8 42E 05 7 52E+04 No
trans 1 2 Dichloroethene 171 6 76 7 1 8E 07 3 94E 06 1 76E 06 7 91E+05 No
trans 1 3 Dichloropropene 171 6 76 7 1 5E 07 3 30E 06 1 47E 06 4 53E+03 No
trans 2 butene 171 6 76 7 3 4E 06 7 19E 05 3 21E 05 5 73E+05 No
Tnchloroethene 171 6 76 7 3 IE 07 6 74E 06 3 01E 06 5 36E+04 No
Vinyl Chlonde 171 6 76 7 2 2E06 4 65E 05 2 08E 05 2 55E+03 No
TABLE 21
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 3 of 3
Maximum Onsite Receptor for M 225
UTM East I 386268 | UTM North | 4609480"
Chemical
M225
Source A
M225
Source B
OBODI
Average
Emission
Factor (lb/lb)
M225
Source A
M225 Source
B OSHA TWA^
(pg/m')
Exceedance Chemical 1 Hour Air Dispersion
Factor (p/m' lb/lb)
OBODI
Average
Emission
Factor (lb/lb)
8 hour Air (
(M
Concentration
3/m')
OSHA TWA^
(pg/m')
Exceedance
CEM
C02 171 6 76 7 5 7E 01 1 22E+01 5 45E+00 8 98E+06 No
CO 171 6 76 7 1 753E 03 3 76E 02 1 68E 02 2 86E+04 No
NOX 171 6 76 7 2 6E 03 5 56E 02 2 48E 02 8 98E+04 No
S02 171 6 76 7 1 2E 04 2 55E 03 1 14E 03 5 23E+03 No
1 Source 2008 TLVs for Chemical Substances and Physical Agents American Council of Government Industnal Hygienists (ACGIH)
TABLE 22
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 1 of 3
Maximum Onsite Receptor for M 225
UTM East I 386268 | UTM North | 4609480~
M225 M22S OBODI M22S M225 Source
Chemical Source A Source B Maximum Source A B OSHA TWA^ Exceedance Chemical 1 Hour Air Dispersion Emission 8 hour Air Concentration (pg/m') Exceedance
Factor (p/m' lb/lb) Factor (lb/lb) (pg/m')
(pg/m')
Metals
Aluminum 171 6 76 7 2 7E-02 5 BOE 01 2 59E 01 1 OOE+03 No
Antimony 171 6 76 7 1 2E 05 2 48E 04 1 11E 04 5 OOE+02 No
Arsenic 171 6 76 7 1 7E 07 3 55E 06 1 59E 06 1 OOE+01 No
Banum 171 6 76 7 2 5E 06 5 34E 05 2 39E 05 5 OOE+02 No
Beryllium 171 6 76 7 5 7E-08 1 22E 06 5 43E 07 2 OOE+00 No
Cadmium 171 6 76 7 1 6E07 3 38E06 1 51E 06 1 OOE+01 No
Chromium 171 6 76 7 9 7E 06 2 08E 04 9 27E 05 5 OOE+02 No
Cobalt 171 6 76 7 1 7E 07 3 54E 06 1 58E-06 2 OOE+01 No
Copper 171 6 76 7 8 0E 06 1 72E 04 7 67E 05 1 OOE+03 No
Lead 171 6 76 7 10E 05 2 23E-04 9 96E-05 5 OOE+01 No
Magnesium 171 6 76 7 9 3E-06 1 99E 04 B 90E 05 1 OOE+04 No
Manganese 171 6 76 7 2 5E 05 5 2BE 04 2 36E 04 2 OOE+02 No
Mercury 171 6 76 7 2 0E 08 4 34E-07 1 94E 07 2 50E+01 No
Nickel 171 6 76 7 1 BE 05 3 95E 04 1 77E 04 1 50E+03 No
Phosphorus 171 6 76 7 6 9E 05 1 47E-03 6 57E 04 1 OOE+02 No
Selenium 171 6 76 7 8 2E 07 1 76E 05 7 BSE 06 2 OOE+02 No
Silver 171 6 76 7 3 9E 07 8 39E 06 3 75E 06 1 OOE+02 No
Thallium 171 6 76 7 1 IE 06 2 36E-05 1 06E 05 1 OOE+02 No
Zinc 171 6 76 7 7 2E 06 1 54E 04 6 B7E 05 2 OOE+03 No
SVOCs
1 2 Dichlorobenzene 171 6 76 7 1 5E07 3 15E 06 1 41E 06 6 OOE+04 No
1 3 Dinitrobenzene 171 6 76 7 1 5E-07 3 21E 06 1 43E 06 1 03E+03 No
2 Methylnaphthalene 171 6 76 7 1 4E 06 2 97E 05 1 33E 05 2 90E+03 No
Acetophenone 171 6 76 7 1 2E06 2 68E 05 1 20E-05 4 90E+04 No
Aniline 171 6 76 7 2 IE 06 4 51E 05 2 01E 05 7 60E+03 No
Diethyl phthalate 171 6 76 7 2 2E-07 4 70E 06 2 10E 06 5 OOE+03 No
Dimethyl phthalate 171 6 76 7 1 4E 07 3 09E 06 1 38E 06 5 OOE+03 No
Diphenylamine 171 6 76 7 1 4E 07 3 09E 06 1 38E 06 1 OOE+04 No
Hexachlorobenzene 171 6 76 7 1 7E 06 3 59E 05 1 60E-05 2 OOE+00 No
Hexachlorobutadiene 171 6 76 7 2 IE 07 4 57E 06 2 04E 06 2 OOE+01 No
Hexachlorocyclopentadiene 171 6 76 7 2 9E06 6 17E-05 2 76E 05 1 OOE+01 No
Hexachloroethane 171 6 76 7 1 6E 07 3 33E 06 1 49E-06 1 OOE+03 No
Naphthalene 171 6 76 7 6 0E06 1 2BE-04 5 74E 05 5 23E+04 No
Nitrobenzene 171 6 76 7 1 BE 07 3 52E 06 1 57E 06 5 02E+03 No
0 Toluidine 171 6 76 7 1 8E 06 3 95E 05 1 77E 05 8 75E+03 No
Pentachloronitrobenzene 171 6 76 7 1 4E 07 3 09E 06 1 38E 06 5 OOE+02 No
Pentachlorophenol 171 6 76 7 7 2E 06 1 54E 04 6 90E 05 5 OOE+02 No
Phenol 171 6 76 7 1 OE 06 2 21E05 9 89E 06 1 92E+04 No
Pyndine 171 6 76 7 2 1E 07 4 57E-06 2 04E 06 3 23E+03 No
Carbonyis
Acetone 171 6 76 7 6 5E 06 1 39E 04 6 23E 05 1 1BE+06 No
TABLE 22
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 136 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 2 of 3
UTM East
Maximum Onsite Receptor for M 225
UTM North I 46094B0" 386268
M225 M225 OBODI M225 M225 Source
Chemical Source A Source B Maximum Source A B OSHA TWA^ Chemical 1 Hour Air Dispersion Emission 8 hour Air Concentration (pg/m') Exceedance
Factor (p/m' lb/lb) Factor (lb/lb) (pg/m')
(pg/m')
HCI/CI2/NH3
NHS 171 6 76 7 1 3E 05 2 7BE 04 1 24E 04 1 74E+04 No
HCN 171 6 76 7 6 5E 06 1 40E 04 6 25E 05 519E+03 No
VOCs
112 2 Tetrachloroethane 171 6 76 7 1 1E 07 2 30E 06 1 03E 06 6 85E+03 No
1 1 Dichloroethane 171 6 76 7 BOE 08 1 72E 06 7 70E 07 4 04E+05 No
1 3 Butadiene 171 6 76 7 4 7E 06 1 02E 04 4 54E 05 4 42E+03 No
1 4 Dioxane 171 6 76 7 1 6E 07 3 46E 06 1 55E 06 719E+04 No
1 Butene 171 6 76 7 9 OE-06 1 94E 04 B 66E 05 5 73E+05 No
1 Hexene 171 6 76 7 8 2E 06 1 75E 04 7 83E 05 1 72E+05 No
2 Nitropropane 171 6 76 7 7 OE-07 1 50E 05 6 71E 06 3 64E+04 No
2 Propanol 171 6 76 7 7 5E-0B 1 62E 06 7 22E 07 491E+05 No
Acetone 171 6 76 7 8 9E 06 1 91E 04 8 55E 05 1 18E+06 No
Acetonitnle 171 6 76 7 4 3E-06 9 27E 05 4 14E 05 3 35E+04 No
Acrylonitnle 171 6 76 7 3 9E 06 8 46E 05 3 78E 05 4 33E+03 No
Benzene 171 6 76 7 2 2E-05 4 63E 04 2 07E 04 1 59E+03 No
Bromofomi 171 6 76 7 3 2E-07 6B1E 06 3 04E 06 516E+03 No
Carbon Disulfide 171 6 76 7 4 OE-06 8 59E 05 3 B4E 05 311E+03 No
Carbon Tetrachlonde 171 6 76 7 8 6E 06 1 85E 04 8 25E 05 314E+04 No
Chlorobenzene 171 6 76 7 1 OE 06 2 25E 05 1 OOE 05 4 59E+04 No
Chloroform 171 6 76 7 3 1E-06 6 65E 05 2 97E 05 4 87E+04 No
CIS 1 2 Dichloroethene 171 6 76 7 1 2E-07 2 48E 06 1 11E 06 791E+05 No
CIS 1 3 Dichloropropene 171 6 76 7 3 IE 07 6 72E 06 3 OOE 06 4 53E+03 No
Cumene 171 6 76 7 1 IE 07 2 25E 06 1 01E 06 2 45E+05 No
Cyclohexane 171 6 76 7 7 7E-07 1 64E 05 7 35E 06 3 44E+05 No
Cyclopentane 171 6 76 7 4 BE 07 1 04E-05 4 64E 06 1 72E+06 No Ethanol 171 6 76 7 5 2E 07 1 13E 05 5 03E 06 1 B8E+06 No
Ethene 171 6 76 7 6 6E-05 1 42E 03 6 37E 04 2 29E+05 No Ethyl Benzene 171 6 76 7 1 3E 06 2 74E-05 1 22E 05 4 33E+05 No
Ethyl Ether 171 6 76 7 6 3E-07 1 34E 05 5 99E-06 1 21E+06 No
Heptane 171 6 76 7 2 9E 06 6 31 E-05 2 82E 05 164E+06 No
Hexachlorobutadiene 171 6 76 7 4 3E 07 9 19E-06 4 11E 06 213E+02 No
Hexane 171 6 76 7 3 6E 06 7 69E 05 3 44E 05 1 76E+06 No m p Xylene 171 6 76 7 4 4E 06 9 47E 05 4 23E 05 4 33E+05 No
Methacryionitnle 171 6 76 7 1 4E 06 3 06E 05 1 37E 05 2 74E+03 No
Methyl Acrylate 171 6 76 7 3 0E 07 6 54E 06 2 92E 06 7 03E+03 No
Methyl Methacrylate 171 6 76 7 3 9E 07 8 44E 06 3 77E 06 2 04E+05 No
Methylcyclohexane 171 6 76 7 2 0E06 4 20E 05 1 BBE 05 1 60E+06 No Nonane 171 6 76 7 5 1E 06 1 09E 04 4 B7E 05 1 05E+06 No
Octane 171 6 76 7 3 3E-06 7 08E 05 3 16E 05 1 40E+06 No
0 Xylene 171 6 76 7 1 7E 06 3 60E 05 1 61 E-05 4 33E+05 No
Pentane 171 6 76 7 8 4E 06 1 79E 04 8 01 E-05 1 77E+06 No
Propylene 171 6 76 7 2 1E 05 4 44E 04 1 98E-04 B 59E+05 No
Styrene 171 6 76 7 2 7E 07 5 74E 06 2 56E 06 8 50E+04 No
Tetrachloroethene 171 6 76 7 1 IE 06 2 44E 05 1 09E-05 1 69E+05 No
Tetrahydrofuran 171 6 76 7 3 4E 07 7 20E 06 3 22E-06 1 47E+05 No
Toluene 171 6 76 7 BBE 06 1 88E 04 B 42E-05 7 52E+04 No
trans 1 2 Dichloroethene 171 6 76 7 1 8E-07 3 94E 06 1 76E 06 791E+05 No
trans 1 3 Dichloropropene 171 6 76 7 1 5E 07 3 30E 06 1 47E 06 4 53E+03 No
trans 2 butene 171 6 76 7 3 4E 06 7 19E 05 3 21E05 5 73E+05 No
Trichloroethene 171 6 76 7 3 1E 07 6 74E 06 3 01E 06 5 36E+04 No
Vinyl Chlonde 171 6 76 7 2 2E 06 4 65E-05 2 OBE 05 2 55E+03 No
TABLE 22
A COMPARISON OF MAXIMUM 8 HOUR ONSITE CONCENTRATIONS
TO OSHA 8 HOUR TIME WEIGHTED CONCENTRATIONS
AS A RESULT OF M 138 OPERATIONS
BASED ON MAXIMUM OBODI EMISSION FACTORS
Page 3 of 3
Maximum Onsite Receptor for M 225
UTM East I 386268 | UTM North j 4609480
Chemical
M225
Source A
M22S
Source B
OBODI
Maximum
Emission
Factor (lb/lb)
M225
Source A
M22S Source
B OSHA TWA'
(pg/m') Exceedance Chemical 1-Hour Air Dispersion
Factor (p/m' lb/lb)
OBODI
Maximum
Emission
Factor (lb/lb)
8 hour Air Concentration
(pg/m')
OSHA TWA'
(pg/m') Exceedance
CEM
C02 171 6 76 7 5 7E01 1 22E+01 5 45E+00 8 9BE+06 No
CO 171 6 76 7 1 753E 03 3 76E 02 1 68E 02 2 86E+04 No
NOX 171 6 76 7 2 6E 03 5 56E 02 2 48E-02 8 98E+04 No
S02 171 6 76 7 1 2E 04 2 55E-03 1 14E 03 5 23E+03 No
1 Source 2008 TLVs for Chemical Substances and Physical Agents Amencan Council of Govemment Industnal Hygienists (ACGIH)
TABLE 23
CHEMICALS OF POTENTIAL CONCERN
EVALUATED IN HUMAN HEALTH RISK ASSESSMENT
THIOKOL PROPULSION, INC
BRIGHMAN CITY, UTAH
PAGE 1 OF 6
Cas No COPC
Listed in USEPA
HHRAP
Database'^'
Toxicity
Information
Available'^'
Quantitatively
Evaluated'^'
Metals
7429-90 5 Aluminum Yes Yes
7440-36 0 Antimony Yes Yes Yes
7440-38 2 Arsenic Yes Yes Yes
7440-39 3 Banum Yes Yes Yes
7440-41-7 Beryllium Yes Yes Yes
7440-43 9 Cadmium Yes Yes Yes
7440-47 3 Chromium Yes Yes Yes
7440-48 4 Cobalt Yes Yes
7440-50-8 Copper Yes Yes
7439-92 1 Lead Yes Yes Yes
7439-95 4 Magnesium
7439-96-5 Manganese Yes Yes
7439-97 6 Mercury Yes Yes Yes
7440-02 0 Nickel Yes Yes Yes
7723-14 0 Phosphorus Yes Yes
7782-49 2 Selenium Yes Yes Yes
7440-22 4 Sliver Yes Yes Yes
7440-28-0 Thallium Yes Yes Yes
7440-66 6 Zinc Yes Yes Yes
Perchlorates
14797-73-0 Perchlorate Yes Yes
Semivolatile Organic Compounds
95-94-3 1 2 4 5-Tetrachiorobenzene Yes Yes Yes
120-82-1 1 2 4 Tnchlorobenzene Yes Yes Yes
95-50-1 1 2-Dichiorobenzene Yes Yes Yes
122-66-7 1 2 Diphenylhydrazine Yes Yes Yes
99 35-4 1 3 5-Tnnitrobenzene Yes Yes Yes
541 73-1 1 3 Dichlorobenzene Yes Yes Yes
99 65-0 1 3-Dinitrobenzene Yes Yes Yes
106-46-7 1 4-Dichiorobenzene Yes Yes Yes
90 13-1 1 -Chloronaphthalene Yes Yes
134 32-7 1-Naphthylamine Yes Yes
58 90-2 2 3 4 6-Tetrachlorophenol Yes Yes Yes
95 95-4 2 4 5-Tnchlorophenol Yes Yes Yes
88 06-2 2 4 6-Tnchlorophenoi Yes Yes Yes
120-83-2 2 4-Dichlorophenoi Yes Yes Yes
105-67-9 2 4-Dimethylphenol Yes Yes Yes
51-28-5 2 4 Dinitrophenol Yes Yes Yes
121-14-2 2 4-Dinitrotoluene Yes Yes Yes
87-65 0 2 6-Dichlorophenol Yes Yes
606-20 2 2 6-Dinitrotoluene Yes Yes Yes
53-96-3 2 Acetylaminofluorene Yes Yes
91-58-7 2 Chloronaphthalene Yes Yes Yes
95-57-8 2 Chiorophenol Yes Yes Yes
91-57-6 2-Methylnaphthaiene Yes Yes
95-48-7 2-Methylphenoi Yes Yes Yes
91 59-8 2-Naphthylamine Yes Yes
88-74-4 2-Nitroanilme Yes Yes Yes
88-75-5 2-Nitrophenol Yes Yes Yes
91-94-1 3 3-Dichiorobenzidine Yes Yes Yes
TABLE 23
CHEMICALS OF POTENTIAL CONCERN
EVALUATED IN HUMAN HEALTH RISK ASSESSMENT
THIOKOL PROPULSION, INC
BRIGHMAN CITY, UTAH
PAGE 2 OF 6
Cas No COPC
Listed in USEPA
HHRAP
Database'^'
Toxicity
Information
Available'^'
Quantitatively
Evaluated'^'
119-93-7 3 3-Dimethylbenzidine Yes Yes
56-49 5 3-Methylcholanthrene
3-Methylphenol & 4-Methylphenol
99-09-2 3-Nitroaniline Yes Yes Yes
534-52-1 4 6 Dinitro 2 methylphenol Yes Yes
92 67-1 4 Aminobiphenyl Yes Yes
101-55-3 4-Bromophenyl phenyl ether Yes Yes Yes
59-50-7 4 Chloro 3 methylphenol Yes Yes Yes
106-47 8 4 Chloroaniline Yes Yes Yes
7005 72-3 4-Chlorophenyl phenyl ether Yes Yes Yes
100-01-6 4-Nitroaniline Yes Yes Yes
100-02-7 4-Nitrophenol Yes Yes Yes
57 97-6 7 12 Dimethylbenz(a)anthracene Yes Yes
83-32 9 Acenaphthene Yes Yes Yes
208 96-8 Acenaphthylene Yes Yes
98-86 2 Acetophenone Yes Yes Yes
62 53-3 Aniline Yes Yes Yes
120-12-7 Anthracene Yes Yes Yes
92-87-5 Benzidine Yes Yes
56-55-3 Benzo(a)anthracene Yes Yes Yes
50-32-8 Benzo(a)pyrene Yes Yes Yes
205-99-2 Benzo(b)fluoranthene Yes Yes Yes
191-24 2 Benzo(g h i)perylene Yes Yes
207 08-9 Benzo(k)fluoranthene Yes Yes Yes
65-85 0 Benzoic aad Yes Yes Yes
100-51-6 Benzyl alcohol Yes Yes Yes
111 91-1 bis(2-Chloroethoxy)methane Yes Yes
111-44-4 bis(2 Chloroethyl)ether Yes Yes Yes
39638-32 9 bis(2 Chloroisopropyl)ether Yes Yes Yes
117-81 7 bis(2 Ethylhexyl)phthalate Yes Yes Yes
85-68-7 Butyl benzyl phthalate Yes Yes Yes
86-74-8 Carbazole
218-01-9 Chrysene Yes Yes Yes
CS
53-70 3 Dibenzo(a h)anthracene Yes Yes Yes
132 64-9 Dibenzofuran
84-66 2 Diethyl phthalate Yes Yes Yes
131 11-3 Dimethyl phthalate Yes Yes Yes
84-74-2 Di-n-butyl phthalate Yes Yes Yes
117-84-0 Di-n-octyl phthalate Yes Yes Yes
88-85-7 Dinoseb Yes Yes
122-39-4 Diphenylamine Yes Yes
62-50-0 Ethyl methanesulfonate Yes Yes Yes
206-44-0 Fluoranthene Yes Yes Yes
86 73-7 Fluorene Yes Yes Yes
118-74 1 Hexachlorobenzene Yes Yes Yes
87 68-3 Hexachlorobutadiene Yes Yes Yes
77-47 4 Hexachlorocyclopentadiene Yes Yes Yes
67 72-1 Hexachloroethane Yes Yes Yes
1888-71 7 Hexachloropropene Yes Yes
193 39-5 lndeno(1 2 3 cd)pyrene Yes Yes Yes
TABLE 23
CHEMICALS OF POTENTIAL CONCERN
EVALUATED IN HUMAN HEALTH RISK ASSESSMENT
THIOKOL PROPULSION, INC
BRIGHMAN CITY, UTAH
PAGE 3 OF 6
Cas No COPC
Listed in USEPA
HHRAP
Database'^'
Toxicity
Information
Available'^'
Quantitatively
Evaluated'^'
78-59-1 Isophorone Yes Yes Yes
120-58-1 Isosafrole
66-27-3 Methyl methanesulfonate
91-20-3 Naphthalene Yes Yes Yes
98-95 3 Nitrobenzene Yes Yes Yes
N Nitro-o-toluidine
55-18-5 N Nitrosodiethylamine Yes Yes
62-75-9 N Nitrosodimethylamine Yes Yes
924-16-3 N Nitrosodi n-butylamine Yes Yes Yes
621-64-7 N-Nitrosodi n-propylamine Yes Yes Yes
86-30-6 N-Nitrosodiphenylamine Yes Yes Yes
10595-95-6 N Nitrosomethylethylamine Yes Yes
59-89-2 N Nitrosomorpholine Yes Yes
100-75-4 N-Nitrosopipendine
930-55-2 N-Nitrosopyrrolidine Yes Yes
95-53-4 o-Toiuidine Yes Yes Yes
60-11-7 p-Dimethyiaminoazobenzene Yes Yes
608-93-5 Penta chlorobenzene Yes Yes Yes
76-01-7 Penta chloroethane Yes Yes
82-68-8 Pentachloronitrobenzene Yes Yes Yes
87 86-5 Pentachlorophenol Yes Yes Yes
62 44-2 Phenacetin
85 01-8 Phenanthrene Yes Yes Yes
108 95-2 Phenol Yes Yes Yes
129 00-0 Pyrene Yes Yes Yes
110 86-1 Pyndine Yes Yes Yes
94 59-7 Safroie Yes Yes Yes
Dioxins/Furans
1746-01-6 2 3 7 8 TCDD Yes Yes Yes
40321-76-4 1 2 3 7 8-PeCDD Yes Yes Yes
39227-28-6 1 2 3 4 7 8 HxCDD Yes Yes Yes
57653-85-7 1 2 3 6 7 8-HxCDD Yes Yes Yes
19408-74-3 1 2 3 7 8 9 HxCDD Yes Yes Yes
35822-46-9 1 2 3 4 6 7 8-HpCDD Yes Yes Yes
3268-87 9 1 2 3 4 6 7 8 9-OCDD Yes Yes Yes
51207 31-9 2 3 7 8-TCDF Yes Yes Yes
57117-41-6 1 2 3 7 8-PeCDF Yes Yes Yes
57117-31-4 2 3 4 7 8-PeCDF Yes Yes Yes
70648-26 9 1 2 3 4 7 8-HxCDF Yes Yes Yes
57117-44-9 1 2 3 6 7 8-HxCDF Yes Yes Yes
60851-34-5 2 3 4 6 7 8-HxCDF Yes Yes Yes
72918-21 9 1 2 3 7 8 9 HxCDF Yes Yes Yes
67562-39-4 1 2 3 4 6 7 8 HpCDF Yes Yes Yes
55673-89-7 1 2 3 4 7 8 9-HpCDF Yes Yes Yes
39001-02-0 1 2 3 4 6 7 8 9 OCDF Yes Yes Yes
Carbonyis
5779-94-2 2 5 Dimethylbenzaldehyde Yes Yes
75-07 0 Acetaldehyde Yes Yes Yes
67-64-1 Acetone Yes Yes Yes
100-52-7 Benzaldehyde Yes Yes Yes
4170-30-3 Crotonaldehyde Yes Yes
TABLE 23
CHEMICALS OF POTENTIAL CONCERN
EVALUATED IN HUMAN HEALTH RISK ASSESSMENT
THIOKOL PROPULSION, INC
BRIGHMAN CITY, UTAH
PAGE 4 OF 6
Cas No COPC
Listed in USEPA
HHRAP
Database'^'
Toxicity
Information
Available'^*
Quantitatively
Evaluated'^'
50-00-0 Formaldehyde Yes Yes Yes
66-25-1 Hexanal
590-86-3 Isopentanal
NA m p-Tolualdehyde
NA MEK/Butyraldehydes
529 20-4 o-Tolualdehyde Yes Yes
110-62 3 Pentanal
123-38-6 Propanal Yes Yes
HCI/CI2/NH3
7647-01-0 HCI Yes Yes Yes
7782 50-5 CI2 Yes Yes Yes
7664-41 7 NH3
74 90-8 HCN
Volatile Organic Compounds
NA TNMOC
71-55 6 1 1 1-Tnchloroethane Yes Yes Yes
79-34-5 112 2 Tetrachloroethane Yes Yes Yes
79-00-5 1 1 2-Tnchloroethane Yes Yes Yes
75-34-3 1 1-Dichloroethane Yes Yes Yes
75 35-4 1 1-Dichloroethene Yes Yes Yes
526-73-8 1 2 3-Tnmethylbenzene Yes Yes
120 82-1 1 2 4-Tnchlorobenzene Yes Yes Yes
95-63 6 1 2 4-Tnmethylbenzene Yes Yes
106 93-4 1 2-Dibromoethane Yes Yes Yes
95-50-1 1 2-Dichiorobenzene Yes Yes Yes
107-06-2 1 2-Dichloroethane Yes Yes Yes
78 87-5 1 2-Dichloropropane Yes Yes Yes
108-67-8 1 3 5-Tnmethylbenzene Yes Yes Yes
106 99-0 1 3-Butadiene
541-73 1 1 3 Dichlorobenzene Yes Yes Yes
141 93-5 1 3-Diethylbenzene
106-46-7 1 4 Dichlorobenzene Yes Yes Yes
105-05-5 1 4-Diethylbenzene Yes Yes
123-91-1 1 4 Dioxane Yes Yes Yes
106-98-9 1 Butene
592 41-6 1-Hexene
109-67 1 1 Pentene
540-84-1 2 2 4-Trimethylpentane Yes Yes
75-83-2 2 2-Dimethylbutane Yes Yes
565-75-3 2 3 4-Tnmethylpentane Yes Yes
79-29-8 2 3-Dimethylbutane Yes Yes
565-59-3 2 3-Dimethylpentane Yes Yes
108-08-7 2 4-Dimethylpentane Yes Yes
78-93-3 2-Butanone Yes Yes
611-14-3 2-Ethyltoluene Yes Yes
591-78 6 2 Hexanone Yes Yes
540 84-1 2-Methylheptane Yes Yes
591-74-6 2-Methylhexane Yes Yes
107 83-5 2-Methylpentane Yes Yes
79-46 9 2-Nitropropane
67 63-0 2-Propanol
TABLE 23
CHEMICALS OF POTENTIAL CONCERN
EVALUATED IN HUMAN HEALTH RISK ASSESSMENT
THIOKOL PROPULSION, INC
BRIGHMAN CITY, UTAH
PAGE 5 OF 6
Cas No COPC
Listed in USEPA
HHRAP
Database'^'
Toxicity
Information
Available'^)
Quantitatively
Evaluated'^'
107-05-1 3-Chloropropene
620-14-4 3 Ethyltoluene Yes Yes
589-81-1 3-Methylheptane Yes Yes
96-14-0 3-Methylhexane Yes Yes
96-14 0 3-Methylpentane Yes Yes
622-96-8 4-Ethyltoluene Yes Yes
108-10-1 4-Methyl-2-pentanone Yes Yes Yes
67-64 1 Acetone Yes Yes Yes
75-05 8 Acetonitnle Yes Yes Yes
74-86 2 Acetylene Not Toxic
107-13 1 Acrylonitnle Yes Yes Yes
100-44 7 alpha Chlorotoluene Yes Yes Yes
71-43 2 Benzene Yes Yes Yes
75-27 4 Bromodichloromethane Yes Yes Yes
75-25-2 Bromoform Yes Yes Yes
74-83 9 Bromomethane Yes Yes Yes
106-97 8 Butane Not Toxic
75-15 0 Carbon Disulfide Yes Yes Yes
56-23 5 Carbon Tetrachlonde Yes Yes Yes
107-14 2 Chloroacetonitnle Yes Yes
108-90 7 Chlorobenzene Yes Yes Yes
75-00 3 Chloroethane Yes Yes Yes
67-66 3 Chloroform Yes Yes Yes
74-87 3 Chloromethane Yes Yes Yes
156-59 2 CIS 1 2-Dichloroethene Yes Yes Yes
10061 01-5 CIS 1 3-Dichloropropene Yes Yes
590-18-1 CIS 2-Butene
627-20 3 CIS 2 Pentene Not Toxic
98-82 8 Cumene Yes Yes Yes
110-82-7 Cyclohexane Yes Yes
287-92 3 Cyclopentane Not TOXIC
124-18 5 Decane Not TOXIC
124-48-1 Dibromochloromethane Yes Yes Yes
74-84-0 Ethane Not TOXIC
64-17-5 Ethanol
74-85-1 Ethene Not TOXIC
100-41-4 EthylBenzene Yes Yes Yes
60-29-7 Ethyl Ether
97-63-2 Ethyl Methacrylate Yes Yes Yes
75-69-4 Freon 11 Yes Yes Yes
76 13-1 Freon 113 Yes Yes
76-14-2 Freon 114 Yes Yes
75-71-8 Freon 12 Yes Yes Yes
142-82-5 Heptane Not TOXIC
87-68-3 Hexachlorobutadiene Yes Yes Yes
110-54-3 Hexane Yes Yes
75-28-5 Isobutane Not TOXIC
78-78 4 Isopentane Not TOXIC
78-79 5 Isoprene
NA m p Xylene
126-98 7 Methacryionitnle Yes Yes Yes
TABLE 23
CHEMICALS OF POTENTIAL CONCERN
EVALUATED IN HUMAN HEALTH RISK ASSESSMENT
THIOKOL PROPULSION, INC
BRIGHMAN CITY, UTAH
PAGE 6 OF 6
Cas No COPC
Listed in USEPA
HHRAP
Database'^'
Toxicity
Information
Available'^*
Quantitatively
Evaluated'^'
96-33 3 Methyl Acrylate
80-62-6 Methyl Methacrylate Yes Yes
1634-04-4 Methyl tert butyl ether Yes Yes
108-87-2 Methyl cyclohexane Not Toxic
96 37-7 Mettiylcyclopentane
75-09-2 Methylene Chlonde Yes Yes Yes
109-69-3 n-Butylchlonde
111 84-2 Nonane Not Toxic
111-65 9 Octane Not Toxic
95-47-6 o-Xylene Yes Yes Yes
109 66-0 Pentane Not TOXIC
74-98 6 Propane Not TOXIC
103-65-1 Propylbenzene Yes Yes
115-07-1 Propylene Not TOXIC
100-42-5 Styrene Yes Yes Yes
127 18-4 Tetrachloroethene Yes Yes Yes
109-99-9 Tetrahydrofuran Yes Yes Yes
108-88-3 Toluene Yes Yes Yes
156 60-5 trans-1 2 Dichloroethene Yes Yes Yes
10061-02-6 trans-1 3-Dichloropropene Yes Yes
624-64-6 trans-2-butene
646 04-8 trans 2 Pentene Not TOXIC
79-01 6 Tnchloroethene Yes Yes Yes
1120-21-4 Undecane Yes Yes
75 01-4 Vinyl Chlonde Yes Yes Yes
CEM
124-38-9 C02
630-08-0 CO
7647-01-0 HCI Yes Yes Yes
NA NOX
7446-09-5 S02
Notes
COPC - Chemical of Potential Concern
HHRAP - Human health risk assessment protocol
1 These chemicals were listed in the USEPA (2005) HHRAP Appendix A for consideration as a COPC
2 USEPA's Integrated Risk Information System (IRIS) Health Effects Assessment Summary Tables (USEPA 1997) and
Oak Ridge National Laboratory Regional Screening Level Table (September 2008)
3 - A chemical was quantitatively evaluated in the human health nsk assessment if there was current toxicity cntena available
or if an appropnate surrogate could be identified if there was no current toxicity cntena available
TABLE 24
SUMMARY OF CANCER RISKS AND HAZARD INDICES
THIOKOL PROPULSION
BRIGHAM CITY, UTAH
PAGE 1 OF 2
Exposure Point Receptor Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Average Maximum Average Maximum
Adams Ranch Adult Farmer 6 3E-08 1 IE 07 1 9E 04 2 4E 04 Adams Ranch
Child Farmer 2 IE 08 3 6E 08 4 IE 04 5 OE-04
Adams Ranch
Adult Resident 2 7E 08 4 6E 08 1 IE 04 1 4E-04
Adams Ranch
Child Resident 1 3E 08 2 2E 08 2 6E 04 3 IE 04
Autoliv Adult Farmer 1 3E-07 2 3E 07 4 5E-04 5 7E 04 Autoliv
Child Farmer 4 4E 08 7 5E 08 9 8E 04 1 2E 03
Autoliv
Adult Resident 5 7E 08 9 6E 08 2 7E 04 3 2E 04
Autoliv
Child Resident 2 7E 08 4 6E 08 6 2E 04 7 4E 04
Blue Creek Adult Farmer 9 8E 08 1 7E-07 2 4E 04 31E-04 Blue Creek
Child Farmer 3 4E 08 5 7E 08 5 IE 04 6 3E 04
Blue Creek
Adult Resident 4 6E 08 7 7E 08 1 4E 04 1 8E 04
Blue Creek
Child Resident 2 2E 08 3 7E 08 3 2E 04 3 9E 04
Boundary #1 Adult Farmer 6 5E 08 1 IE 07 2 0E 05 3 7E 05 Boundary #1
Child Farmer 2 3E-08 3 9E-08 2 IE 05 3 9E-05
Boundary #1
Adult Resident 3 2E-08 5 4E-08 1 OE 05 2 OE-05
Boundary #1
Child Resident 1 5E-08 2 6E-08 1 IE 05 2 IE 05
Boundary #2 Adult Farmer 6 6E-08 1 IE 07 2 OE-04 2 6E 04 Boundary #2
Child Farmer 2 2E 08 3 8E 08 4 3E 04 5 3E 04
Boundary #2
Adult Resident 2 9E 08 4 8E 08 1 2E 04 1 5E 04
Boundary #2
Child Resident 1 4E 08 2 3E 08 2 8E 04 3 3E 04
Boundary #3 Adult Farmer 1 8E 07 3 2E-07 1 8E 03 2 2E 03 Boundary #3
Child Farmer 5 4E 08 9 4E 08 4 0E 03 4 8E-03
Boundary #3
Adult Resident 5 7E 08 9 6E 08 1 1E-03 1 3E-03
Boundary #3
Child Resident 2 7E 08 4 5E-08 2 6E-03 3 OE-03
Boundary #4 Adult Farmer 1 OE 07 1 8E 07 1 3E 03 1 6E 03 Boundary #4
Child Farmer 2 9E-08 5 1E-08 3 0E 03 3 6E 03
Boundary #4
Adult Resident 2 6E-08 4 4E-08 8 0E 04 9 3E 04
Boundary #4
Child Resident 1 2E-08 2 IE 08 1 9E 03 2 3E 03
Chnstensen Ranch Adult Farmer 3 8E 08 6 5E 08 1 OE 04 1 3E 04 Chnstensen Ranch
Child Farmer 1 2E 08 2 IE 08 2 2E-04 2 7E-04
Chnstensen Ranch
Adult Resident 1 5E 08 2 6E 08 6 OE-05 7 4E-05
Chnstensen Ranch
Child Resident 7 3E 09 1 2E 08 1 4E 04 1 7E 04
Holmgren Ranch Pond Adult Farmer 9 8E 08 1 7E 07 8 BE 04 8 2E 04 Holmgren Ranch Pond
Child Farmer 3 IE 08 5 4E-08 1 5E 03 1 8E 03
Holmgren Ranch Pond
Adult Resident 3 6E-08 6 1E-08 3 9E 04 4 6E-04
Holmgren Ranch Pond
Child Resident 1 7E-08 2 9E-08 9 4E 04 1 IE 03
Howe Dairy Adult Farmer 4 8E-08 8 2E 08 7 IE 05 9 4E 05 Howe Dairy
Child Farmer 1 6E 08 2 8E 08 1 4E 04 1 8E-04
Howe Dairy
Adult Resident 2 IE 08 3 6E 08 4 1 E-05 5 3E 05
Howe Dairy
Child Resident 1 OE 08 1 7E 08 9 OE-05 1 IE 04
M-136 Offsite Maximum Deposition Adult Farmer 5 9E 09 1 IE 08 2 1E 04 2 6E-04 M-136 Offsite Maximum Deposition
Child Farmer 1 8E 09 3 2E-09 4 6E 04 5 5E 04
M-136 Offsite Maximum Deposition
Adult Resident 1 7E 09 2 9E-09 1 2E 04 1 4E 04
M-136 Offsite Maximum Deposition
Child Resident 8 2E-10 1 4E 09 2 9E 04 3 4E-04
M 136 Offsite Maximum-Gaseous Adult Farmer 9 5E 08 1 6E-07 2 IE 05 4 0E 05 M 136 Offsite Maximum-Gaseous
Child Farmer 3 4E 08 5 6E 08 2 4E-05 4 5E 05
M 136 Offsite Maximum-Gaseous
Adult Resident 4 7E 08 7 8E 08 1 5E 05 3 0E 05
M 136 Offsite Maximum-Gaseous
Child Resident 2 2E 08 3 7E-08 1 5E 05 3 0E 05
M 136 Offsite Maximum Particulate Adult Farmer 9 5E-08 1 6E 07 2 IE 05 4 0E 05 M 136 Offsite Maximum Particulate
Child Farmer 3 4E-08 5 6E-08 2 4E 05 4 5E-05
M 136 Offsite Maximum Particulate
Adult Resident 4 7E-08 7 8E 08 1 5E 05 3 OE-05
M 136 Offsite Maximum Particulate
Child Resident 2 2E 08 3 7E 08 1 5E 05 3 0E 05
M 136 Onsite Maximum-Deposition Adult Farmer 7 5E 09 1 3E 08 2 3E 04 2 9E-04 M 136 Onsite Maximum-Deposition
Child Farmer 2 6E 09 4 6E 09 5 0E 04 6 0E 04
M 136 Onsite Maximum-Deposition
Adult Resident 3 3E 09 5 6E 09 1 3E 04 1 5E 04
M 136 Onsite Maximum-Deposition
Child Resident 1 6E 09 2 7E-09 3 IE 04 3 7E-04
M 136 Onsite Maximum Gaseous Adult Farmer 2 OE-07 3 4E 07 4 4E 05 8 5E 05 M 136 Onsite Maximum Gaseous
Child Farmer 7 1E-08 1 2E 07 5 OE-05 9 5E 05
M 136 Onsite Maximum Gaseous
Adult Resident 9 8E 08 1 7E 07 3 IE 05 6 3E 05
M 136 Onsite Maximum Gaseous
Child Resident 4 7E 08 7 9E 08 3 IE 05 6 4E 05
TABLE 24
SUMMARY OF CANCER RISKS AND HAZARD INDICES
THIOKOL PROPULSION
BRIGHAM CITY, UTAH
PAGE 2 OF 2
Exposure Point Receptor Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Average Maximum Average Maximum
M 136 Onsite Maximum Particulate Adult Farmer 2 0E 07 3 4E 07 4 4E 05 8 5E 05 M 136 Onsite Maximum Particulate
Child Farmer 7 IE 08 1 2E 07 5 OE-05 9 5E 05
M 136 Onsite Maximum Particulate
Adult Resident 9 8E 08 1 7E-07 3 IE 05 6 3E 05
M 136 Onsite Maximum Particulate
Child Resident 4 7E-08 7 9E 08 3 1 E-05 6 4E 05
M 225 Offsite Maximum-Deposition Adult Farmer 2 3E 07 4 4E-07 2 7E-02 3 4E-02 M 225 Offsite Maximum-Deposition
Child Farmer 5 5E-08 1 OE 07 6 2E-02 7 4E-02
M 225 Offsite Maximum-Deposition
Adult Resident 2 IE 08 3 6E 08 1 6E 02 1 9E 02
M 225 Offsite Maximum-Deposition
Child Resident 9 IE 09 1 6E 08 4 0E 02 4 7E-02
M 225 Offsite Maximum Gaseous Adult Farmer 4 9E-07 8 2E-07 1 IE 04 2 1E-04 M 225 Offsite Maximum Gaseous
Child Farmer 1 7E 07 2 9E-07 1 2E 04 2 3E 04
M 225 Offsite Maximum Gaseous
Adult Resident 2 4E 07 4 0E 07 7 5E-05 1 5E-04
M 225 Offsite Maximum Gaseous
Child Resident 1 IE 07 1 9E 07 7 6E 05 1 5E 04
M 225 Offsite Maximum Particulate Adult Farmer 3 2E 08 5 3E 08 2 7E 02 3 3E 02 M 225 Offsite Maximum Particulate
Child Farmer 9 5E-09 1 6E 08 6 2E 02 7 4E 02
M 225 Offsite Maximum Particulate
Adult Resident 8 4E 09 1 4E-08 1 6E 02 1 9E-02
M 225 Offsite Maximum Particulate
Child Resident 4 IE 09 6 8E 09 4 OE-02 4 6E 02
M 225 Onsite Maximum Deposition Adult Farmer 2 5E 07 4 5E 07 1 2E-02 1 5E-02 M 225 Onsite Maximum Deposition
Child Farmer 7 2E 08 1 3E 07 2 7E-02 3 2E-02
M 225 Onsite Maximum Deposition
Adult Resident 6 6E-08 1 IE 07 7 0E 03 8 2E 03
M 225 Onsite Maximum Deposition
Child Resident 3 IE 08 5 3E-08 1 7E-02 2 OE-02
M 225 Onsite Maximum Gaseous Adult Farmer 3 7E-06 6 2E-06 8 IE 04 1 6E-03 M 225 Onsite Maximum Gaseous
Child Farmer 1 3E 06 2 2E-06 9 3E 04 1 8E-03
M 225 Onsite Maximum Gaseous
Adult Resident 1 8E 06 3 0E 06 5 7E-04 1 2E 03
M 225 Onsite Maximum Gaseous
Child Resident 8 6E-07 1 5E 06 5 8E 04 1 2E 03
M 225 Onsite Maximum-Particulate Adult Farmer 2 2E 09 3 6E 09 4 7E 07 9 0E 07 M 225 Onsite Maximum-Particulate
Child Farmer 7 6E-10 1 3E 09 5 4E 07 1 OE 06
M 225 Onsite Maximum-Particulate
Adult Resident 1 IE 09 1 8E-09 3 3E 07 6 7E 07
M 225 Onsite Maximum-Particulate
Child Resident 5 0E 10 8 4E 10 3 4E-07 6 8E 07
Thiokol Ranch Pond Adult Farmer 1 4E-08 2 4E 08 3 6E-05 4 7E-05 Thiokol Ranch Pond
Child Farmer 4 6E 09 7 9E-09 7 8E-05 9 6E-05
Thiokol Ranch Pond
Adult Resident 6 OE-09 1 OE 08 2 2E 05 2 7E 05
Thiokol Ranch Pond
Child Resident 2 9E 09 4 8E-09 5 0E 05 6 OE-05
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 1 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
Adams Ranch Adult Farmer 136 A 2 9E-09 5 0E-09 7 4E 06 9 6E06
136B 5 3E 10 9 9E 10 1 4E07 1 9E-07
136C 5 2E 11 8 9E 11 6 7E 08 9 IE-OB
136D 1 IE 12 1 9E 12 2 4E 09 3 IE 09
225A 5 1E-08 8 8E-0B 1 7E 04 2 2E 04
225B 8 2E-09 1 4E-08 9 6E06 1 3E 05
Total 6 3E 08 1 IE 07 1 9E04 2 4E04
Child Farmer 136A 9 9E 10 1 7E-09 1 6E05 1 9E 05
136B 1 2E 10 2 2E 10 3 0E 07 3 9E 07
136C 1 8E 11 3 IE 11 1 3E07 1 7E 07
136D 3 BE 13 6 4E 13 5 0E09 6 2E 09
225A 1 7E 08 2 9E-08 3 7E 04 4 5E04
225B 2 9E 09 4 8E-09 1 9E05 2 4E 05
Total 2 IE 08 3 6E 08 4 IE 04 5 0E04
Adult Resident 136A 1 3E 09 2 2E 09 4 4E 06 5 4E06
136B 3 6E 11 63E 11 6 9E08 8 5E 08
136C 2 5E 11 4 2E 11 3 8E08 5 1E08
136D 50E 13 8 5E 13 1 4E 09 1 7E09
225A 2 2E 08 3 7E-08 1 0E04 1 2E04
225B 3 9E 09 6 6E-09 5 5E 06 7 5E 06
Total 2 7E 08 4 6E 08 1 IE 04 1 4E 04
Child Resident 136A 6 3E 10 1 1E-09 1 0E05 1 2E05
136B 1 5E 11 2 7E 11 1 7E 07 2 0E 07
136C 1 2E 11 2 0E 11 8 3E 08 1 OE 07
136D 2 4E 13 4 0E 13 3 2E 09 3 8E 09
225A 1 OE 08 1 8E-08 2 4E 04 2 BE 04
225B 19E 09 3 1E-09 1 2E 05 1 5E05
Total 1 3E 08 2 2E 08 2 6E 04 3 IE 04
Autoliv Adult Farmer 136A 2 4E 09 4 0E-09 5 9E 06 7 6E 06
136B 1 3E 11 2 3E 11 1 3E 08 1 7E 08
136C 5 0E 11 8 4E 11 5 2E 08 7 3E 08
136D 2 3E 12 3 8E12 9 0E-09 1 4E08
225A 1 IE 07 1 9E-07 4 2E-04 5 3E 04
225B 1 BE 08 3 OE-08 2 3E-05 3 1E05
Total 1 3E 07 2 3E 07 4 5E-04 5 7E 04
Child Farmer 136A e2E 10 1 4E-09 1 3E-05 1 5E 05
136B 3 9E 12 6 8E 12 2 5E-0e 3 2E08
136C 1 7E 11 2 9E 11 1 OE-07 1 3E-07
136D 9 7E 13 1 6E 12 9 0E-09 1 3E-08
225A 3 7E08 6 3E 08 9 2E 04 1 1E-03
225B 6 2E-09 1 OE 08 4 6E 05 5 8E-05
Total 4 4E-08 7 5E 08 9 8E04 1 2E-03
Adult Resident 136A 1 1E-09 1 BE 09 3 5E 06 4 3E-06
136B 4 3E 12 7 3E 12 7 2E 09 9 6E-09
136C 2 4E 11 4 0E 11 3 0E 08 4 1E 08
136D 1 6E 12 2 6E 12 1 IE 09 1 4E 09
225A 4 7E-08 BOE 08 2 5E04 3 0E04
225B 8 5E-09 1 4E 08 1 3E 05 1 8E 05
Total 5 7E-08 9 6E08 2 7E 04 3 2E 04
Child Resident 136A 5 2E 10 BBE 10 8 0E 06 9 6E 06
136B 2 0E 12 3 4E 12 1 6E08 2 0E 08
136C 1 IE 11 1 9E 11 6 2E 08 7 9E08
136D 7 5E 13 1 3E 12 2 5E 09 3 0E 09
225A 2 2E 08 3 8E 08 5 9E 04 6 9E 04
225B 4 0E 09 6 8E-09 2 9E-05 3 6E 05
Total 2 7E 08 4 6E 08 6 2E-04 7 4E04
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 2 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
Blue Creek Adult Farmer 136A 5 3E 08 9 OE-08 1 OE 04 1 4E-04
136B 2 9E 10 5 2E 10 51E-06 6 3E-06
136C 6 6E 10 1 IE 09 1 3E 06 1 7E 06
136D 1 5E 11 2 6E 11 1 IE 07 1 3E 07
225A 3 8E08 6 4E-08 1 2E 04 1 6E-04
225B 6 6E 09 1 IE 08 7 9E-06 1 1E-05
Total 9 BE 08 1 7E 07 2 4E 04 31E-04
Child Farmer 136A 1 BE 08 3 IE 08 2 2E 04 2 7E 04
136B 7 BE 11 1 4E 10 1 2E05 1 4E 05
136C 2 3E 10 3 9E 10 2 6E 06 3 3E06
136D 4 9E 12 8 4E 12 2 4E-07 2 9E-07
225A 1 3E 08 2 2E 08 2 6E 04 3 2E04
225B 2 3E 09 3 9E09 1 6E 05 2 0E 05
Total 3 4E-0B 5 7E 08 5 IE 04 6 3E 04
Adult Resident 136A 2 5E 08 4 IE-OB 6 1E-05 7 7E-05
136B 6 3E 11 1 IE 10 3 1E-06 3 6E-06
136C 3 3E 10 5 5E 10 7 5E 07 9 6E 07
136D 5 9E 12 1 OE 11 6 3E08 7 5E 08
225A 1 7E-0B 2 9E-08 7 2E 05 BBE 05
225B 3 2E09 5 3E09 4 5E-06 61E-06
Total 4 6E 08 7 7E 08 1 4E04 1 BE 04
Child Resident 136A 1 2E 08 2 0E 08 1 4E 04 1 7E 04
136B 2 9E 11 5 0E 11 7 4E 06 8 7E 06
136C 1 6E 10 2 6E 10 1 7E 06 2 OE-06
136D 2 8E 12 4 8E 12 1 5E-07 1 8E-07
225A 8 3E 09 1 4E 08 1 7E 04 2 0E 04
225B 1 5E 09 2 5E 09 9 7E 06 1 2E 05
Total 2 2E-08 3 7E 08 3 2E04 3 9E04
Boundary #1 Adult Farmer 136A 1 6E08 2 7E-08 4 9E06 B9E-06
136B 1 IE 10 1 BE 10 3 2E-08 5 9E 08
136C 6 6E 10 1 IE 09 2 0E 07 3 7E 07
136D 1 3E 11 2 2E 11 4 IE 09 7 4E 09
225A 4 1E-08 6 9E-0B 1 3E 05 2 4E-05
225B 7 4E-09 1 3E-08 2 3E-06 4 2E-06
Total 6 5E 08 1 IE 07 2 OE-05 3 7E 05
Child Farmer 136A 5 6E 09 9 5E 09 5 IE 06 9 3E 06
136B 3 7E 11 6 3E 11 3 4E 08 6 IE 08
136C 2 3E 10 3 9E 10 2 IE 07 3 9E-07
136D 4 7E 12 7 BE 12 4 2E-09 7 7E-09
225A 1 4E 08 2 4E 08 1 4E 05 2 5E 05
225B 2 6E 09 4 4E 09 2 4E 06 4 4E 06
Total 2 3E 08 3 9E08 2 IE 05 3 9E 05
Adult Resident 136A 7 9E 09 1 3E0e 2 5E 06 5 OE-06
136B 5 2E 11 8 7E 11 1 6E-08 3 3E-08
136C 3 2E 10 5 5E 10 1 OE 07 2 0E 07
136D 6 5E 12 1 IE 11 2 0E 09 4 IE 09
225A 2 0E 08 3 4E 08 6 3E06 1 3E 05
225B 3 7E 09 6 2E-09 1 2E 06 2 3E-06
Total 3 2E-0B 5 4E 08 1 OE-05 2 OE-05
Child Resident 136A 3 8E-09 6 3E 09 2 6E-06 5 2E 06
136B 2 5E 11 4 2E 11 1 7E 08 3 4E 08
136C 1 6E 10 2 6E 10 1 IE 07 2 IE 07
136D 3 IE 12 5 2E 12 2 1E-09 4 2E-09
225A 9 6E-09 1 6E-08 6 8E-06 1 3E05
225B 1 8E09 3 0E 09 1 2E-06 2 4E 06
Total 1 5E 08 2 6E0B 1 IE 05 2 IE 05
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 3 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
Boundary #2 Adult Farmer 136A 2 4E 09 4 IE 09 5 9E06 7 6E 06
136B 1 IE 11 2 0E 11 1 OE-07 1 3E 07
136C 4 3E 11 7 3E 11 5 0E 08 6 9E 08
136D 9 4E 13 1 6E 12 1 BE 09 2 4E 09
225A 5 5E 08 9 4E-08 1 BE 04 2 3E-04
225B B9E-09 1 5E-0B 1 OE 05 1 4E 05
Total 6 6E0B 1 1E07 2 0E04 2 6E 04
Child Farmer 136A 8 1E 10 1 4E 09 1 3E 05 1 6E 05
136B 3 5E 12 6 0E 12 2 4E-07 2 8E 07
136C 1 5E 11 2 5E 11 9 7E 08 1 2E-07
136D 3 3E 13 5 5E 13 3 BE 09 4 7E-09
225A 1 BE 08 3 1E-08 4 0E 04 4 9E-04
225B 3 1E-09 5 2E-09 2 0E05 2 6E 05
Total 2 2E-0B 3 BE 08 4 3E04 5 3E 04
Adult Resident 136A 1 IE 09 1 BE 09 3 6E 06 4 5E 06
136B 3 8E 12 6 5E12 6 3E 08 7 4E08
136C 2 IE 11 3 5E11 2 9E-08 3 9E 08
136D 4 4E 13 7 4E 13 1 IE 09 1 3E-09
225A 2 3E 08 3 9E08 1 IE 04 1 3E-04
225B 4 2E 09 7 IE 09 6 0E 06 8 IE 06
Total 2 9E-08 4 8E 08 1 2E04 1 5E 04
Child Resident 136A 51E 10 8 5E 10 8 3E-06 9 9E 06
136B 1 BE 12 3 IE 12 1 5E-07 1 BE 07
136C 9 9E 12 1 7E 11 6 0E0B 7 6E-08
136D 2 IE 13 3 5E 13 2 4E 09 2 9E-09
225A 1 IE 08 1 9E08 2 5E 04 3 0E 04
225B 2 0E-09 3 4E-09 1 3E05 1 6E 05
Total 1 4E-08 2 3E 08 2 8E-04 3 3E 04
Boundary #3 Adult Farmer 136A 1 4E 09 2 4E 09 2 7E-06 3 5E-06
136B BOE 12 1 4E 11 5 3E 08 6 6E-0e
136C 3 4E 11 5 7E 11 2 9E 08 4 IE 08
136D 7 2E 13 1 2E 12 BBE 10 1 2E09
225A 1 5E-07 2 8E-07 1 7E 03 2 IE 03
225B 2 4E-0B 4 OE-08 9 8E 05 1 2E 04
Total 1 8E-07 3 2E 07 1 8E-03 2 2E-03
Child Farmer 136A 49E 10 8 3E 10 5 5E 06 6 9E-06
136B 2 5E 12 4 4E 12 1 2E 07 1 4E 07
136C 1 2E 11 2 0E 11 5 2E 08 6 9E 08
136D 2 5E 13 42E 13 1 7E 09 2 2E 09
225A 4 6E-08 BOE-OB 3 8E 03 4 5E 03
225B 7BE-09 1 3E08 2 2E-04 2 6E-04
Total 5 4E 08 9 4E 08 4 0E 03 4 8E03
Adult Resident 136A 6 6E 10 1 IE 09 1 6E06 2 0E 06
136B 3 0E 12 50E 12 3 2E08 3 BE 08
136C 1 6E 11 2 7E 11 1 6E-08 2 3E 08
136D 3 4E 13 5 7E 13 5 0E 10 BBE 10
225A 4 6E-08 7 BE 08 1 OE 03 1 2E-03
225B 1 0E08 1 7E 08 5 BE 05 7 0E 05
Total 5 7E 08 9 6E08 1 IE 03 1 3E 03
Child Resident 136A 3 IE 10 5 3E 10 3 5E-06 4 3E 06
136B 1 4E 12 2 4E 12 7 6E-08 8 9E-0B
136C 78E 12 1 3E 11 3 2E 08 4 2E08
136D 1 6E 13 2 7E13 1 IE 09 1 4E 09
225A 2 2E 08 3 7E 08 2 4E 03 2 BE 03
225B 4 BE 09 8 OE-09 1 4E 04 1 6E 04
Total 2 7E-0B 4 5E 08 2 6E-03 3 0E-03
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 4 OF 12
Exposure Point Receptor Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source'' Average Maximum Average Maximum
Boundary #4 Adult Farmer 136A 1 7E-09 2 9E 09 2 7E06 3 5E 06 Boundary #4
136B 8 3E 12 1 4E 11 5 3E 08 6 6E 08
136C 3 4E 11 5 7E 11 3 IE 08 4 4E-08
136D 6 7E 13 1 IE 12 1 0E09 1 4E-09
225A 8 9E 08 1 6E-07 1 3E-03 1 5E 03
225B 1 2E-08 2 IE 08 7 3E-05 9 IE 05
Total 1 OE-07 1 8E07 1 3E 03 1 6E 03
Child Famner 136A 5 4E 10 9 3E 10 5 8E 06 7 2E06
136B 2 6E 12 4 5E 12 1 2E07 1 4E-07
136C 1 2E 11 2 0E 11 5 7E-0B 7 5E 08
136D 2 3E 13 4 0E 13 2 1E-09 2 6E 09
225A 2 4E-08 4 4E 08 2 8E 03 3 4E 03
225B 3 BE 09 6 6E09 1 6E 04 2 OE-04
Total 2 9E 08 5 IE 08 3 0E03 3 6E-03
Adult Resident 136A 6 5E 10 1 1E-09 1 7E-06 2 IE 06
136B 3 0E 12 5 0E 12 3 2E0B 3 BE 08
136C 1 6E 11 2 7E 11 1 7E 08 2 5E08
136D 3 2E 13 5 3E 13 5 9E 10 7 7E 10
225A 2 IE 08 3 5E 08 7 5E 04 8 8E-04
225B 4 6E 09 7 7E-09 4 3E-05 5 2E 05
Total 2 6E 08 4 4E 08 8 OE-04 9 3E 04
ChiW Resident 136A 3 IE 10 5 2E10 3 7E 06 4 5E-06
136B 1 4E 12 2 4E 12 7 6E 08 8 9E-0B
136C 78E 12 1 3E 11 3 5E 08 4 5E-0B
136D 1 5E 13 2 5E 13 1 3E-09 1 6E09
225A 9 7E 09 1 6E08 1 BE 03 2 IE 03
225B 2 2E 09 3 7E 09 1 OE 04 1 2E 04
Total 1 2E-08 2 IE 08 1 9E 03 2 3E-03
Chnstensen Ranch Adult Farmer 136A B4E09 1 5E 08 1 IE 05 1 5E-05
136B 23E 11 4 0E 11 1 6E-07 2 0E 07
136C 1 IE 10 1 8E 10 8 3E-0B 1 2E 07
136D 2 0E 12 3 4E 12 3 IE 09 4 IE 09
225A 2 5E 08 4 3E 08 BBE 05 1 1E-04
225B 41E-09 7 0E09 4 9E 06 6 7E-06
Total 3 8E-08 6 5E 08 1 OE-04 1 3E-04
Child Famner 136A 2 5E 09 4 4E-09 2 3E-05 2 9E 05
136B 7 2E 12 1 2E 11 3 5E 07 4 3E 07
136C 37E 11 63E 11 1 5E 07 2 0E 07
136D 6 9E 13 1 2E 12 6 3E 09 7 9E-09
225A B4E-09 1 4E 08 1 9E04 2 3E-04
225B 1 4E-09 2 4E09 9 5E 06 1 2E 05
Total 1 2E08 2 IE 08 2 2E-04 2 7E 04
Adult Resident 136A 2 6E 09 4 5E-09 6 4E 06 8 IE 06
136B 8 IE 12 1 4E 11 9 5E 08 1 IE 07
136C 51E 11 BBE 11 4 7E 08 6 8E-08
136D 9 3E 13 1 6E 12 1 BE 09 2 3E-09
225A 1 1E-08 1 BE 08 5 IE 05 6 2E 05
225B 2 0E09 3 3E-09 2 8E-06 3 BE 06
Total 1 5E08 2 6E 08 6 OE-05 7 4E 05
Child Resident 136A 1 2E 09 2 IE 09 1 4E 05 1 8E-05
136B 3 9E 12 6 5E 12 2 3E 07 2 7E-07
136C 2 4E 11 41E 11 9 IE 08 1 2E-07
136D 4 4E 13 7 5E 13 4 0E09 4 9E 09
225A 51E-09 8 6E-09 1 2E-04 1 4E 04
225B 9 3E 10 1 6E-09 5 9E 06 7 5E06
Total 7 3E 09 1 2E 08 1 4E 04 1 7E-04
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 7 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
M 136 Offsite Maximum Particulate Adult Farmer 136A 5 5E-08 9 3E-08 1 2E 05 2 3E 05
136B 4 3E 10 7 2E10 9 4E 08 1 BE 07
136C 1 5E 09 2 5E 09 3 3E07 6 3E-07
136D 4 3E 11 7 2E 11 9 4E 09 1 8E-0B
225A 3 2E 08 5 4E 08 7 OE-06 1 4E 05
225B BOE 09 1 OEOB 1 3E06 2 5E 06
Total 9 5E 08 1 6E 07 2 IE 05 4 0E 05
Child Farmer 136A 1 9E-0B 3 3E 08 1 4E 05 2 6E-05
136B 1 5E 10 2 5E10 1 1E-07 2 OE-07
136C 5 3E 10 8 9E 10 BBE 07 7 IE 07
136D 1 5E 11 2 5E 11 1 1E-08 2 0E 08
225A 1 IE 08 1 9E 08 8 IE 06 1 5E 05
225B 2 1E-09 3 6E-09 1 5E 06 2 9E-06
Total 3 4E-08 5 6E 08 2 4E 05 4 5E-05
Adult Resident 136A 2 7E 08 4 5E 08 8 4E 06 1 7E05
136B 2 IE 10 3 5E 10 6 6E 08 1 3E 07
136C 7 4E 10 1 2E09 2 3E-07 4 7E 07
136D 2 IE 11 3 5E 11 6 6E09 1 3E 08
225A 1 BE 08 2 7E 08 4 9E 06 1 OE-05
225B 2 9E-09 5 OE-09 9 2E07 1 9E-06
Total 4 7E0B 7 BE 08 1 5E 05 3 0E 05
Child Resident 136A 1 3E 08 2 2E08 BBE-OB 1 7E 05
136B 1 OE 10 1 7E 10 6 7E-08 1 4E 07
136C 3 5E 10 5 9E 10 2 4E 07 4BE-07
136D 1 OE 11 1 7E 11 6 7E 09 1 4E 08
225A 7 5E 09 1 3E 08 5 0E 06 1 OE 05
225B 1 4E 09 2 4E 09 9 4E-07 1 9E 06
Total 2 2E 08 3 7E08 1 5E 05 3 OE-05
M 136 Onsite Maximum Deposition Adult Farmer 136A 6 IE 09 1 1E-08 3 0E 05 4 3E-05
136B 3 3E 10 6 2E 10 3 2E06 3 9E 06
136C 8 7E11 1 5E10 5 4E06 6 7E06
136D 6 3E 11 1 2E 10 6 3E-07 7 7E 07
225A 7 5E 10 1 3E09 1 3E 04 1 6E-04
225B 1 8E 10 3 0E 10 6 3E05 7 7E 05
Total 7 5E 09 1 3E 08 2 3E 04 2 9E 04
Child Famner 136A 2 1E-09 3 7E 09 4 5E 05 5 9E 05
1368 75E 11 1 4E 10 7 2E-06 8 6E 06
136C 2 9E 11 5 0E 11 1 2E05 1 4E-05
136D 1 4E 11 2 7E 11 1 4E 06 1 7E 06
225A 3 3E 10 5 6E 10 2 9E04 3 5E 04
225B 74E 11 1 2E 10 1 4E-04 1 7E 04
Total 2 6E 09 4 6E09 5 0E 04 6 OE-04
Adult Resident 136A 2 BE 09 4 3E 09 9 4E 06 1 IE 05
136B 2 4E 11 4 3E 11 1 9E06 2 2E 06
136C 38E 11 6 4E 11 3 2E 06 3 BE 06
136D 46E 12 BOE 12 3 7E-07 4 3E-07
225A 5 4E 10 9 IE 10 7 7E 05 9 0E05
225B 1 IE 10 1 BE 10 3 7E 05 4 4E 05
Total 3 3E09 5 6E 09 1 3E 04 1 5E 04
Child Resident 136A 1 2E09 2 IE 09 2 2E-05 2 6E-05
136B 1 OE 11 1 BE 11 4 6E 06 5 3E06
136C 1 7E 11 2 9E 11 7 5E 06 BBE 06
136D 1 9E 12 3 5E 12 9 OE-07 1 1E06
225A 2 6E 10 4 4E 10 1 9E-04 2 2E-04
225B 5 3E 11 8 9E 11 9 IE 05 1 IE 04
Total 1 6E 09 2 7E 09 3 1E04 3 7E 04
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 8 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
M 136 Onsite Maximum Gaseous Adult Farmer 136A 1 5E-07 2 6E07 3 4E-05 6 5E-05
136B 4 3E 10 7 2E 10 9 4E 08 1 8E 07
136C 2 2E 09 3 6E 09 4 7E-07 9 0E 07
13BD 5 6E 14 9 4E 14 1 2E 11 24E 11
225A 3 7E 08 6 3E 08 8 IE 06 1 6E 05
225B 6 9E-09 1 2E 08 1 5E-06 2 9E-06
Total 2 0E 07 3 4E 07 4 4E 05 8 5E 05
Child Famner 136A 5 4E 08 9 2E 08 3 9E 05 7 3E 05
136B 1 5E 10 2 5E 10 1 IE 07 2 0E07
136C 7 6E 10 1 3E 09 5 4E 07 1 OE 06
136D 2 0E 14 3 3E 14 1 4E 11 2 7E 11
225A 1 3E 08 2 2E-0B 9 3E 06 1 BE 05
225B 2 4E 09 4 IE 09 1 7E-06 3 3E06
Total 7 1E08 1 2E 07 5 0E 05 9 5E 05
Adult Resident 136A 7 6E 08 1 3E 07 2 4E 05 4 8E 05
136B 2 IE 10 3 5E 10 6 6E-08 1 3E-07
136C 1 1E09 1 8E-09 3 3E 07 6 7E 07
136D 2 7E 14 46E 14 8 6E 12 1 7E 11
225A 1 8E-08 3 IE 08 5 7E 06 1 2E05
225B 3 4E 09 5 7E09 1 IE 06 2 1E06
Total 9BE-08 1 7E 07 3 1E-05 6 3E-05
Child Resident 136A 3 6E08 6 IE-OB 2 4E 05 4 9E 05
136B 1 OE 10 1 7E 10 6 7E-0B 1 4E 07
136C 5 0E 10 8 4E 10 3 4E 07 6 8E-07
136D 1 3E 14 2 2E 14 8 7E 12 1 BE 11
225A B7E 09 1 5E 08 5 8E-06 1 2E-05
225B 1 6E-09 2 7E-09 1 IE 06 2 2E 06
Total 4 7E 08 7 9E0B 3 IE 05 6 4E-05
M 136 Onsite Maximum Particulate Adult Farmer 136 A 1 5E-07 2 6E07 3 4E05 6 5E-05
136B 4 3E 10 7 2E 10 9 4E 08 1 BE 07
136C 2 2E 09 3 6E 09 4 7E-07 9 OE-07
136D 0 OE+00 0 OE+00 6 3E 17 1 IE 16
225A 3 7E-08 6 3E-08 8 IE 06 1 6E-05
225B 6 9E 09 1 2E 08 1 5E06 2 9E06
Total 2 OE-07 3 4E 07 4 4E 05 8 5E 05
Child Farmer 136A 5 4E 08 9 2E 08 3 9E-05 7 3E-05
136B 1 5E 10 2 5E 10 1 IE 07 2 0E 07
136C 7 6E 10 1 3E-09 5 4E 07 1 OE 06
136D 0 OE+00 0 OE+00 6 3E 17 1 IE 16
225A 1 3E-0B 2 2E08 9 3E 06 1 BE 05
225B 2 4E 09 4 1E09 1 7E 06 3 3E06
Total 7 IE 08 1 2E 07 5 0E 05 9 5E 05
Adult Resident 136A 7 6E-0B 1 3E-07 2 4E 05 4 BE 05
136B 2 IE 10 3 5E 10 6 6E-08 1 3E-07
136C 1 IE 09 1 8E09 3 3E 07 6 7E 07
136D 0 OE+00 0 OE+00 6 3E 17 1 IE 16
225A 1 BE 08 3 IE 08 5 7E-06 1 2E-05
225B 3 4E-09 5 7E 09 1 IE 06 2 IE 06
Total 9 8E-08 1 7E 07 3 IE 05 6 3E-05
Child Resident 136A 3 6E 08 6 IE 08 2 4E-05 4 9E 05
136B 1 OE 10 1 7E 10 6 7E 08 1 4E 07
136C 5 0E 10 8 4E 10 3 4E-07 6BE-07
136D 0 OE+00 0 OE+00 6 3E 17 1 1E 16
225A B7E-09 1 5E-0B 5 BE 06 1 2E 05
225B 1 6E 09 2 7E 09 1 1E-06 2 2E-06
Total 4 7E 08 7 9E08 3 IE 05 6 4E 05
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 9 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
M 225 Offsite Maximum Deposition Adult Farmer 136A 2 5E 11 4 2E 11 5 4E07 7 2E-07
136B 1 2E 13 2 0E 13 1 5E 08 1 OEOB
136C 6 6E 13 1 IE 12 5 4E 08 6 BE 08
136D 1 4E 14 2 4E 14 2 3E 09 2 9E09
225A 2 IE 07 3 9E-07 4 BE 03 5 9E-03
225B 2 9E 08 5 0E-0B 2 3E-02 2 8E-02
Total 2 3E07 4 4E 07 2 7E-02 3 4E-02
Child Farmer 136A 1 2E 11 2 0E 11 1 OE-06 1 3E-06
136B 5 5E 14 9 2E 14 3 4E-08 4 IE-OB
136C 3 IE 13 5 2E 13 1 2E-07 1 4E-07
136D 6 3E 15 1 IE 14 5 2E-09 6 2E-09
225A 4 8E-08 B9E 08 1 IE 02 1 3E-02
225B 6 8E-09 1 2E-0B 5 1E02 6 IE 02
Total 5 5E-08 1 OE 07 6 2E 02 7 4E-02
Adult Resident 136A 20E 11 3 4E 11 2 5E-07 3 OE-07
136B 91E 14 1 5E 13 B9E-09 1 OE-OB
136C 5 2E 13 B7E 13 3 IE 08 3 6E-0B
136D 1 OE 14 1 7E 14 1 4E09 1 6E-09
225A 1 8E-08 3 2E 08 2 9E-03 3 3E-03
225B 2 4E-09 3 9E 09 1 4E 02 1 6E-02
Total 2 IE-OB 3 6E 08 1 6E-02 1 9E-02
Child Resident 13BA 9 9E 12 1 7E 11 B 1E-07 7 2E-07
13BB 4 4E 14 7 4E 14 2 2E-0B 2 5E-0B
136C 2 5E 13 4 2E 13 7 5E-0B 8 7E-0B
136D 4 9E 15 B3E 15 3 3E-09 3 8E-09
225A 8 OE-09 1 4E-08 7 0E-03 81E-03
225B 1 1E-09 1 8E-09 3 3E-02 3 8E-02
Total 91E-09 1 6E 08 4 OE-02 4 7E-02
M 225 Offsite Maximum Gaseous Adult Fanner 136A 1 3E-09 2 2E-09 2 8E-07 5 4E 07
136B 58E 12 9 BE 12 1 3E-09 2 4E 09
136C 3 4E 14 5 BE 14 7 5E 12 1 4E 11
136D 71E 13 1 2E 12 1 5E 10 3 0E 10
225A 4 2E-07 7 1E-07 9 2E-05 1 8E 04
225B 6 5E-08 1 1E-07 1 4E 05 2 7E05
Total 4 9E-07 B2E 07 1 IE 04 2 IE 04
Child Famner 136A 4 5E 10 7 6E 10 3 2E 07 6 IE 07
136B 2 0E 12 3 4E 12 1 5E 09 2 BE 09
13BC 1 2E 14 2 0E 14 BBE 12 1 6E 11
13BD 2 5E 13 4 2E 13 1 BE 10 3 4E 10
225A 1 5E-07 2 5E-07 1 1E-04 2 0E 04
225B 2 3E-0B 3 9E-0B 1 6E 05 3 IE 05
Total 1 7E-07 2 9E 07 1 2E 04 2 3E 04
Adult Resident 136A 6 3E 10 1 IE 09 2 0E 07 4 0E 07
136B 2 BE 12 4 BE 12 8 9E 10 1 BE 09
136C 1 7E 14 2 BE 14 5 3E 12 1 IE 11
136D 3 5E 13 58E 13 1 IE 10 2 2E 10
225A 2 IE 07 3 5E 07 6 5E 05 1 3E-04
225B 3 2E 08 5 4E 08 1 0E05 2 OE-05
Total 2 4E 07 4 0E07 7 5E 05 1 5E-04
Child Resident 136A 3 0E 10 51E10 2 0E 07 41E-07
136B 1 4E 12 2 3E 12 9 IE 10 1 8E-09
136C 8 0E 15 1 4E 14 5 4E 12 1 IE 11
136D 1 7E 13 2 BE 13 1 IE 10 2 2E 10
225A 9 BE 08 1 7E 07 6 6E 05 1 3E-04
225B 1 5E 08 2 6E 08 1 0E05 2 IE 05
Total 1 IE 07 1 9E 07 7 6E-05 1 5E 04
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 10 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
M 225 Offsite Maximum Particulate Adult Farmer 136A 2 5E 11 4 2E 11 5 4E-07 7 2E-07
136B 1 2E 13 2 0E 13 1 5E08 1 9E 08
136C 6 6E 13 1 IE 12 5 4E 08 6 8E-08
136D 1 4E 14 2 4E 14 2 3E09 2 9E 09
225A 1 2E 08 2 0E 08 4 BE 03 5 9E-03
225B 2 OE-08 3 4E-08 2 3E-02 2 BE 02
Total 3 2E 08 5 3E 08 2 7E 02 3 3E 02
Child Farmer 136A 1 2E 11 2 0E 11 1 OE 06 1 3E-06
136B 5 5E 14 9 2E 14 3 4E 08 4 IE 08
136C 3 IE 13 5 2E 13 1 2E 07 1 4E-07
136D 6 3E 15 1 IE 14 5 2E-09 6 2E09
225A 4 BE 09 7 7E 09 1 IE 02 1 3E02
2258 4 9E-09 8 1E-09 51E-02 6 IE 02
Total 9 5E 09 1 6E0B 6 2E 02 7 4E 02
Adult Resident 136A 2 0E 11 3 4E 11 2 5E 07 3 OE-07
136B 91E 14 1 5E 13 8 9E-09 1 OE 08
136C 5 2E 13 8 7E 13 3 IE 08 3 6E-0B
136D 1 OE 14 1 7E 14 1 4E09 1 6E 09
225A 6 5E 09 1 IE 08 2 9E 03 3 3E 03
2258 1 9E 09 3 OE-09 1 4E-02 1 6E02
Total 8 4E 09 1 4E 08 1 6E 02 1 9E 02
Child Resident 136A 9 9E 12 1 7E 11 6 IE 07 7 2E 07
136B 4 4E 14 7 4E 14 2 2E-08 2 5E 08
136C 2 5E 13 42E 13 7 5E 08 B7E0B
136D 4 9E 15 8 3E 15 3 3E-09 3 8E 09
225A 3 2E09 5 3E 09 7 0E 03 B 1E-03
225B 9 2E 10 1 5E09 3 3E02 3 8E-02
Total 4 1E-09 6 BE 09 4 0E 02 4 6E 02
M 225 Onsite Maximum Deposition Adult Farmer 136 A 4 2E 11 7 0E 11 3 9E06 4 8E-06 M 225 Onsite Maximum Deposition
1368 1 9E 13 3 2E 13 1 4E08 1 BE 08
136C 1 IE 12 1 9E12 5 7E 08 7 2E-08
136D 2 IE 14 3 5E 14 2 1E-09 2 6E 09
225A 2 3E 07 41E07 4 4E 03 5 5E 03
2258 2 IE 08 3 6E08 7 7E 03 9 5E-03
Total 2 5E-07 4 5E-07 1 2E 02 1 5E02
Child Farmer 136A 1 9E 11 3 2E 11 BSE 06 1 OE-05
1368 8 9E 14 1 5E 13 3 1E-08 3 7E 08
136C 5 2E 13 8 7E 13 1 2E 07 1 5E 07
136D 9 7E 15 1 6E 14 4 6E 09 5 5E-09
225A 6 6E0B 1 2E-07 9 4E-03 1 1E02
2258 6 6E 09 1 1E08 1 7E 02 21E-02
Total 7 2E 08 1 3E07 2 7E-02 3 2E 02
Adult Resident 136A 3 2E 11 5 5E 11 2 2E 06 2 6E-06
1368 1 5E 13 2 5E 13 BOE 09 9 4E 09
136C BBE 13 1 5E 12 3 IE 08 3 6E 08
136D 1 6E 14 2 7E 14 1 2E 09 1 4E-09
225A 5 9E 08 1 0E07 2 4E-03 2 BE 03
225B 7 1E-09 1 2E-08 4 6E 03 5 4E-03
Total 6 6E08 1 IE 07 7 0E 03 8 2E 03
Child Resident 136A 1 6E 11 2 BE 11 5 4E-06 6 3E 06
1368 7 3E 14 1 2E 13 1 9E 08 2 3E-08
136C 4 3E 13 7 2E 13 7 5E-0B BSE 08
136D 7 BE 15 1 3E 14 2 9E 09 3 4E-09
225A 2 BE 08 4 BE 08 5 9E 03 6 9E 03
225B 3 4E 09 5 7E-09 1 IE 02 1 3E 02
Total 3 IE-OB 5 3E 08 1 7E 02 2 OE-02
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 11 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
M 225 Onsite Maximum Gaseous Adult Farmer 136A 2 2E09 3 BE 09 4 7E 07 9 OE-07
136B 9 7E 12 1 BE 11 2 IE 09 4 1E-09
136C 5 8E 11 98E 11 1 3E08 2 4E-0B
136D 1 OE 12 1 7E 12 2 3E 10 4 3E 10
225A 3 3E-06 5 5E 06 7 2E 04 1 4E-03
225B 4 2E-07 7 IE 07 9 IE 05 1 8E-04
Total 3 7E06 6 2E06 8 1E-04 1 6E-03
Child Fanner 136A 7 6E 10 1 3E 09 5 4E-07 1 OE 06
1368 3 4E 12 5 7E 12 2 4E-09 4 6E 09
136C 2 0E 11 3 4E 11 1 5E-08 2 BE 08
136D 3 6E 13 6 1E-13 2 6E 10 4 9E 10
225A 1 2E 06 1 9E-06 8 2E 04 1 6E 03
2258 1 5E 07 2 5E-07 1 OE 04 2 0E 04
Total 1 3E 06 2 2E 06 9 3E 04 1 BE 03
Adult Resident 136A 1 1E-09 1 8E-09 3 3E-07 6 7E 07
1368 4 7E 12 BOE 12 1 5E 09 BOE 09
136C 2 8E 11 4 8E 11 8 9E09 1 8E 08
136D 50E 13 B5E 13 1 BE 10 3 2E 10
225A 1 6E 06 2 7E-06 5 0E 04 1 OE 03
2258 2 0E 07 3 4E 07 6 4E 05 1 3E 04
Total 1 SE 06 3 0E 06 5 7E 04 1 2E 03
Child Resident 136A 5 0E 10 8 4E 10 3 4E 07 6 BE 07
1368 2 3E 12 BBE 12 1 5E 09 3 IE 09
136C 1 4E 11 2 3E 11 9 IE 09 1 BE 08
136D 2 4E 13 41E 13 1 6E 10 3 3E 10
225A 7 7E 07 1 3E 06 5 IE 04 1 OE 03
2258 9SE 08 1 6E 07 6 6E05 1 3E 04
Total BBE 07 1 5E 06 5 8E04 1 2E 03
M 225 Onsite Maximum Particulate Adult Farmer 136A 2 2E09 3 6E09 4 7E 07 9 0E 07
1368 0 OE+00 0 OE+00 0 OE+00 0 OE+00
136C 0 OE+00 0 OE+00 0 OE+00 0OE+00
136D 0 OE+00 0 OE+00 0 OE+00 0 OE+00
225A 0 OE+00 0 OE+00 0 OE+00 0 OE+00
2258 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Total 2 2E 09 3 6E 09 4 7E-07 9 OE-07
Child Farmer 136A 7 BE 10 1 3E 09 5 4E 07 1 OE-06
1368 0 OE+00 0 OE+00 0 OE+00 0 OE+00
136C 0 OE+00 0 OE+00 0 OE+00 0 OE+00
136D 0 OE+00 0 OE+00 0 OE+00 0 OE+00
225A 0 OE+00 0 OE+00 0 OE+00 0 OE+00
2258 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Total 7 6E 10 1 3E 09 5 4E 07 1 OE-06
Adult Resident 136A 1 IE 09 1 BE 09 3 3E 07 6 7E-07
136B 0 OE+00 0 OE+00 0 OE+00 0 OE+OO
136C 0 OE+00 0 OE+00 0 OE+00 0 OE+OO
136D 0 OE+00 0 OE+00 0 OE+00 0 OE+00
225A 0 OE+00 0 OE+00 0 OE+00 0 OE+OO
225B 0 OE+00 0 OE+00 0 OE+00 0 OE+OO
Total 1 IE 09 1 BE 09 3 3E-07 6 7E 07
Child Resident 136A 5 0E 10 B4E 10 3 4E07 6 8E 07
1368 0 OE+00 0 OE+00 0 OE+00 0 OE+00
136C 0 OE+00 0 OE+00 0 OE+00 0 OE+OO
136D 0 OE+00 0 OE+00 0 OE+00 0 OE+00
225A 0 OE+00 0 OE+00 0 OE+00 0 OE+00
2258 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Total 5 0E-10 8 4E 10 3 4E 07 BBE 07
TABLE 25
SUMMARY OF CANCER RISKS AND HAZARD INDICES BY SOURCE
THIOKOL PROPULSION INC
BRIGHAM CITY UTAH
PAGE 12 OF 12
Exposure Point Receptor Source Total Cancer Risk Total Hazard Quotient Exposure Point Receptor Source Average Maximum Average Maximum
Thiokol Ranch Pond Adult Farmer 136A 4 6E 10 7 BE 10 6 4E 07 8 7E 07
1368 1 BE 12 3 1E 12 9 7E 09 1 2E 08
136C 7 BE 12 1 3E 11 6 0E 09 8 BE 09
136D 1 6E 13 2 7E 13 2 0E 10 2 7E 10
225A 1 2E-08 2 0E08 3 4E 05 4 4E-05
225B 1 4E09 2 3E09 1 BE-06 2 3E-06
Total 1 4E 08 2 4E 08 3 6E-05 4 7E 05
Child Farmer 136A 1 6E 10 2 7E 10 1 3E 06 1 6E 06
136B 5 7E 13 9 9E 13 2 IE 08 2 6E 08
136C 2 8E 12 4 6E 12 1 IE 08 1 4E 08
136D 5 6E 14 9 5E 14 4 0E 10 5 IE 10
225A 4 0E 09 6 8E09 7 4E 05 9 0E05
2258 4 BE 10 8 IE 10 3 2E-06 41E-06
Total 4 6E-09 7 9E09 7 8E-05 9 6E-05
Adult Resident 136A 2 2E 10 3 7E 10 3 7E 07 4 9E07
136B 68E 13 1 1E 12 5 7E 09 6 9E 09
136C 3 8E 12 6 4E 12 3 3E 09 4 9E 09
136D 7 6E 14 1 3E 13 1 2E 10 1 6E 10
225A 5 IE 09 B7E 09 2 0E 05 2 5E 05
2258 6 5E 10 1 IE 09 9 4E 07 1 3E-06
Total 6 OE-09 1 OEOB 2 2E05 2 7E-05
Child Resident 136A 1 OE 10 1 7E 10 8 2E-07 1 0E06
1368 3 2E 13 5 4E 13 1 4E 08 1 6E OS
136C 1 BE 12 3 IE 12 6 4E 09 8 5E 09
136D 3 6E 14 6 IE 14 2 5E10 3 IE 10
225A 2 5E 09 4 1E09 4 7E 05 5 6E 05
2258 3 IE 10 5 3E 10 2 0E 06 2 5E 06
Total 2 9E 09 4 BE 09 5 0E 05 6 0E 05
Notes
1 136 A 08 Treatment at Burn Stations 1
136 8 08 Treatment at Burn Station 13
136 C OB Treatment at Burn Station 14
136 D OD Treatment at Burn Station 13
225A OB Treatment at M 225
2258 OD Treatment at M 225
12
TABLE 26
CANCER RISKS AND HAZARD INDICES
FOR INDUSTRIAL WORKERS AT AUTOLIV PLANT
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
Source Cancer Risk Hazard Index Source Average Maximum Average Maximum
136A 3 2E-12 5 3E-12 7 8E-08 1 6E-07
136B 1 9E-14 2 8E-14 3 1E-10 6 2E-10
136C 7 0E-14 1 2E-13 1 7E-09 3 5E-09
136D 1 1E-15 1 9E-15 2 8E-11 5 7E-11
225A 1 3E-10 2 2E-10 3 3E-06 6 7E-06
225B 2 5E-11 4 1E-11 2 8E-01 5 7E-01
Total Risk from all Sources 1 6E-10 2 7E-10 2 8E-01 5 7E-01
TABLE 27
RISK BY EXPOSURE PATHWAY
ADULT FARMER FROM SOURCE 225A
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
Exposure Pathway Total Cancer Risk Total Hazard Quotient Exposure Pathway Average | Maximum Average | Maximum
Adult Farmer
Inhalation of Vapor and Particulates 3 4E 08 5 7E-08 5 6E-04 1 1E-03
Ingestion of Homegrown Produce 3 5E-06 5 9E-06 1 2E-05 2 1E-05
Ingestion of Homegrown Beef 3 8E-08 6 5E 08 5 IE 05 8 6E-05
Ingestion of Homegrown Chicken 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+OO
Ingestion of Eggs from Homegrown Chicken 0 OE+OO 0 OE+00 0 OE+OO 0 OE+00
Ingestion of Milk from Homegrown Cows 1 4E-07 2 3E-07 1 8E-04 3 1E-04
Ingestion of Homegrown Pork 1 5E-09 2 5E-09 1 9E-06 3 3E 06
Incidental Ingestion of Soil 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+OO
Total Risk Across All Pathways 3 7E 06 6 2E-06 8 1E-04 1 6E-03
Child Farmer
Inhalation of Vapor and Particulates 5 1E-09 8 5E 09 5 6E 04 1 1E-03
Ingestion of Homegrown Produce 1 3E-06 2 IE 06 2 9E 05 4 9E-05
Ingestion of Homegrown Beef 3 5E-09 6 OE-09 3 2E-05 5 3E-05
Ingestion of Homegrown Chicken 0 OE+OO 0 OE+00 0 OE+OO 0 OE+OO
Ingestion of Eggs from Homegrown Chicken 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+OO
Ingestion of Milk from Homegrown Cows 3 4E-08 5 8E 08 3 0E 04 5 1E-04
Ingestion of Homegrown Pork 1 7E-10 2 8E-10 1 5E-06 2 5E-06
Incidental Ingestion of Soil 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+00
Total Risk Across All Pathways 1 3E-06 2 2E-06 9 3E-04 1 8E-03
Adult Resident
Inhalation of Vapor and Particulates 2 5E-08 4 3E-08 5 6E-04 1 1E-03
Ingestion of Homegrown Produce 1 8E-06 3 OE-06 8 3E-06 1 4E-05
Ingestion of Homegrown Beef 0 OE+OO 0 OE+OO 0 OE+00 0 OE+OO
Ingestion of Homegrown Chicken 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+OO
Ingestion of Eggs from Homegrown Chicken 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+00
Ingestion of Milk from Homegrown Cows 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+OO
Ingestion of Homegrown Pork 0 OE+00 0 OE+OO 0 OE+OO 0 OE+00
Incidental Ingestion of Soil 0 OE+00 0 OE+OO 0 OE+OO 0 OE+00
Total Risk Across All Pathways 1 8E-06 3 OE-06 5 7E 04 1 2E-03
Child Resident
Inhalation of Vapor and Particulates 5 1E-09 8 5E-09 5 6E-04 1 IE 03
Ingestion of Homegrown Produce 8 6E 07 1 4E-06 2 OE-05 3 4E-05
Ingestion of Homegrown Beef 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+00
Ingestion of Homegrown Chicken 0 OE+OO 0 OE+OO 0 OE+OO 0 OE+OO
Ingestion of Eggs from Homegrown Chicken 0 OE+OO 0 OE+00 0 OE+00 0 OE+OO
Ingestion of Milk from Homegrown Cows 0 OE+OO 0 OE+OO 0 OE+00 0 OE+OO
Ingestion of Homegrown Pork 0 OE+OO 0 OE+00 0 OE+OO 0 OE+OO
Incidental Ingestion of Soil 0 OE+OO 0 OE+00 0 OE+00 0 OE+OO
Total Risk Across All Pathways 8 6E-07 1 5E 06 5 BE 04 1 2E-03
TABLE 28
CHEMICAL-SPECIFIC RISKS
ADULT FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 1 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
1 2 3-Tnmethylbenzene 0 OE+00 0 OE+00 7 9E-10 1 3E-09
1 2 4-Tnmethylbenzene 0 OE+00 0 OE+00 1 3E-08 2 2E-08
1 4-Diethylbenzene 1 8E-14 2 9E-14 1 7E-11 2 8E-11
1 -Chloronaphthalene 0 OE+00 0 OE+00 1 1E-12 1 8E-12
1-Naphthlamine 3 0E-12 5 0E-12 1 5E-09 2 5E-09
2 2 4-Trimethvlpentane 0 OE+00 0 OE+00 1 1E-10 1 8E-10
2 2-Dimethylbutane 0 OE+00 0 OE+00 5 8E-11 9 4E-11
2 3,4,-Trimethylpentane 0 OE+00 0 OE+OO 1 9E-11 31E-11
2 3-Dimethylbutane 0 OE+00 0 OE+00 1 6E-10 2 7E-10
2 3-Dimethylpentane 0 OE+00 0 OE+00 1 6E-10 3 3E-10
2 4-Dimethylpentane 0 OE+00 0 OE+00 7 3E-11 1 2E-10
2 5-Dimethylbenzaldehyde 0 OE+00 0 OE+00 9 9E-10 1 6E-09
2 6-Dichlorophenol 0 OE+00 0 OE+00 1 1E-09 1 2E-09
2-Acetylaminofluorene 0 OE+OO 0 OE+00 9 8E-07 1 6E-06
2-Ethyltoluene 8 8E-15 1 4E-14 6 5E-12 1 1E-11
2-Hexanone 0 OE+00 0 OE+00 5 8E-11 9 4E-11
2-Methyhexane 0 OE+00 0 OE+OO 1 8E-10 3 9E-10
2-Methylnapthalene 0 OE+00 0 OE+00 6 5E-09 1 2E-08
2-Methylpentane 0 OE+OO 0 OE+00 5 8E-10 1 2E-09
2-Naphthaylamine 2 0E-10 3 4E-10 1 4E-05 2 3E-05
3 3 -Dimethylbenzidine 1 OE-06 1 7E-06 0 OE+00 0 OE+00
3-Ethyltoluene 5 4E-14 1 4E-13 3 8E-11 9 9E-11
3-Methylhexane 0 OE+OO 0 OE+00 3 7E-10 7 9E-10
3-methylheptane 0 OE+00 0 OE+00 1 1E-10 2 2E-10
4 6-Dintro-2-methylphenol 0 OE+00 0 OE+00 5 2E-07 8 8E-07
4-Aminobiphenyl 0 OE+00 0 OE+00 4 7E-07 7 8E-07
4-Ethyltoluene 1 1E-13 1 9E-13 7 9E-11 1 4E-10
7 12-Dimethlbenz(a)anthracene 1 5E-08 2 5E-08 0 OE+00 0 OE+00
Acenaphthene 0 OE+00 0 OE+00 3 7E-11 6 3E-11
Acenaphthylene 0 OE+OO 0 OE+00 1 9E-10 3 2E-10
Acetaldehyde 1 4E-12 2 2E-12 1 2E-07 2 OE-07
Acetone 0 OE+00 0 OE+00 1 7E-11 3 3E-11
Acetonitnle 0 OE+00 0 OE+00 2 8E-09 4 5E-09
Acetophenone 0 OE+00 0 OE+00 1 6E-10 2 2E-10
Acrylonitnle 5 6E-12 9 6E-12 7 2E-08 1 2E-07
Aluminum 0 OE+00 0 OE+00 2 6E-04 3 4E-04
Aniline 1 OE-13 1 7E-13 1 1E-07 1 9E-07
Anthracene 0 OE+00 0 OE+00 9 8E-12 1 7E-11
Antimony 0 OE+00 0 OE+00 3 2E-07 6 OE-07
Arsenic 1 1E-13 1 3E-13 1 5E-09 1 8E-09
Banum 0 OE+00 0 OE+00 2 3E-09 3 8E-09
Benzaldehyde 0 OE+00 0 OE+00 6 1E-10 8 7E-10
Benzene 3 5E-12 5 9E-12 2 6E-08 4 4E-08
Benzidine 2 1E-06 3 6E-06 5 3E-06 9 OE-06
Benzo(a)anthracene 6 6E-11 1 IE 10 0 OE+00 0 OE+00
Benzo(a)pyrene 2 1E-09 3 5E-09 0 OE+00 0 OE+00
Benzo(b)fluoranthene 2 0E-11 3 5E-11 0 OE+00 0 OE+00
Benzo(g h i)perylene 0 OE+00 0 OE+00 2 OE-04 3 3E-04
Benzo( k)fluoranthene 1 OE-10 1 7E-10 0 OE+00 0 OE+00
Benzoic acid 0 OE+00 0 OE+00 9 5E-11 1 3E-10
Benzyl alcohol 0 OE+00 0 OE+OO 1 1E-12 1 9E-12
Benzyl chloride 2 1E-13 3 4E-13 7 5E-09 1 2E-08
Beryllium 3 7E-14 6 OE-14 1 3E-09 2 2E-09
TABLE 28
CHEMICAL-SPECIFIC RISKS
ADULT FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 2 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Bis(2-chlorethyl)ether 1 6E-12 2 7E-12 0 OE+00 0 OE+00
Bromodichloromethane 1 1E-13 1 7E-13 1 5E-10 2 4E-10
Bromoform (Tribromomethane) 1 OE-14 1 7E-14 2 4E-10 3 9E-10
Bromophenyl-phenylether 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Butylbenzylphthalate 1 3E-13 2 2E-13 5 8E-10 9 9E-10
Cadmium 7 7E-14 1 3E-13 3 7E-10 61E-10
Carbazole 1 3E-10 2 1E-10 0 OE+00 0 OE+00
Carbon disulfide 0 OE+00 0 OE+00 3 9E-10 9 3E-10
Carbon tetrachloride 3 3E-12 3 9E-12 2 OE-09 2 4E-09
Chlorine 0 OE+00 0 OE+00 1 9E-04 5 7E-04
Chloro-3-methylphenol 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chloroacetonitrile 0 OE+00 0 OE+00 2 6E-10 4 2E-10
Chloroaniline p-4 8E-15 8 1E-15 6 6E-09 1 1E-08
Chlorobenzene 0 OE+00 0 OE+OO 7 8E-10 1 5E-09
Chloroethane 0 OE+00 0 OE+00 3 4E-13 5 5E-13
Chloroform (Trichloromethane) 1 9E-12 2 4E-12 1 5E-09 1 9E-09
Chloroisopropyl ether bis-1 2-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chloronaphthalene 2-0 OE+00 0 OE+00 2 7E-11 4 6E-11
Chlorophenol 2-0 OE+00 0 OE+OO 1 9E-09 2 8E-09
Chlorophenyl-phenylether 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chromium 0 OE+00 0 OE+00 7 7E-13 9 4E-13
Chrysene 8 6E-14 1 4E-13 0 OE+00 0 OE+00
Cobalt 4 6E-11 8 0E-11 1 5E-06 2 6E-06
Copper 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Cresol m-0 OE+00 0 OE+00 1 8E-10 3 OE-10
Cresol o-0 OE+00 0 OE+OO 2 6E-10 4 3E-10
Crotonaldehyde 0 OE+00 0 OE+00 9 4E-06 1 5E-05
Cumene (Isopropylbenzene) 0 OE+00 0 OE+00 1 4E-11 2 2E-11
Di-n-butyl phthalate 0 OE+OO 0 OE+00 8 7E-09 1 5E-08
Di-n-octylphthalate 1 2E-10 2 OE-10 0 OE+00 0 OE+00
Dibenz(a h)anthracene 9 6E-08 1 6E-07 0 OE+00 0 OE+00
Dibenzofuran 0 OE+OO 0 OE+00 0 OE+OO 0 OE+00
Dibromochloromethane 1 6E-13 2 6E-13 1 7E-10 2 7E-10
Dichlorobenzene 1 2-0 OE+00 0 OE+00 3 1E-11 5 1E-11
Dichlorobenzene 1 3-0 OE+00 0 OE+00 1 8E-09 3 OE-09
Dichlorobenzene 1 4-6 1E-14 9 9E-14 1 2E-11 2 OE-11
Dichlorobenzidine 3 3-1 3E-09 2 3E-09 0 OE+00 0 OE+00
Dichlorodifluoromethane 0 OE+00 0 OE+00 1 6E-11 2 6E-11
Dichloroethane 1 1-3 8E-15 6 3E-15 8 4E-12 1 4E-11
Dichloroethane 1 2- (Ethylene Dichlonde) 1 1E-13 1 7E-13 3 0E-12 4 9E-12
Dichloroethylene 1 1-0 OE+00 0 OE+00 2 9E-11 4 7E-11
Dichloroethylene cis-1 2-0 OE+00 0 OE+00 4 4E-16 7 2E-16
Dichloroethylene-1 2 (trans) 0 OE+OO 0 OE+00 1 6E-10 2 6E-10
Dichiorophenol 2 4-0 OE+00 0 OE+00 1 4E-09 1 8E-09
Dichloropropane 1 2-2 7E-14 4 5E-14 1 2E-09 2 OE-09
Diethyl phthalate 0 OE+00 0 OE+00 5 5E-13 9 1E-13
Dimethyl phthalate 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Dimethyl phenol 2 4-0 OE+00 0 OE+00 1 4E-09 2 4E-09
Dinitrobenzene 1 3-0 OE+00 0 OE+OO 2 3E-08 3 9E-08
Dinitrophenol 2 4-0 OE+00 0 OE+00 4 8E-08 8 2E-08
Dinitrotoluene 2 4-4 3E-13 6 4E-13 1 5E-10 2 2E-10
Dinitrotoluene 2 6-9 9E-15 1 2E-14 2 5E-11 3 1E-11
Dinoseb 0 OE+00 0 OE+00 4 6E-21 7 7E-21
TABLE 28
CHEMICAL-SPECIFIC RISKS
ADULT FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 3 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Dioxane 1 4-1 5E-14 2 4E-14 2 3E-12 3 8E-12
Diphenylamine 0 OE+OO 0 OE+00 9 4E-23 1 6E-22
Diphenylhydrazine 1 2-1 1E-12 1 9E-12 0 OE+00 0 OE+00
Ethyl methacrylate 0 OE+00 0 OE+00 6 6E-11 1 1E-10
Ethyl methanesulfonate 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Ethylbenzene 6 9E-14 1 2E-13 4 8E-11 8 5E-11
Ethylene Dibromide 4 OE-12 6 6E-12 1 3E-09 2 1E-09
Ethylhexyi phthalate bis-2-5 5E-13 9 3E-13 3 5E-09 5 8E-09
Fluoranthene 0 OE+OO 0 OE+00 4 5E-10 5 7E-10
Fluorene 0 OE+00 0 OE+00 8 1E-11 1 OE-10
Formaldehyde 3 4E-12 5 9E-12 4 7E-08 8 2E-08
Freon 113 0 OE+00 0 OE+00 4 5E-13 7 4E-13
Freon 114 0 OE+00 0 OE+00 9 8E-11 1 6E-10
HeptaCDD 1 2 3 4 6 7 8-2 7E-13 5 4E-13 0 OE+00 0 OE+00
HeptaCDF 1 2 3 4 6 7 8-6 2E-11 1 2E-10 0 OE+00 0 OE+00
HeptaCDF 1 2 3 4 7 8 9-9 OE-11 1 7E-10 0 OE+OO 0 OE+00
HexaCDD 1 2 3 4 7 8-3 1E-12 4 2E-12 0 OE+00 0 OE+00
HexaCDD 1 2 3 6 7 8-8 4E-12 1 6E-11 0 OE+00 0 OE+00
HexaCDD 1 2 3 7 8 9-4 OE-12 6 6E-12 0 OE+00 0 OE+OO
HexaCDF 1 2 3,4,7 8-2 6E-10 5 3E-10 0 OE+OO 0 OE+00
HexaCDF, 1 2 3 6 7 8-1 7E-10 3 5E-10 0 OE+00 0 OE+00
HexaCDF 1 2 3 7 8 9-2 2E-10 4 5E-10 0 OE+00 0 OE+00
HexaCDF, 2 3 4 6 7 8-2 OE-10 4 2E-10 0 OE+00 0 OE+00
Hexachloro-1 3-butadiene (Perchlorobutadiene) 2 8E-13 4 6E-13 3 5E-11 5 8E-11
Hexachlorobenzene 3 5E-11 9 OE-11 5 4E-09 1 4E-08
Hexachlorocyclopentadiene 0 OE+00 0 OE+00 7 7E-07 1 3E-06
Hexachloroethane (Perchloroethane) 1 9E-14 3 2E-14 2 8E-12 4 8E-12
Hexachloropropene 3 OE-14 4 5E-14 1 9E-10 2 9E-10
Hexane 0 OE+00 0 OE+00 6 5E-10 1 3E-09
Hydrogen chloride 0 OE+00 0 OE+00 1 2E-07 1 9E-07
lndeno(1 2 3-cd) pyrene 9 OE-12 1 5E-11 0 OE+00 0 OE+00
Isophorone 1 2E-15 2 OE-15 3 8E-12 6 5E-12
Lead 2 2E-14 4 OE-14 2 1E-09 3 9E-09
Manganese 0 OE+00 0 OE+OO 3 5E-05 8 7E-05
Mercury 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Methacryionitnle 0 OE+00 0 OE+00 8 5E-08 9 8E-08
Methyl Methacrylate 0 OE+00 0 OE+00 2 9E-11 4 7E-11
Methyl bromide (Bromomethane) 0 OE+00 OOE+00 1 6E-09 2 7E-09
Methyl chloride (Chloromethane) 2 9E-13 4 7E-13 3 2E-09 5 OE-09
Methyl ethyl ketone (2-Butanone) 0 OE+00 0 OE+00 1 8E-11 2 6E-11
Methyl isobutyl ketone 0 OE+00 0 OE+00 3 1E-12 5 OE-12
Methyl tert-butyl ether 5 2E-19 8 4E-19 1 8E-12 3 OE-12
Methylene chloride 4 OE-14 5 8E-14 1 3E-10 2 OE-10
N-Nitrosodiethylamine 1 9E-10 3 2E-10 0 OE+00 0 OE+00
N-Nitrosodimethylamine 6 1E-11 1 OE-10 3 2E-10 5 4E-10
N-Nitrosomethylethylamine 8 3E-13 1 4E 12 0 OE+00 0 OE+00
N-Nitrosomorpholme 5 OE-12 8 5E-12 0 OE+00 0 OE+00
N-Nitrosopyrrolidine 2 9E-12 4 9E-12 0 OE+00 0 OE+00
Naphthalene 4 2E-12 7 5E-12 7 3E-08 1 3E-07
Nickel 1 3E-12 2 2E 12 4 6E-08 8 2E-08
Nitroaniline 2-3 1E-16 5 3E-16 1 8E-09 3 1E-09
Nitroaniline 3-1 8E-15 3 OE-15 3 1E-08 5 2E-08
Nitroaniline 4-1 3E-13 2 2E-13 1 1E-08 1 9E-08
TABLE 28
CHEMICAL-SPECIFIC RISKS
ADULT FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 4 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Nitrobenzene 0 OE+00 0 OE+00 4 4E-09 7 3E-09
Nitrophenol 2-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Nitrophenol 4-0 OE+00 0 OE+00 4 9E-08 8 2E-08
Nitroso-di-n-butylamine n-7 OE-12 1 2E-11 0 OE+00 0 OE+00
Nitrosodiphenylamine N-8 1E-16 1 4E-15 0 OE+00 0 OE+00
Nitrosodipropylamine n-8 8E-12 1 5E-11 0 OE+00 0 OE+00
OctaCDD 1 2 3 4 6 7 8 9-1 8E-14 2 7E-14 0 OE+00 0 OE+OO
OctaCDF 1 2 3 4 6,7 8 9-4 1E-13 7 3E-13 0 OE+00 0 OE+00
PentaCDD 1 2 3 7 8-2 3E-10 4 2E-10 0 OE+00 0 OE+OO
PentaCDF 1 2 3 7 8-8 6E-11 1 7E-10 0 OE+00 0 OE+00
PentaCDF 2 3 4 7 8-1 6E-09 3 5E-09 0 OE+00 0 OE+00
Pentachloro benzene 0 OE+00 0 OE+00 4 5E-09 7 OE-09
Pentachloroethane 0 OE+00 0 OE+00 8 5E-11 1 4E-10
Pentachloronitrobenzene (PCNB) 3 5E-13 5 9E-13 7 5E-10 1 3E-09
Pentachlorophenol 1 2E-10 2 OE-10 5 7E-08 9 5E-08
Perchlorate 0 OE+00 0 OE+00 0 OE+OO 0 OE+00
Phenanthrene 0 OE+00 0 OE+00 2 3E-10 3 1E-10
Phenol 0 OE+00 0 OE+00 2 1E-10 2 9E-10
Phosphorus 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Propanal 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Propylbenzene 1 9E-14 3 1E-14 1 3E-11 2 3E-11
Pyrene 0 OE+00 0 OE+00 4 8E-10 8 2E-10
Pyridine 0 OE+00 0 OE+00 3 2E-09 5 4E-09
Safrole 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Selenium 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Silver 0 OE+00 0 OE+00 1 2E-11 2 4E-11
Styrene 0 OE+00 0 OE+00 1 1E-11 1 4E-11
TetraCDD 2 3 7 8-1 3E-10 2 2E-10 1 7E-06 3 OE-06
TetraCDF 2 3 7 8-3 1E-10 5 2E-10 0 OE+00 0 OE+00
Tetrachlorobenzene 1 2 4 5-0 OE+00 0 OE+00 7 1E-09 1 2E-08
Tetrachloroethane 112 2-1 9E-13 3 1E-13 2 7E-11 4 4E-11
Tetrachloroethylene (Perchloroethylene) 1 5E-13 2 3E-13 1 6E-10 2 5E-10
Tetrachlorophenol 2 3 4 6-0 OE+00 0 OE+00 9 2E-11 1 6E-10
Tetrahydrofuran 1 4E-14 2 2E-14 4 3E-11 6 7E-11
Thallium (1) 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Toluene 0 OE+00 0 OE+00 6 4E-11 1 2E-10
Toluidine o-2 9E-12 4 8E-12 0 OE+00 0 OE+00
Tnchlorobenzene 12 4-4 OE-17 6 6E-17 4 2E-09 6 9E-09
Trichloroethane 111-0 OE+00 0 OE+00 2 4E-12 3 9E-12
Tnchloroethane 112-8 8E-14 1 4E-13 1 1E-14 1 7E-14
Trichloroethylene 1 6E-14 2 OE-14 2 4E-11 2 9E-11
Tnchlorofluoromethane (Freon 11) 0 OE+00 0 OE+00 9 OE-12 1 5E-11
Trichlorophenol 2 4 5-0 OE+00 0 OE+00 6 8E-11 1 1E-10
Tnchlorophenol 2 4 6-4 5E-14 5 6E 14 5 8E-10 7 2E-10
Tnmethylbenzene 1 3 5-0 OE+00 0 OE+00 4 1E-09 8 1E-09
Tnnitrobenzene 13 5 (sym-) 0 OE+00 0 OE+00 4 2E-10 7 OE-10
Undecane 0 OE+00 0 OE+00 9 9E-10 1 9E-09
Vinyl Chloride 3 9E-13 8 OE-13 7 8E-10 1 6E-09
Xylene m-0 OE+00 0 OE+00 2 3E-10 4 4E-10
Xylene o-0 OE+00 0 OE+00 8 8E-11 1 5E-10
Zinc 0 OE+00 0 OE+00 4 6E-13 8 9E-13
bis(2-Chloroethoxy)methane 0 OE+00 0 OE+00 8 OE-10 1 4E-09
o-Tolualdehyde 0 OE+00 0 OE+00 2 9E-10 4 OE-10
TABLE 28
CHEMICAL-SPECIFIC RISKS
ADULT FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 5 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
p-Dimethylaminoazobenzene 3 9E-08 6 6E-08 0 OE+00 0 OE+00
trans-1 3-Dichloropropene 1 9E-14 3 OE-14 4 OE-10 6 6E-10
Total 3 3E-06 5 5E-06 7 2E-04 1 4E-03
TABLE 29
CHEMICAL-SPECIFIC RISKS
CHILD FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 1 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
1 2 3-Tnmethylbenzene 0 OE+OO 0 OE+OO 7 9E-10 1 3E-09
1 2 4-Tnmethylbenzene 0 OE+OO 0 OE+00 1 3E-08 2 2E-08
1 4-Diethylbenzene 3 OE-15 4 9E-15 2 OE-11 3 3E-11
1 -Chloronaphthalene 0 OE+00 0 OE+00 1 9E-12 3 OE-12
1-Naphthlamine 4 5E-13 7 5E-13 31E-09 5 2E-09
2 2 4-Trimethylpentane 0 OE+00 0 OE+00 1 1E-10 1 8E-10
2 2-Dimethylbutane 0 OE+00 0 OE+00 5 8E-11 9 4E-11
2 3 4 -Tnmethylpentane 0 OE+00 0 OE+00 1 9E-11 3 1E-11
2 3-Dimethylbutane 0 OE+OO 0 OE+OO 1 6E-10 2 7E-10
2 3-Dimethylpentane 0 OE+00 0 OE+00 1 6E-10 3 3E-10
2 4-Dimethylpentane 0 OE+00 0 OE+00 7 3E-11 1 2E-10
2 5-Dimethylbenzaldehyde 0 OE+00 0 OE+OO 1 9E-09 3 OE-09
2 6-Dichlorophenol 0 OE+00 0 OE+00 2 OE-09 2 3E-09
2-Acetylaminofluorene 0 OE+00 0 OE+00 1 7E-06 2 9E-06
2-Ethyltoluene 1 4E-15 2 2E-15 7 OE-12 1 1E-11
2-Hexanone 0 OE+00 0 OE+00 5 8E-11 9 4E-11
2-Methyhexane 0 OE+00 0 OE+00 1 8E-10 3 9E-10
2-Methylnapthalene 0 OE+00 0 OE+00 1 5E-08 2 8E-08
2-Methylpentane 0 OE+00 0 OE+00 5 8E-10 1 2E-09
2-Naphthaylamine 3 OE-11 5 OE-11 2 3E-05 3 9E-05
3 3-Dimethylbenzidine 3 6E-07 6 1E-07 0 OE+00 0 OE+OO
3-Ethyltoluene 8 1E-15 2 1E-14 3 8E-11 9 9E-11
3-Methylhexane 0 OE+00 0 OE+00 3 7E-10 7 9E-10
3-methylheptane 0 OE+00 0 OE+00 1 1E-10 2 2E-10
4 6-Dintro-2-methylphenol 0 OE+00 0 OE+00 1 1E-06 1 9E-06
4-Aminobiphenyl 0 OE+00 0 OE+00 8 9E-07 1 5E-06
4-Ethyltoluene 1 6E-14 3 OE-14 8 4E-11 1 5E-10
7 12-Dimethlbenz(a)anthracene 3 1E-09 5 3E-09 0 OE+00 0 OE+00
Acenaphthene 0 OE+00 0 OE+00 3 8E-11 6 4E-11
Acenaphthylene 0 OE+00 0 OE+00 2 9E-10 5 OE-10
Acetaldehyde 2 1E-13 3 4E-13 1 2E-07 2 OE-07
Acetone 0 OE+OO 0 OE+OO 1 7E-11 3 3E-11
Acetonitnle 0 OE+00 0 OE+00 2 8E-09 4 5E-09
Acetophenone 0 OE+00 0 OE+00 1 6E-10 2 2E-10
Acrylonitnle 8 4E-13 1 4E-12 7 2E-08 1 2E-07
Aluminum 0 OE+00 0 OE+00 2 6E-04 3 4E-04
Aniline 1 5E-14 2 6E-14 1 1E-07 1 9E-07
Anthracene 0 OE+00 0 OE+00 1 1E-11 1 8E-11
Antimony 0 OE+00 0 OE+00 3 2E-07 6 OE-07
Arsenic 1 6E-14 2 OE-14 1 5E-09 1 8E-09
Banum 0 OE+00 0 OE+00 2 3E-09 3 8E-09
Benzaldehyde 0 OE+00 0 OE+00 6 1E-10 8 7E-10
Benzene 5 3E-13 8 8E-13 2 6E-08 4 4E-08
Benzidine 7 6E-07 1 3E-06 1 3E-05 2 2E-05
Benzo(a)anthracene 1 4E-11 2 4E-11 0 OE+00 0 OE+00
Benzo(a)pyrene 4 5E-10 7 5E-10 0 OE+00 0 OE+00
Benzo(b)fluoranthene 4 3E-12 7 3E-12 0 OE+00 0 OE+00
Benzo(g h Operylene 0 OE+00 0 OE+00 2 8E-04 4 7E-04
Benzo(k)fluoranthene 2 2E-11 3 7E-11 0 OE+00 0 OE+00
Benzoic acid 0 OE+OO 0 OE+00 9 5E-11 1 3E-10
Benzyl alcohol 0 OE+00 OOE+00 2 6E-12 4 4E-12
Benzyl chloride 3 1E-14 5 1E-14 7 5E-09 1 2E-08
Beryllium 5 5E-15 9 OE-15 1 3E-09 2 2E-09
TABLE 29
CHEMICAL-SPECIFIC RISKS
CHILD FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 2 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Bis(2-chlorethyl)ether 2 4E-13 4 1E-13 0 OE+00 0 OE+00
Bromodichloromethane 1 6E-14 2 6E-14 1 5E-10 2 4E-10
Bromoform (Tribromomethane) 1 6E-15 2 6E-15 2 4E-10 3 9E-10
Bromophenyl-phenylether 4-0 OE+OO OOE+00 0 OE+00 0 OE+OO
Buty 1 benzyl phthalate 2 8E-14 4 7E-14 8 3E-10 1 4E-09
Cadmium 1 1E-14 1 9E-14 3 7E-10 6 1E-10
Carbazole 4 8E-11 7 4E-11 0 OE+00 0 OE+00
Carbon disulfide 0 OE+00 0 OE+00 3 9E-10 9 3E-10
Carbon tetrachloride 4 9E-13 5 9E-13 2 OE-09 2 4E-09
Chlorine 0 OE+00 0 OE+00 1 9E-04 5 7E-04
Chloro-3-methylphenol 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chloroacetonitrile 0 OE+OO 0 OE+00 2 6E-10 4 2E-10
Chloroaniline p-1 7E-15 2 9E-15 6 7E-09 1 1E-08
Chlorobenzene 0 OE+00 0 OE+00 7 8E-10 1 5E-09
Chloroethane 0 OE+00 0 OE+00 3 4E-13 5 5E-13
Chloroform (Trichloromethane) 2 9E-13 3 6E-13 1 5E-09 1 9E-09
Chloroisopropyl ether bis-1 2-0 OE+00 OOE+00 0 OE+00 0 OE+00
Chloronaphthalene 2-0 OE+00 0 OE+00 2 7E-11 4 6E-11
Chlorophenol 2-0 OE+00 0 OE+00 1 9E-09 2 8E-09
Chlorophenyl-phenylether 4-0 OE+00 0 OE+OO 0 OE+00 0 OE+00
Chromium 0 OE+00 0 OE+OO 7 7E-13 9 4E-13
Chrysene 1 5E-14 2 6E-14 0 OE+00 0 OE+00
Cobalt 6 9E-12 1 2E-11 1 5E-06 2 6E-06
Copper 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Cresol m-0 OE+00 0 OE+00 1 8E-10 3 OE-10
Cresol 0-0 OE+00 0 OE+00 2 6E-10 4 4E-10
Crotonaldehyde 0 OE+00 0 OE+00 9 4E-06 1 5E-05
Cumene (Isopropylbenzene) 0 OE+00 0 OE+00 1 4E-11 2 2E-11
Di-n-butyl phthalate 0 OE+00 0 OE+00 1 2E-08 2 1E-08
Di-n-octylphthalate 2 6E-11 4 3E-11 0 OE+OO 0 OE+00
Dibenz(a h)anthracene 2 1E-08 3 5E-08 0 OE+00 0 OE+00
Dibenzofuran 0 OE+00 0 OE+00 0 OE+00 0 OE+OO
Dibromochloromethane 2 4E-14 3 9E-14 1 7E-10 2 7E-10
Dichlorobenzene 1 2-0 OE+00 0 OE+00 3 1E-11 5 1E-11
Dichlorobenzene 1 3-0 OE+00 0 OE+00 1 9E-09 3 OE-09
Dichlorobenzene 1 4-9 1E-15 1 5E 14 1 2E-11 2 OE-11
Dichlorobenzidine 3 3-3 5E-10 5 8E-10 0 OE+00 0 OE+00
Dichlorodifluoromethane 0 OE+00 0 OE+00 1 6E-11 2 6E-11
Dichloroethane 1 1-5 8E-16 9 4E 16 8 4E-12 1 4E-11
Dichloroethane 1 2- (Ethylene Dichloride) 1 6E-14 2 6E-14 3 OE-12 4 9E-12
Dichloroethylene 1 1-0 OE+00 0 OE+00 2 9E-11 4 7E-11
Dichloroethylene cis-1 2-0 OE+00 0 OE+00 9 7E-16 1 6E-15
Dichloroethylene-1 2 (trans) 0 OE+00 0 OE+00 1 6E-10 2 6E-10
Dichiorophenol 2 4-0 OE+OO 0 OE+00 1 5E-09 1 9E-09
Dichloropropane 1 2-4 1E-15 6 7E-15 1 2E-09 2 OE-09
Diethyl phthalate 0 OE+00 0 OE+00 1 1E-12 1 8E-12
Dimethyl phthalate 0 OE+00 0 OE+00 0 OE+00 0 OE+OO
Dimethylphenol 2 4-0 OE+00 0 OE+00 1 4E-09 2 4E-09
Dinitrobenzene 1 3-0 OE+00 0 OE+00 2 4E-08 4 OE-08
Dinitrophenol 2 4-0 OE+00 0 OE+00 4 9E-08 8 3E-08
Dinitrotoluene 2 4-7 3E-14 1 1E-13 3 2E-10 4 8E-10
Dinitrotoluene 2 6-3 3E-15 4 1E-15 5 7E-11 7 OE-11
Dinoseb 0 OE+00 0 OE+00 1 1E-20 1 8E-20
TABLE 29
CHEMICAL-SPECIFIC RISKS
CHILD FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 3 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Dioxane 1 4-2 2E-15 3 7E-15 2 3E-12 3 8E-12
Diphenylamine 0 OE+00 0 OE+00 2 2E-22 3 7E-22
Diphenylhydrazine 1 2-1 8E-13 3 1E-13 0 OE+OO 0 OE+00
Ethyl methacrylate 0 OE+00 0 OE+00 6 6E-11 1 1E-10
Ethyl methanesulfonate 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Ethylbenzene 1 OE-14 1 8E-14 4 8E-11 8 5E-11
Ethylene Dibromide 6 OE-13 9 9E-13 1 3E-09 2 1E-09
Ethylhexyi phthalate bis-2-1 3E-13 2 2E-13 5 5E-09 9 2E-09
Fluoranthene 0 OE+00 0 OE+00 6 OE-10 7 7E-10
Fluorene 0 OE+OO 0 OE+00 8 5E-11 1 1E-10
Formaldehyde 5 2E-13 8 9E-13 4 7E-08 8 2E-08
Freon 113 0 OE+00 0 OE+00 4 5E-13 7 4E-13
Freon 114 0 OE+00 0 OE+00 9 8E-11 1 6E-10
HeptaCDD 1 2 3 4 6 7 8-5 8E-14 1 2E-13 0 OE+00 0 OE+00
HeptaCDF 1 2 3 4 6 7 8-1 3E-11 2 6E-11 0 OE+00 0 OE+00
HeptaCDF 1 2 3 4 7 8 9-1 9E-11 3 8E-11 0 OE+00 0 OE+00
HexaCDD 1 2 3 4 7 8-6 6E-13 9 OE-13 0 OE+00 0 OE+00
HexaCDD 1 2 3 6 7 8-1 8E-12 3 5E-12 0 OE+00 0 OE+00
HexaCDD 1 2 3 7 8 9-8 5E-13 1 4E-12 0 OE+00 0 OE+00
HexaCDF 1 2 3 4 7 8-5 7E-11 1 1E-10 0 OE+00 0 OE+00
HexaCDF 1 2 3 6 7 8-3 6E-11 7 4E-11 0 OE+00 0 OE+00
HexaCDF 1 2 3 7 8 9-4 7E-11 9 6E-11 0 OE+00 0 OE+00
HexaCDF 2346 7 8-4 2E-11 8 9E-11 0 OE+00 0 OE+00
Hexachloro-1 3-butadiene (Perchlorobutadiene) 4 3E-14 7 OE-14 5 1E-11 8 3E-11
Hexachlorobenzene 5 6E-12 1 4E-11 7 8E-09 2 OE-08
Hexachlorocyclopentadiene 0 OE+00 0 OE+00 7 7E-07 1 3E-06
Hexachloroethane (Perchloroethane) 2 8E-15 4 8E-15 4 8E-12 8 OE-12
Hexachloropropene 4 6E-15 6 9E-15 2 8E-10 4 1E-10
Hexane 0 OE+00 0 OE+00 6 5E-10 1 3E-09
Hydrogen chloride 0 OE+OO 0 OE+00 1 2E-07 1 9E-07
lndeno(1 2 3-cd) pyrene 1 9E-12 3 2E-12 0 OE+00 0 OE+00
Isophorone 1 8E-16 3 OE-16 3 8E-12 6 5E-12
Lead 3 3E-15 5 9E-15 2 1E-09 3 9E-09
Manganese 0 OE+00 OOE+00 3 5E-05 8 7E-05
Mercury 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Methacryionitnle 0 OE+00 0 OE+00 8 5E-08 9 8E-08
Methyl Methacrylate 0 OE+00 0 OE+00 2 9E-11 4 8E-11
Methyl bromide (Bromomethane) 0 OE+00 0 OE+00 1 6E-09 2 7E-09
Methyl chloride (Chloromethane) 4 4E-14 7 OE-14 3 2E-09 5 OE-09
Methyl ethyl ketone (2-Butanone) 0 OE+00 0 OE+00 1 8E-11 2 6E-11
Methyl isobutyl ketone 0 OE+00 OOE+00 3 1E-12 5 OE-12
Methyl tert-butyl ether 1 9E-19 3 OE-19 1 8E-12 3 OE-12
Methylene chloride 6 OE-15 8 7E-15 1 3E-10 2 OE-10
N-Nitrosodiethylamine 2 9E-11 4 8E-11 0 OE+00 0 OE+00
N-Nitrosodimethylamine 9 2E-12 1 6E-11 7 7E-10 1 3E-09
N-Nitrosomethylethylamine 3 OE-13 5 OE-13 0 OE+00 0 OE+00
N-Nitrosomorpholine 1 8E-12 3 OE-12 0 OE+00 0 OE+00
N-Nitrosopyrrolidine 4 9E-13 8 2E-13 0 OE+00 0 OE+00
Naphthalene 6 4E-13 1 1E-12 7 3E-08 1 3E-07
Nickel 1 9E-13 3 4E-13 4 6E-08 8 2E-08
Nitroaniline 2-1 OE-16 1 7E-16 4 OE-09 6 8E-09
Nitroaniline 3-6 2E-16 1 IE 15 3 2E-08 5 4E-08
Nitroaniline 4-4 5E-14 7 7E-14 1 6E-08 2 7E-08
TABLE 29
CHEMICAL-SPECIFIC RISKS
CHILD FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 4 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Nitrobenzene 0 OE+00 0 OE+00 4 4E-09 7 3E-09
Nitrophenol 2-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Nitrophenol 4-0 OE+00 0 OE+00 1 OE-07 1 8E-07
Nitroso-di-n-butylamine n-1 1E-12 1 8E-12 0 OE+00 0 OE+00
Nitrosodiphenylamine N-2 2E-16 3 7E-16 0 OE+OO 0 OE+00
Nitrosodipropylamine n-1 3E-12 2 2E-12 0 OE+00 0 OE+00
OctaCDD 1 2 3 4 6 7 8 9-3 9E-15 5 8E 15 0 OE+00 0 OE+00
OctaCDF 1 2 3 4 6 7 8 9-8 8E-14 1 6E 13 0 OE+00 0 OE+00
PentaCDD 1 2 3 7 8-5 OE-11 9 0E 11 0 OE+00 0 OE+00
PentaCDF 1 2 3 7 8-1 8E-11 3 6E-11 0 OE+00 0 OE+00
PentaCDF 2 34 7 8-3 4E-10 7 4E-10 0 OE+00 0 OE+00
Penlachlorobenzene 0 OE+00 0 OE+00 4 7E-09 7 5E-09
Pentachloroethane 0 OE+00 0 OE+00 8 5E-11 1 4E-10
Pentachloronitrobenzene (PCNB) 5 4E-14 9 1E-14 7 8E-10 1 3E-09
Pentachlorophenol 3 5E-11 5 8E-11 1 1E-07 1 9E-07
Perchlorate 0 OE+00 0 OE+OO 0 OE+00 0 OE+00
Phenanthrene 0 OE+00 0 OE+00 2 7E-10 3 7E-10
Phenol 0 OE+00 0 OE+00 2 1E-10 2 9E-10
Phosphorus 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Propanal 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Propylbenzene 2 8E-15 4 8E-15 1 4E-11 2 3E-11
Pyrene 0 OE+00 0 OE+OO 6 6E-10 1 1E-09
Pyridine 0 OE+00 0 OE+00 3 2E-09 5 4E-09
Safrole 0 OE+00 0 OE+OO 0 OE+00 0 OE+00
Selenium 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Silver 0 OE+00 0 OE+00 1 2E-11 2 4E-11
Styrene 0 OE+00 0 OE+00 1 1E-11 1 4E-11
TetraCDD 2 3 7 8-2 7E-11 4 8E-11 2 4E-06 4 3E-06
TetraCDF 2 3 7 8-6 7E-11 1 1E-10 0 OE+00 0 OE+OO
Tetrachlorobenzene 1 2 4 5-0 OE+00 0 OE+00 7 1E-09 1 2E-08
Tetrachloroethane 112 2-2 8E-14 4 6E-14 2 7E-11 4 4E-11
Tetrachloroethylene (Perchloroethylene) 2 2E-14 3 4E-14 1 6E-10 2 5E-10
Tetrachlorophenol 2 3 4 6-0 OE+00 0 OE+00 9 4E-11 1 6E-10
Tetrahydrofuran 2 1E-15 3 3E-15 4 3E-11 6 7E-11
Thallium (1) 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Toluene 0 OE+00 0 OE+00 6 4E-11 1 2E-10
Toluidine o-4 3E-13 7 2E-13 0 OE+00 0 OE+00
Tnchlorobenzene 12 4-1 OE-17 1 7E-17 4 2E-09 6 9E-09
Tnchloroethane 111-0 OE+00 0 OE+00 2 4E-12 3 9E-12
Tnchloroethane 1 1 2-1 3E-14 2 2E-14 2 3E-14 3 7E-14
Trichloroethylene 2 4E-15 3 OE-15 2 4E-11 2 9E-11
Tnchlorofluoromethane (Freon 11) 0 OE+00 0 OE+00 9 OE-12 1 5E-11
Trichlorophenol 2 4 5-0 OE+00 0 OE+OO 8 2E-11 1 4E-10
Trichlorophenol 2 4 6-7 4E-15 9 3E-15 1 4E-09 1 7E-09
Trimethylbenzene 13 5-0 OE+OO 0 OE+OO 4 1E-09 8 1E-09
Tnnitrobenzene 13 5 (sym-) 0 OE+00 0 OE+OO 8 7E-10 1 5E-09
Undecane 0 OE+00 0 OE+00 1 1E-09 2 OE-09
Vinyl Chlonde 5 9E-14 1 2E-13 7 8E-10 1 6E-09
Xylene m-0 OE+00 0 OE+00 2 3E-10 4 4E-10
Xylene o-0 OE+00 0 OE+00 8 8E-11 1 5E-10
Zinc 0 OE+00 0 OE+00 4 6E-13 8 9E-13
bis(2-Chloroethoxv)methane 0 OE+00 0 OE+00 1 9E-09 3 3E-09
o-Tolualdehyde 0 OE+00 0 OE+00 5 9E-10 8 2E-10
TABLE 29
CHEMICAL-SPECIFIC RISKS
CHILD FARMER FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 5 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
p-Dimethylaminoazobenzene 8 4E-09 1 4E-08 0 OE+00 0 OE+00
trans-1,3-Dichloropropene 2 8E-15 4 6E-15 4 OE-10 6 6E-10
Total 1 2E-06 1 9E-06 8 2E-04 1 6E-03
TABLE 30
CHEMICAL-SPECIFIC RISKS
ADULT RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 1 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
1 2 3-Trimethylbenzene 0 OE+00 0 OE+OO 7 9E-10 1 3E-09
1 2 4-Trimethylbenzene 0 OE+00 0 OE+OO 1 3E-08 2 2E-08
1 4-Diethylbenzene 9 5E-15 1 5E-14 8 8E-12 1 4E-11
1 -Chloronaphthalene 0 OE+00 0 OE+00 1 9E-13 3 OE-13
1-Naphthlamine 2 2E-12 3 8E-12 7 2E-10 1 2E-09
2 2 4-Trimethylpentane 0 OE+00 0 OE+00 1 1E-10 1 8E-10
2 2-Dimethylbutane 0 OE+00 0 OE+00 5 8E-11 9 4E-11
2 3 4 -Tnmethylpentane 0 OE+00 0 OE+00 1 9E-11 3 1E-11
2 3-Dimethylbutane 0 OE+00 0 OE+00 1 6E-10 2 7E-10
2 3-Dimethylpentane 0 OE+00 0 OE+00 1 6E-10 3 3E-10
2 4-Dimethylpentane 0 OE+00 0 OE+00 7 3E-11 1 2E-10
2 5-Dimethylbenzaldehyde 0 OE+00 0 OE+00 3 3E-10 5 3E-10
2 6-Dichlorophenol 0 OE+00 0 OE+00 3 4E-10 3 9E-10
2-Acetylaminofluorene 0 OE+00 0 OE+00 2 5E-07 4 1E-07
2-Ethyltoluene 6 4E-15 1 OE-14 6 OE-12 9 8E-12
2-Hexanone 0 OE+00 0 OE+OO 5 8E-11 9 4E-11
2-Methyhexane 0 OE+00 0 OE+00 1 8E-10 3 9E-10
2-Methylnapthalene 0 OE+00 0 OE+00 4 3E-09 7 7E-09
2-Methylpentane 0 OE+00 0 OE+00 5 8E-10 1 2E-09
2-Naphthaylamine 1 5E-10 2 5E-10 2 7E-06 4 5E-06
3 3 -Dimethylbenzidine 5 1E-07 8 6E-07 0 OE+00 0 OE+00
3-Ethyltoluene 4 OE-14 1 1E-13 3 8E-11 9 9E-11
3-Methylhexane 0 OE+00 0 OE+00 3 7E-10 7 9E-10
3-methylheptane 0 OE+00 0 OE+00 1 1E-10 2 2E-10
4 6-Dintro-2-methylphenol 0 OE+00 0 OE+00 2 5E-07 4 2E-07
4-Aminobiphenyl 0 OE+00 0 OE+00 1 6E-07 2 6E-07
4-Ethylloluene 7 6E-14 1 4E-13 7 2E-11 1 3E-10
7 12-Dimethlbenz(a)anthracene 2 6E-11 4 4E-11 0 OE+00 0 OE+00
Acenaphthene 0 OE+00 0 OE+00 3 7E-11 6 2E-11
Acenaphthylene 0 OE+00 0 OE+00 6 3E-11 1 1E-10
Acetaldehyde 1 OE-12 1 7E-12 1 2E-07 2 OE-07
Acetone 0 OE+00 0 OE+00 1 7E-11 3 3E-11
Acetonitnle 0 OE+00 0 OE+00 2 8E-09 4 5E-09
Acetophenone 0 OE+OO 0 OE+00 1 6E-10 2 2E-10
Acrylonitnle 4 2E-12 7 2E-12 7 2E-08 1 2E-07
Aluminum 0 OE+00 0 OE+00 2 6E-04 3 4E-04
Aniline 7 7E-14 1 3E-13 1 1E-07 1 9E-07
Anthracene 0 OE+00 0 OE+00 7 6E-12 1 3E-11
Antimony 0 OE+00 0 OE+00 3 2E-07 6 OE-07
Arsenic 81E-14 9 9E-14 1 5E-09 1 8E-09
Banum 0 OE+00 0 OE+OO 2 3E-09 3 8E-09
Benzaldehyde 0 OE+00 0 OE+00 6 1E-10 8 7E-10
Benzene 2 6E-12 4 4E-12 2 6E-08 4 4E-08
Benzidine 1 1E-06 1 8E-06 3 6E-06 6 1E-06
Benzo(a)anthracene 2 7E-13 4 6E-13 0 OE+00 0 OE+00
Benzo(a)pyrene 3 4E-12 5 7E-12 0 OE+00 0 OE+00
Benzo(b)fluoranthene 7 9E-13 1 3E-12 0 OE+00 0 OE+00
Benzo(g h Operylene 0 OE+00 0 OE+00 3 9E-07 6 5E-07
Benzo(k)fluoranthene 4 3E-13 7 3E-13 0 OE+00 0 OE+00
Benzoic acid 0 OE+00 0 OE+00 9 5E-11 1 3E-10
Benzyl alcohol 0 OE+00 0 OE+00 7 OE-13 1 2E-12
Benzyl chloride 1 6E-13 2 6E-13 7 5E-09 1 2E-08
Beryllium 2 8E-14 4 5E-14 1 3E-09 2 2E-09
TABLE 30
CHEMICAL-SPECIFIC RISKS
ADULT RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 2 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Bis(2-chlorethyl)ether 1 2E-12 2 OE-12 0 OE+00 0 OE+00
Bromodichloromethane 7 9E-14 1 3E-13 1 5E-10 2 4E-10
Bromoform (Tribromomethane) 7 9E-15 1 3E-14 2 4E-10 3 9E-10
Bromophenyl-phenylether 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Butylbenzylphthalate 5 5E-15 9 2E-15 1 3E-11 2 3E-11
Cadmium 5 7E-14 9 4E-14 3 7E-10 6 1E-10
Carbazole 6 7E-11 1 OE-10 0 OE+00 0 OE+00
Carbon disulfide 0 OE+00 0 OE+00 3 9E-10 9 3E-10
Carbon tetrachloride 2 5E-12 2 9E-12 2 OE-09 2 4E-09
Chlonne 0 OE+00 0 OE+00 1 9E-04 5 7E-04
Chloro-3-methylphenol 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chloroacetonitrile 0 OE+00 0 OE+00 2 6E-10 4 2E-10
Chloroaniline p-2 4E-15 4 1E-15 6 6E-09 1 1E-08
Chlorobenzene 0 OE+00 0 OE+00 7 8E-10 1 5E-09
Chloroethane 0 OE+00 0 OE+00 3 4E-13 5 5E-13
Chloroform (Trichloromethane) 1 4E-12 1 8E-12 1 5E-09 1 9E-09
Chloroisopropyl ether bis-1 2-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chloronaphthalene 2-0 OE+00 0 OE+00 2 7E-11 4 6E-11
Chlorophenol 2-0 OE+00 0 OE+00 1 9E-09 2 8E-09
Chlorophenyl-phenylether 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chromium 0 OE+00 0 OE+00 7 7E-13 9 4E-13
Chrysene 3 4E-14 5 8E-14 0 OE+00 0 OE+00
Cobalt 3 4E-11 6 OE-11 1 5E-06 2 6E-06
Copper 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Cresol m-0 OE+00 0 OE+00 1 8E-10 3 OE-10
Cresol 0-0 OE+00 0 OE+00 2 6E-10 4 3E-10
Crotonaldehyde 0 OE+00 0 OE+OO 9 4E-06 1 5E-05
Cumene (Isopropylbenzene) 0 OE+00 0 OE+00 1 4E-11 2 2E-11
Di-n-butyl phthalate 0 OE+00 0 OE+00 4 5E-10 7 5E-10
Di-n-octylphthalate 6 5E-13 1 1E-12 0 OE+00 0 OE+00
Dibenz(a h)anthracene 1 3E-10 2 2E-10 0 OE+00 0 OE+00
Dibenzofuran 0 OE+OO 0 OE+00 0 OE+00 0 OE+00
Dibromochloromethane 1 2E-13 1 9E-13 1 7E-10 2 7E-10
Dichlorobenzene 1,2-0 OE+00 0 OE+00 31E-11 5 1E-11
Dichlorobenzene 1 3-0 OE+00 0 OE+OO 1 8E-09 3 OE-09
Dichlorobenzene 1 4-4 6E-14 7 5E-14 1 2E-11 2 OE-11
Dichlorobenzidine 3 3-2 2E-10 3 7E-10 0 OE+00 0 OE+OO
Dichlorodifluoromethane 0 OE+00 0 OE+00 1 6E-11 2 6E-11
Dichloroethane 1 1-2 9E-15 4 7E-15 8 4E-12 1 4E-11
Dichloroethane 1 2- (Ethylene Dichloride) 8 OE-14 1 3E-13 3 OE-12 4 9E-12
Dichloroethylene 11-0 OE+00 0 OE+00 2 9E-11 4 7E-11
Dichloroethylene cis-1 2-0 OE+00 0 OE+00 2 3E-16 3 8E-16
Dichloroethylene-1 2 (trans) 0 OE+00 0 OE+OO 1 6E-10 2 6E-10
Dichiorophenol 2 4-0 OE+00 0 OE+00 1 4E-09 1 7E-09
Dichloropropane 1 2-2 1E-14 3 4E-14 1 2E-09 2 OE-09
Diethyl phthalate 0 OE+00 0 OE+00 2 2E-13 3 6E-13
Dimethyl phthalate 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Dimethylphenol 2 4-0 OE+OO 0 OE+00 1 4E-09 2 3E-09
Dinitrobenzene 1 3 0 OE+00 0 OE+00 2 3E-08 3 9E-08
Dinitrophenol 2 4-0 OE+00 0 OE+00 4 8E-08 8 2E-08
Dinitrotoluene 2 4-3 OE-13 4 5E 13 7 6E-11 1 1E-10
Dinitrotoluene 2 6-4 1E-15 5 1E-15 1 4E-11 1 7E-11
Dinoseb 0 OE+00 0 OE+00 3 OE-21 5 1E-21
TABLE 30
CHEMICAL-SPECIFIC RISKS
ADULT RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 3 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Dioxane 1 4-1 1E-14 1 8E-14 2 3E-12 3 8E-12
Diphenylamine 0 OE+00 0 OE+00 6 2E-23 1 OE-22
Diphenylhydrazine 1 2-7 5E-13 1 3E-12 0 OE+00 0 OE+00
Ethyl methacrylate 0 OE+00 0 OE+00 6 6E-11 1 1E-10
Ethyl methanesulfonate 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Ethylbenzene 5 2E-14 9 IE 14 4 8E-11 8 5E-11
Ethylene Dibromide 3 OE-12 4 9E-12 1 3E-09 2 1E-09
Ethylhexyi phthalate bis-2-4 9E-14 8 2E-14 41E-10 6 8E-10
Fluoranthene 0 OE+00 0 OE+00 7 8E-11 9 9E-11
Fluorene 0 OE+00 0 OE+00 7 2E-11 9 2E-11
Formaldehyde 2 6E-12 4 5E-12 4 7E-08 8 2E-08
Freon 113 0 OE+00 0 OE+00 4 5E-13 7 4E-13
Freon 114 0 OE+00 0 OE+00 9 8E-11 1 6E-10
HeptaCDD 1 2 3 4 6 7 8-1 4E-15 2 9E-15 0 OE+00 0 OE+00
HeptaCDF 1 2 3 4 6 7 8-1 8E-13 3 5E-13 0 OE+00 0 OE+00
HeptaCDF 1 2 3 4 7 8 9-2 6E-13 51E-13 0 OE+00 0 OE+00
HexaCDD 1 2 3 4 7 8-1 4E-14 1 9E-14 0 OE+OO 0 OE+OO
HexaCDD 1 2 3 6 7 8-2 4E-14 4 6E-14 0 OE+00 0 OE+00
HexaCDD 1 2 3 7 8 9-1 1E-14 1 9E-14 0 OE+00 0 OE+00
HexaCDF 1 2,3 4 7 8-8 2E-13 1 6E 12 0 OE+00 0 OE+00
HexaCDF 1 2 3 6 7 8-5 2E-13 1 1E-12 0 OE+00 0 OE+00
HexaCDF 1 2,3 7 8 9-6 8E-13 1 4E-12 0 OE+00 0 OE+00
HexaCDF 2 3 4 6 7 8-6 1E-13 1 3E-12 0 OE+00 0 OE+OO
Hexachloro-1 3-butadiene (Perchlorobutadiene) 2 1E-13 3 5E-13 5 3E-14 8 8E-14
Hexachlorobenzene 2 4E-11 6 OE-11 7 6E-12 1 9E-11
Hexachlorocyclopentadiene 0 OE+00 0 OE+00 7 7E-07 1 3E-06
Hexachloroethane (Perchloroethane) 1 4E-14 2 4E-14 4 9E-13 8 2E-13
Hexachloropropene 2 1E-14 3 2E-14 3 4E-13 5 1E-13
Hexane 0 OE+00 0 OE+00 6 5E-10 1 3E-09
Hydrogen chloride 0 OE+00 0 OE+00 1 2E-07 1 9E-07
lndeno(1 2 3-cd) pyrene 1 5E-14 2 5E-14 0 OE+00 0 OE+00
Isophorone 8 9E-16 1 5E-15 3 8E-12 6 5E-12
Lead 1 6E-14 3 OE-14 2 1E-09 3 9E-09
Manganese 0 OE+00 0 OE+00 3 5E-05 8 7E-05
Mercury 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Methacryionitnle 0 OE+00 0 OE+00 8 5E-08 9 8E-08
Methyl Methacrylate 0 OE+00 0 OE+00 2 9E-11 4 7E-11
Methyl bromide (Bromomethane) 0 OE+00 0 OE+00 1 6E-09 2 7E-09
Methyl chloride (Chloromethane) 2 2E-13 3 5E-13 3 2E-09 5 OE-09
Methyl ethyl ketone (2-Butanone) 0 OE+00 0 OE+00 1 8E-11 2 6E-11
Methyl isobutyl ketone 0 OE+00 0 OE+00 3 1E-12 5 OE-12
Methyl tert-butyl ether 2 6E-19 4 3E 19 1 8E-12 3 OE-12
Methylene chloride 3 OE-14 4 4E 14 1 3E-10 2 OE-10
N-Nitrosodiethylamine 1 4E-10 2 4E-10 0 OE+00 0 OE+00
N-Nitrosodimethylamine 4 6E-11 7 8E-11 2 2E-10 3 7E-10
N-Nitrosomethylethylamine 4 2E-13 7 1E-13 0 OE+00 0 OE+00
N-Nitrosomorpholine 2 5E-12 4 3E-12 0 OE+OO 0 OE+00
N-Nitrosopyrrolidine 2 1E-12 3 6E-12 0 OE+00 0 OE+OO
Naphthalene 3 2E-12 5 6E-12 7 3E-08 1 3E-07
Nickel 9 4E-13 1 7E-12 4 6E-08 8 2E-08
Nitroaniline 2-1 3E-16 2 1E-16 9 8E-10 1 6E-09
Nitroaniline, 3-8 2E-16 1 4E-15 3 1E-08 5 2E-08
Nitroaniline 4-6 OE-14 1 OE-13 9 8E-09 1 7E-08
TABLE 30
CHEMICAL-SPECIFIC RISKS
ADULT RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 4 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Nitrobenzene 0 OE+00 0 OE+00 4 4E-09 7 3E-09
Nitrophenol 2-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Nitrophenol 4-0 OE+00 0 OE+00 2 6E-08 4 4E-08
Nitroso-di-n-butylamine n-5 3E-12 8 9E-12 0 OE+00 0 OE+OO
Nitrosodiphenylamine N-1 7E-16 2 8E-16 0 OE+00 0 OE+00
Nitrosodipropylamine n-6 6E-12 1 1E-11 0 OE+00 0 OE+OO
OctaCDD 1 2 3 4 6 7 8 9-1 2E-16 1 7E-16 0 OE+00 0 OE+00
OctaCDF 1 2 3 4 6,7 8 9-2 OE-15 3 6E-15 0 OE+00 0 OE+00
PentaCDD 1 2,3 7 8-5 OE-13 9 1E-13 0 OE+00 0 OE+00
PentaCDF 1 2 3 7 8-2 9E-13 5 6E-13 0 OE+00 0 OE+00
PentaCDF 2 3 4 7 8-4 5E-12 9 9E-12 0 OE+00 0 OE+OO
Pentachlorobenzene 0 OE+00 0 OE+00 3 8E-09 6 OE-09
Pentachloroethane 0 OE+00 0 OE+00 8 5E-11 1 4E-10
Pentachloronitrobenzene (PCNB) 2 4E-13 4 1E-13 7 OE-10 1 2E-09
Pentachlorophenol 3 4E-11 5 7E-11 2 1E-08 3 6E-08
Perchlorate 0 OE+OO 0 OE+00 0 OE+00 0 OE+00
Phenanthrene 0 OE+OO 0 OE+00 1 2E-10 1 6E-10
Phenol 0 OE+00 0 OE+00 2 1E-10 2 9E-10
Phosphorus 0 OE+OO 0 OE+OO 0 OE+00 0 OE+00
Propanal 0 OE+00 0 OE+00 0 OE+00 0 OE+OO
Propylbenzene 1 4E-14 2 3E-14 1 3E-11 2 2E-11
Pyrene 0 OE+00 0 OE+00 7 4E-11 1 2E-10
Pyridine 0 OE+00 0 OE+00 3 2E-09 5 4E-09
Safrole 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Selenium 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Silver 0 OE+00 0 OE+00 1 2E-11 2 4E-11
Styrene 0 OE+00 0 OE+00 1 1E-11 1 4E-11
TetraCDD 2 3 7 8-5 5E-13 9 7E-13 3 7E-09 6 5E-09
TetraCDF 2 3 7 8-1 2E-12 2 OE-12 0 OE+00 0 OE+00
Tetrachlorobenzene 1 2 4 5-0 OE+00 0 OE+00 7 OE-09 1 2E-08
Tetrachloroethane 112 2-1 4E-13 2 3E-13 2 7E-11 4 4E-11
Tetrachloroethylene (Perchloroethylene) 1 1E-13 1 7E-13 1 6E-10 2 5E-10
Tetrachlorophenol 2 3 4 6-0 OE+00 0 OE+00 9 1E-11 1 5E-10
Tetrahydrofuran 1 1E-14 1 6E-14 4 3E-11 6 7E-11
Thallium (1) 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Toluene 0 OE+OO 0 OE+00 6 4E-11 1 2E-10
Toluidine o-2 1E-12 3 6E-12 0 OE+00 0 OE+00
Trichlorobenzene 12 4-5 OE-18 8 2E-18 4 2E-09 6 9E-09
Tnchloroethane, 111-0 OE+00 0 OE+00 2 4E-12 3 9E-12
Trichloroethane, 1 1,2-6 6E-14 1 1E-13 5 3E-15 8 7E-15
Tnchloroethylene 1 2E-14 1 5E-14 2 4E-11 2 9E-11
Trichlorofluoromethane (Freon 11) 0 OE+00 0 OE+00 9 OE-12 1 5E-11
Tnchlorophenol 2 4 5-0 OE+00 0 OE+00 6 3E-11 1 1E-10
Tnchlorophenol 2 4 6-3 3E-14 4 1E-14 3 9E-10 4 8E-10
Trimethylbenzene 1 3 5-0 OE+00 0 OE+00 4 1E-09 8 1E-09
Tnnitrobenzene 1 3 5 (sym-) 0 OE+00 0 OE+00 2 9E-10 4 8E-10
Undecane 0 OE+00 0 OE+00 8 5E-10 1 6E-09
Vinyl Chloride 2 9E-13 6 OE-13 7 8E-10 1 6E-09
Xylene m-0 OE+00 0 OE+00 2 3E-10 4 4E-10
Xylene o-0 OE+00 0 OE+00 8 8E-11 1 5E-10
Zinc 0 OE+00 0 OE+00 4 6E-13 8 9E-13
bis(2-Chloroethoxy)methane 0 OE+00 0 OE+00 5 5E-10 9 2E-10
o-Tolualdehyde 0 OE+00 0 OE+00 1 3E-10 1 8E-10
TABLE 30
CHEMICAL-SPECIFIC RISKS
ADULT RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 5 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
p-Dimethylaminoazobenzene 4 8E-11 8 0E-11 0 OE+00 0 OE+OO
trans-1 3-Dichloropropene 1 4E-14 2 3E-14 4 OE-10 6 6E-10
Total 1 6E-06 2 7E-06 5 OE-04 1 OE-03
TABLE 31
CHEMICAL-SPECIFIC RISKS
CHILD RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 1 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
1 2 3-Trimethylbenzene 0 OE+00 0 OE+00 7 9E-10 1 3E-09
1 2 4-Trimethylbenzene 0 OE+00 0 OE+00 1 3E-08 2 2E-08
1 4-Diethylbenzene 1 9E-15 31E-15 8 9E-12 1 4E-11
1 -Chloronaphthalene 0 OE+00 0 OE+00 4 5E-13 7 3E-13
1-Naphthlamine 4 5E-13 7 5E-13 1 6E-09 2 8E-09
2 2 4-Trimethylpentane 0 OE+00 0 OE+00 1 1E-10 1 8E-10
2 2-Dimethylbulane 0 OE+00 0 OE+00 5 8E-11 9 4E-11
2 3 4 -Tnmethylpentane 0 OE+00 0 OE+00 1 9E-11 3 1E-11
2 3-Dimethylbutane 0 OE+00 0 OE+00 1 6E-10 2 7E-10
2 3-Dimethylpentane 0 OE+00 0 OE+00 1 6E-10 3 3E-10
2 4-Dimethylpentane 0 OE+00 0 OE+00 7 3E-11 1 2E-10
2 5-Dimethylbenzaldehyde 0 OE+00 0 OE+00 7 9E-10 1 3E-09
2 6-Dichlorophenol 0 OE+00 0 OE+00 8 2E-10 9 4E-10
2-Acetylaminofluorene 0 OE+00 0 OE+00 5 9E-07 9 9E-07
2-Ethyltoluene 1 3E-15 2 1E-15 6 2E-12 1 OE-11
2-Hexanone 0 OE+00 0 OE+00 5 8E-11 9 4E-11
2-Methyhexane 0 OE+00 0 OE+00 1 8E-10 3 9E-10
2-Methylnapthalene 0 OE+00 0 OE+00 1 OE-08 1 9E-08
2-Methylpentane 0 OE+00 0 OE+00 5 8E-10 1 2E-09
2-Naphthaylamine 3 OE-11 5 OE-11 6 4E-06 1 1E-05
3 3-Dimethylbenzidine 2 4E-07 4 1E-07 0 OE+00 0 OE+00
3-Ethyltoluene 8 1E-15 2 1E-14 3 8E-11 9 9E-11
3-Methylhexane 0 OE+00 0 OE+00 3 7E-10 7 9E-10
3-methylheptane 0 OE+00 0 OE+00 1 1E-10 2 2E-10
4 6-Dintro-2-methvlphenol 0 OE+00 0 OE+OO 61E-07 1 OE-06
4-Aminobiphenyl 0 OE+00 0 OE+00 3 7E-07 6 3E-07
4-Ethyltoluene 1 5E-14 2 8E-14 7 4E-11 1 4E-10
7 12-Dimethlbenz(a)anthracene 1 3E-11 2 1E-11 0 OE+00 0 OE+00
Acenaphthene 0 OE+00 0 OE+00 3 7E-11 6 2E-11
Acenaphthylene 0 OE+00 0 OE+00 9 9E-11 1 7E-10
Acetaldehyde 2 1E-13 3 4E-13 1 2E-07 2 OE-07
Acetone 0 OE+00 0 OE+00 1 7E-11 3 3E-11
Acetonitnle 0 OE+00 0 OE+00 2 8E-09 4 5E-09
Acetophenone 0 OE+00 0 OE+00 1 6E-10 2 2E-10
Acrylonitnle 8 4E-13 1 4E-12 7 2E-08 1 2E-07
Aluminum 0 OE+00 0 OE+00 2 6E-04 3 4E-04
Aniline 1 5E-14 2 6E-14 1 1E-07 1 9E-07
Anthracene 0 OE+00 0 OE+00 7 7E-12 1 3E-11
Antimony 0 OE+00 0 OE+00 3 2E-07 6 OE-07
Arsenic 1 6E-14 2 OE-14 1 5E-09 1 8E-09
Banum 0 OE+00 0 OE+00 2 3E-09 3 8E-09
Benzaldehyde 0 OE+00 0 OE+00 6 1E-10 8 7E-10
Benzene 5 3E-13 8 8E-13 2 6E-08 4 4E-08
Benzidine 5 2E-07 8 8E-07 8 7E-06 1 5E-05
Benzo(a)anthracene 7 4E-14 1 2E-13 0 OE+00 0 OE+00
Benzo(a)pyrene 1 3E-12 2 3E-12 0 OE+00 0 OE+00
Benzo(b)fluoranthene 1 6E-13 2 8E-13 0 OE+00 0 OE+00
Benzo(g h Operylene 0 OE+00 0 OE+00 9 3E-07 1 6E-06
Benzo(k)fluoranthene 1 2E-13 2 OE-13 0 OE+00 0 OE+00
Benzoic acid 0 OE+00 0 OE+00 9 5E-11 1 3E-10
Benzyl alcohol 0 OE+00 0 OE+00 1 7E-12 2 9E-12
Benzyl chlonde 3 1E-14 5 1E-14 7 5E-09 1 2E-08
Beryllium 5 5E-15 9 OE-15 1 3E-09 2 2E-09
TABLE 31
CHEMICAL-SPECIFIC RISKS
CHILD RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 2 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Bis(2-chlorethyl)ether 2 4E-13 4 1E-13 0 OE+00 0 OE+00
Bromodichloromethane 1 6E-14 2 6E-14 1 5E-10 2 4E-10
Bromoform (Tribromomethane) 1 6E-15 2 6E-15 2 4E-10 3 9E-10
Bromophenyl-phenylether 4-0 OE+00 0 OE+OO 0 OE+00 0 OE+00
Butylbenzylphthalate 1 1E-15 1 9E-15 1 5E-11 2 5E-11
Cadmium 1 1E-14 1 9E-14 3 7E-10 61E-10
Carbazole 3 2E-11 5 OE-11 0 OE+00 0 OE+00
Carbon disulfide 0 OE+00 0 OE+00 3 9E-10 9 3E-10
Carbon tetrachloride 4 9E-13 5 9E-13 2 OE-09 2 4E-09
Chlonne 0 OE+00 0 OE+00 1 9E-04 5 7E-04
Chloro-3-methylphenol 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chloroacetonitrile 0 OE+00 0 OE+00 2 6E-10 4 2E-10
Chloroaniline p-1 2E-15 2 OE-15 6 6E-09 1 1E-08
Chiorobenzene 0 OE+00 0 OE+00 7 8E-10 1 5E-09
Chloroethane 0 OE+00 0 OE+00 3 4E-13 5 5E-13
Chloroform (Trichloromethane) 2 9E-13 3 6E-13 1 5E-09 1 9E-09
Chloroisopropyl ether bis-1 2-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chloronaphthalene 2-0 OE+00 0 OE+00 2 7E-11 4 6E-11
Chlorophenol 2-0 OE+00 0 OE+00 1 9E-09 2 8E-09
Chlorophenyl-phenylether, 4-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Chromium 0 OE+00 0 OE+00 7 7E-13 9 4E-13
Chrysene 6 9E-15 1 2E-14 0 OE+00 0 OE+00
Cobalt 6 9E-12 1 2E-11 1 5E-06 2 6E-06
Copper 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Cresol m-0 OE+00 0 OE+00 1 8E-10 3 OE-10
Cresol 0-0 OE+00 0 OE+00 2 6E-10 4 4E-10
Crotonaldehyde 0 OE+00 0 OE+00 9 4E-06 1 5E-05
Cumene (Isopropylbenzene) 0 OE+00 0 OE+00 1 4E-11 2 2E-11
Di-n-butyl phthalate 0 OE+00 0 OE+00 4 7E-10 7 8E-10
Di-n-octylphthalate 3 1E-13 5 2E-13 0 OE+00 0 OE+00
Dibenz(a h)anthracene 6 3E-11 1 1E-10 0 OE+00 0 OE+00
Dibenzofuran 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Dibromochloromethane 2 4E-14 3 9E-14 1 7E-10 2 7E-10
Dichlorobenzene 1 2-0 OE+00 0 OE+00 3 1E-11 5 1E-11
Dichlorobenzene 1 3-0 OE+00 0 OE+00 1 8E-09 3 OE-09
Dichlorobenzene 1 4-9 1E-15 1 5E-14 1 2E-11 2 OE-11
Dichlorobenzidine 3 3-1 OE-10 1 8E 10 0 OE+00 0 OE+00
Dichlorodifiuoromethane 0 OE+00 0 OE+00 1 6E-11 2 6E-11
Dichloroethane 1 1-5 8E-16 9 4E-16 8 4E-12 1 4E-11
Dichloroethane 1 2- (Ethylene Dichlonde) 1 6E-14 2 6E-14 3 OE-12 4 9E-12
Dichloroethylene 11-0 OE+00 0 OE+00 2 9E-11 4 7E-11
Dichloroethylene, cis-1 2-0 OE+00 0 OE+00 5 6E-16 9 1E-16
Dichloroethylene-1 2 (trans) 0 OE+00 0 OE+00 1 6E-10 2 6E-10
Dichiorophenol 2 4-0 OE+00 0 OE+00 1 4E-09 1 8E-09
Dichioropropane 1 2-4 1E-15 6 7E-15 1 2E-09 2 OE-09
Diethyl phthalate 0 OE+00 0 OE+00 5 3E-13 8 7E-13
Dimethyl phthalate 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Dimethylphenol 2 4-0 OE+00 0 OE+00 1 4E-09 2 4E-09
Dinitrobenzene 1 3-0 OE+00 0 OE+00 2 3E-08 3 9E-08
Dinitrophenol 2 4-0 OE+00 0 OE+00 4 9E-08 8 2E-08
Dinitrotoluene 2 4-6 6E-14 9 8E-14 1 8E-10 2 7E-10
Dinitrotoluene 2 6-2 OE-15 2 5E 15 3 4E-11 4 2E-11
Dinoseb 0 OE+00 0 OE+00 7 2E-21 1 2E-20
TABLE 31
CHEMICAL-SPECIFIC RISKS
CHILD RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 3 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Dioxane 1 4-2 2E-15 3 7E-15 2 3E-12 3 8E-12
Diphenylamine 0 OE+00 0 OE+00 1 5E-22 2 5E-22
Diphenylhydrazine 1 2-1 6E-13 2 7E-13 0 OE+00 0 OE+00
Ethyl methacrylate 0 OE+00 0 OE+00 6 6E-11 1 1E-10
Ethyl methanesulfonate 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Ethylbenzene 1 OE-14 1 8E-14 4 8E-11 8 5E-11
Ethylene Dibromide 6 OE-13 9 9E-13 1 3E-09 2 1E-09
Ethylhexyi phthalate bis-2-2 3E-14 3 9E-14 9 8E-10 1 6E-09
Fluoranthene 0 OE+00 0 OE+00 7 8E-11 1 OE-10
Fluorene 0 OE+00 0 OE+00 7 2E-11 9 2E-11
Formaldehyde 5 2E-13 8 9E-13 4 7E-08 8 2E-08
Freon 113 0 OE+00 0 OE+00 4 5E-13 7 4E-13
Freon 114 0 OE+00 0 OE+00 9 8E-11 1 6E-10
HeptaCDD 1 2 3 4 6 7 8-6 5E-16 1 3E-15 0 OE+00 0 OE+00
HeptaCDF 1 2 3 4 6 7 8-8 1E-14 1 6E-13 0 OE+00 0 OE+00
HeptaCDF, 1,2,3 4 7 8 9-1 2E-13 2 3E-13 0 OE+00 0 OE+00
HexaCDD 1,2 347 8-61E-15 8 3E-15 0 OE+00 0 OE+00
HexaCDD 1,2 3 67 8-1 OE-14 2 OE-14 0 OE+00 0 OE+00
HexaCDD 1 2 3 7 8 9-4 9E-15 8 1E-15 0 OE+00 0 OE+00
HexaCDF 1 2 3 4 7 8-3 OE-13 6 OE-13 0 OE+00 0 OE+00
HexaCDF 1 2 3 6 7 8-1 9E-13 4 OE-13 0 OE+00 0 OE+00
HexaCDF 1 2 3 7 8 9-2 5E-13 5 1E-13 0 OE+00 0 OE+00
HexaCDF 2 346 7,8-2 3E-13 4 8E-13 0 OE+00 0 OE+00
Hexachloro-1,3-butadiene (Perchlorobutadiene) 4 2E-14 6 9E-14 1 3E-13 2 1E-13
Hexachlorobenzene 4 7E-12 1 2E-11 1 8E-11 4 6E-11
Hexachlorocyclopentadiene 0 OE+00 0 OE+00 7 7E-07 1 3E-06
Hexachloroethane (Perchloroethane) 2 8E-15 4 8E-15 1 2E-12 2 OE-12
Hexachloropropene 4 3E-15 6 4E-15 8 2E-13 1 2E-12
Hexane 0 OE+00 0 OE+00 6 5E-10 1 3E-09
Hydrogen chloride 0 OE+00 0 OE+00 1 2E-07 1 9E-07
lndeno(1 2 3-cd) pyrene 6 6E-15 1 1E-14 0 OE+00 0 OE+00
Isophorone 1 8E-16 3 OE-16 3 8E-12 6 5E-12
Lead 3 3E-15 5 9E-15 2 1E-09 3 9E-09
Manganese 0 OE+00 0 OE+00 3 5E-05 8 7E-05
Mercury 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Methacryionitnle 0 OE+00 0 OE+00 8 5E-08 9 8E-08
Methyl Methacrylate 0 OE+00 0 OE+00 2 9E-11 4 8E-11
Methyl bromide (Bromomethane) 0 OE+00 0 OE+00 1 6E-09 2 7E-09
Methyl chloride (Chloromethane) 4 4E-14 7 OE-14 3 2E-09 5 OE-09
Methyl ethyl ketone (2-Butanone) 0 OE+00 0 OE+00 1 8E-11 2 6E-11
Methyl isobutyl ketone 0 OE+00 0 OE+00 3 1E-12 5 OE-12
Methyl tert-butyl ether 1 3E-19 2 1E-19 1 8E-12 3 OE-12
Methylene chloride 6 OE-15 8 7E-15 1 3E-10 2 OE-10
N-Nitrosodiethylamine 2 9E-11 4 8E-11 0 OE+00 0 OE+00
N-Nitrosodimethylamine 9 2E-12 1 6E-11 5 3E-10 8 9E-10
N-Nitrosomethylethylamine 2 OE-13 3 4E-13 0 OE+00 0 OE+00
N-Nitrosomorpholine 1 2E-12 2 1E-12 0 OE+00 0 OE+00
N-Nitrosopyrrolidine 4 6E-13 7 7E-13 0 OE+00 0 OE+00
Naphthalene 6 4E-13 1 1E-12 7 3E-08 1 3E-07
Nickel 1 9E-13 3 4E-13 4 6E-08 8 2E-08
Nitroaniline 2-6 1E-17 1 OE-16 2 4E-09 4 OE-09
Nitroaniline 3-4 OE-16 6 7E-16 3 1E-08 5 3E-08
Nitroaniline 4-2 9E-14 4 9E-14 1 3E-08 2 2E-08
TABLE 31
CHEMICAL-SPECIFIC RISKS
CHILD RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 4 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
Nitrobenzene 0 OE+00 0 OE+00 4 4E-09 7 3E-09
Nitrophenol 2-0 OE+00 0 OE+00 0 OE+00 0 OE+00
Nitrophenoi 4-0 OE+00 0 OE+00 6 1E-08 1 OE-07
Nitroso-di-n-butylamine n-1 1E-12 1 8E 12 0 OE+00 0 OE+00
Nitrosodiphenylamine N-8 OE-17 1 4E-16 0 OE+00 0 OE+00
Nitrosodipropylamine, n-1 3E-12 2 2E-12 0 OE+00 0 OE+00
OctaCDD 1,2 3 46 7,8 9-5 4E-17 8 OE-17 0 OE+00 0 OE+OO
OctaCDF 1 2 3 4 6 7 8 9-9 6E-16 1 7E-15 0 OE+00 0 OE+00
PentaCDD 1 2 3 7 8-2 OE-13 3 6E-13 0 OE+00 0 OE+00
PentaCDF 1 2 3 7 8-9 6E-14 1 9E-13 0 OE+00 0 OE+00
PentaCDF 2,3 4 7 8-1 5E-12 3 3E-12 0 OE+00 0 OE+00
Pentachlorobenzene 0 OE+00 0 OE+00 3 8E-09 6 OE-09
Pentachloroethane 0 OE+00 0 OE+00 8 5E-11 1 4E-10
Pentachloronitrobenzene (PCNB) 4 9E-14 8 2E-14 7 OE-10 1 2E-09
Pentachlorophenol 1 6E-11 2 7E-11 5 2E-08 8 7E-08
Perchlorate 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Phenanthrene 0 OE+OO 0 OE+00 1 2E-10 1 6E-10
Phenol 0 OE+00 0 OE+00 2 1E-10 2 9E-10
Phosphorus 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Propanal 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Propylbenzene 2 8E-15 4 7E-15 1 3E-11 2 2E-11
Pyrene 0 OE+00 0 OE+00 7 5E-11 1 3E-10
Pyridine 0 OE+00 0 OE+00 3 2E-09 5 4E-09
Safrole 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Selenium 0 OE+00 0 OE+OO 0 OE+00 0 OE+00
Silver 0 OE+00 0 OE+00 1 2E-11 2 4E-11
Styrene 0 OE+00 0 OE+00 1 1E-11 1 4E-11
TetraCDD 2 3 7 8-1 7E-13 3 OE-13 8 9E-09 1 6E-08
TetraCDF 2,3 7 8-3 5E-13 5 8E 13 0 OE+00 0 OE+OO
Tetrachlorobenzene 1 2 4 5-0 OE+00 0 OE+OO 7 OE-09 1 2E-08
Tetrachloroethane 1,12 2-2 8E-14 4 6E-14 2 7E-11 4 4E-11
Tetrachloroethylene (Perchloroethylene) 2 2E-14 3 4E-14 1 6E-10 2 5E-10
Tetrachlorophenol 2 3 4 6-0 OE+00 0 OE+00 9 2E-11 1 6E-10
Tetrahydrofuran 2 1E-15 3 3E-15 4 3E-11 6 7E-11
Thallium (1) 0 OE+OO 0 OE+00 0 OE+00 0 OE+OO
Toluene 0 OE+00 0 OE+00 6 4E-11 1 2E-10
Toluidine o-4 3E-13 7 2E-13 0 OE+00 0 OE+00
Tnchlorobenzene 1,2 4-2 4E-18 3 9E-18 4 2E-09 6 9E-09
Trichioroethane 111-0 OE+00 0 OE+00 2 4E-12 3 9E-12
Tnchloroethane 1,1 2-1 3E-14 2 2E-14 1 3E-14 2 1E-14
Trichloroethylene 2 4E-15 3 OE-15 2 4E-11 2 9E-11
Trichlorofluoromethane (Freon 11) 0 OE+00 0 OE+00 9 OE-12 1 5E-11
Tnchlorophenol 2 4 5-0 OE+00 0 OE+00 7 2E-11 1 2E-10
Tnchlorophenol 2 4 6-7 OE-15 8 8E-15 9 3E-10 1 2E-09
Tnmethyi benzene 1,3,5-0 OE+00 0 OE+00 4 1E-09 8 1E-09
Trinitrobenzene 13 5 (sym-) 0 OE+00 0 OE+00 5 9E-10 1 OE-09
Undecane 0 OE+00 0 OE+00 8 5E-10 1 6E-09
Vinyl Chloride 5 9E-14 1 2E-13 7 8E-10 1 6E-09
Xylene m-0 OE+00 0 OE+00 2 3E-10 4 4E-10
Xylene o-0 OE+00 0 OE+00 8 8E-11 1 5E-10
Zinc 0 OE+00 0 OE+00 4 6E-13 8 9E-13
bis(2-Chloroethoxy)methane 0 OE+00 0 OE+00 1 3E-09 2 2E-09
o-Tolualdehyde 0 OE+00 0 OE+00 3 1E-10 4 3E-10
TABLE 31
CHEMICAL-SPECIFIC RISKS
CHILD RESIDENT FROM SOURCE 225A (OPEN BURNING)
AT M225 ON-SITE MAXIMUM GASEOUS LOCATION
THIOKOL PROPULSION, INC
BRIGHAM CITY, UTAH
PAGE 5 OF 5
Chemical
Total Cancer Risk Total Hazard Quotient
Chemical Average Maximum Average Maximum
p-Dimethylaminoazobenzene 2 3E-11 3 9E-11 0 OE+00 0 OE+00
trans-1 3-Dichloropropene 2 8E-15 4 6E-15 4 OE-10 6 6E-10
Total 7 7E-07 1 3E-06 5 1E-04 1 OE-03
TABLE 32
COMPARISON OF TOTAL ONE HOUR AIR CONCENTRATIONS (ug/m') TO UDAQ TOXIC SCREENING LEVELS AVERAGE EMISSION RATES
THIOKOL PROULSION INC
BRIGHMAN CITY UTAH
Chemical
Chronic/
Carcinogenic
Toxic
Screening
Level (1)
Adams
Ranch Autoliv Blue Creek Boundary #1 Boundary #: ! Boundary #: Boundary #' Chnstensen
Ranch
Holmgren
Ranch Pond Howe Dairy Thiokol
Ranch Pond
M 136
Offsite
Maximum
Gaseous
M 136
Offsite
Maximum
Particulate
M 225
Offsite
Maximum
Gaseous
M 225
Offsite
Maximum
Particulate
M 136
Onsite
Maximum
Gaseous
M 136
Onsite
Maximum
Particulate
M 225
Onsite
Maximum
Gaseous
M225
Onsite
Maximum
Particulate
2 Methylnapthaiene 2 90E+02 8 2E05 1 SE 09 BOE 05 1 1E04 9 0E 05 5 3E04 2 BE 04 4 9E-05 2 BE 04 2 BE 05 7 BE 06 1 3E04 1 3E04 2 6E 03 0 OE+00 1 0EO4 1 0E04 1 3E03 31 E-06
Acetone 1 1SE+05 8 IE 04 1 8E 08 7 9E04 1 IE 03 B9E-04 5 2E03 2 6E-03 4 9E 04 2 BE 03 2 BE 04 7 8E05 1 3E03 1 3E-03 2 6E 02 0 OE+00 1 OE 03 1 OE 03 1 BE 02 3 IE 05
Acetonitnle 3 35E+03 2 6E04 5 BE 09 2 5E 04 3 4E 04 2 9E04 1 7E 03 B4E04 1 BE 04 8 9E-04 B9E05 2 5E05 4 IE 04 4 IE 04 8 3E03 0 OE+00 3 2E04 3 2E 04 4 3E03 9 9E-06
Acetophenone 4 90E+03 BOE 05 2 0E09 8 7E 05 1 2E 04 9 8E05 5 8E 04 2 9E04 5 4E 05 3 IE 04 31 E-05 8 6E06 1 4E 04 1 4E 04 2 9E 03 0 OE+OO 1 IE 04 1 IE 04 1 5E03 3 4E-06
Acrylonitnle 4 33E+02 2 3E04 5 IE 09 2 2E04 2 9E 04 2 5E-04 1 5E03 7 3E04 1 4E 04 7 8E04 7 BE 05 2 2E05 3 BE 04 3 6E-04 7 3E03 0 OE+OO 2 BE 04 2 8E-04 3 7E 03 S7E-06
Aluminum 1 OOE+02 2 OE+00 4 5E05 2 OE+00 2 BE+OO 2 2E+00 1 3E+01 6 BE+OO 1 2E+00 7 OE+OO 7 0E01 2 0E-01 3 2E+00 3 2E+00 6 5E+01 0 OE+OO 2 5E+00 2 5E+00 3 3E+01 7 7E-02
Aniline 7 60E+02 1 BE-04 3 9E09 1 7E 04 2 3E04 1 9E04 1 IE 03 5 7E 04 1 IE 04 6 OE 04 6 OE-05 1 7E-05 2 BE 04 2 BE 04 5 6E03 0 OE+OO 2 2E-04 2 2E-04 2 9E03 6 7E 06
Antimony 5 OOE+01 7 1E 04 1 6E08 6 9E04 9 2E 04 7 8E 04 4 6E03 2 3E03 4 3E04 2 4E 03 2 4E04 6 BE 05 1 1E03 1 IE 03 2 3E02 0 OE+OO B7E 04 8 7E 04 1 2E-02 2 7E-05
Arsenic 1 OOE+OO 4 3E06 1 5E 10 4 BE 06 B9E-08 5 2E06 4 4E05 1 9E-05 2 2E 06 1 9E-05 1 3E 06 2 4E06 5 5E 06 5 5E06 2 3E06 6 1E-05 7 8E06 7 BE 06 1 2E06 3 9E04
Banum 5OOE+01 7 7E-05 2 7E 09 B2E-05 2 4E-06 9 2E05 7 BE-04 3 4E 04 4 0E 05 3 5E 04 2 2E 05 4 3E05 9 9E 05 9 9E 05 6 0E 05 1 IE 03 1 4E 04 1 4E04 3 2E 05 6 9E03
Benzene 1 59E+02 1 2E 03 2 BE 08 1 2E03 1 6E03 1 4E 03 8 OEOB 4 OEOB 7 5E 04 4 2E-03 4 2E 04 1 2E04 2 OEOB 2 0E03 4 0E 02 OOE+00 1 5E 03 1 5E03 2 0E02 4 7E05
Beryllium 2 OOE 01 1 BE-06 6 IE 11 1 9E06 5 5E-08 21E06 1 8E-05 7 BE-06 9 2E 07 7 9E-06 5 IE 07 9 9E-07 2 3E-06 2 3E06 1 4E 06 2 5E 05 3 2E0B 3 2E0B 7 4E07 1 6E 04
Cadmium 1 OOE+OO 4 9E06 1 7E 10 5 2E 06 1 5E07 5 9E-06 5 0E 05 2 2E 05 2 6E-06 2 2E05 1 4E-06 2 7E-06 6 3E 06 6 3E06 3 8E06 6 9E 05 B9E0B B9E-06 2 1E06 4 4E 04
Carbon disulfide 311E+02 4 3E-04 9 5E09 4 2E04 5 5E-04 4 7E 04 2BE-03 1 4E 03 2 6E-04 1 5E03 1 5E 04 4 1E05 6 BE-04 6 8E04 1 4E 02 0 OE+00 5 2E-04 5 2E 04 7 OEOB 1 BE 05
Carbon tetrachloride 314E+03 6 0E 04 1 BEOS 5 9E04 7 BE 04 6 6E04 3 9E-03 1 9E-03 3 6E-04 2 IE 03 2 IE 04 5 BE 05 9 6E-04 9 6E-04 1 9E-02 0 OE+OO 7 4E 04 7 4E 04 9 9E 03 2 BE 05
Chlorobenzene 4 59E+03 6 2E05 1 4E 09 6 0E05 BOE 05 6 BE 05 4 0E 04 2 0E04 3 7E 05 2 1E04 2 1 E-05 5 9E06 9 BE 05 9 BE 05 2 OEOB 0 OE+OO 7 5E 05 7 5E-05 1 OE-03 2 3E 06
Chromium 5 OOE+01 2 7E-04 9 4E-09 2 8E-04 8 3E 06 3 2E04 2 7E-03 1 2E 03 1 4E 04 1 2E03 7 BE 05 1 5E 04 3 4E04 3 4E-04 2 1E 04 3 8E-03 4 9E-04 4 9E04 1 IE 04 2 4E 02
Cobalt 2 OOE+00 1 4E-05 3 IE 10 1 4E 05 1 BE 05 1 5E-05 9 IE 05 4 5E-05 B5E 06 4 8E05 4SE-06 1 3E06 2 2E-05 2 2E05 4 5E 04 0 OE+00 1 7E05 1 7E 05 2 BE 04 5 4E 07
Copper 1 OOE+02 2 4E 04 B5E09 2 6E04 0 OE+00 2 9E04 2 5E 03 1 IE 03 1 3E04 1 1E-03 7 OE-05 1 4E 04 3 IE 04 3 1E04 3 3E06 3 5E03 4 4E 04 4 4E04 6 6E-06 2 2E 02
Dichlorobenzene 1 2 6 OOE+03 9BE-0B 2 2E 10 9 6E-06 1 3E-05 1 1E-05 6 3E 05 3 2E05 5 9E-06 3 4E-05 3 4E 06 9 4E 07 1 6E-05 1 6E-05 31E-04 0 OE+00 1 2E-05 1 2E 05 1 6E04 3 7E 07
Dichloroethane 1 1 4 04E+04 6 6E06 1 5E 10 6 5E 06 BBE 06 7 3E0B 4 3E05 2 IE 05 4 0E 06 2 3E 05 2 3E06 6 3E-07 1 1E-05 1 IE 05 2 IE 04 0 OE+00 8 IE 06 8 IE 06 1 IE 04 2 5E 07
Dichloroethylene cis 1 2 7 91E+04 9 5E06 2 IE 10 9 3E06 1 2E05 1 OE 05 6 2E05 3 IE 05 5 BE 06 3 3E-05 3 3E0B 9 IE 07 1 5E 05 1 5E05 3 IE 04 0 OE+OO 1 2E-05 1 2E 05 1 BE-04 3 6E-07
Dichloroethylene 1 2 (trans) 7 91E+04 1 5E-05 3 4E 10 1 5E-05 2 0E05 1 7E 05 9 BE 05 4 9E-05 9 2E 06 5 2E-05 5 2E 06 1 5E 06 2 4E05 2 4E-05 4 9E-04 0 OE+00 1 9E 05 1 9E 05 2 5E 04 5 BE 07
Diethyl phthalate 5 OOE+02 1 BE 05 40E 10 1 BE-05 2 3E-05 2 0E05 1 2E-04 5 8E05 1 IE 05 6 2E05 6 2E-06 1 7E06 2 9E05 2 9E05 5 8E04 0 OE+OO 2 2E05 2 2E 05 3 OE-04 6 9E-07
Dimethyl phthalate 5 OOE+02 1 2E05 2 7E 10 1 2E 05 1 6E 05 1 3E 05 7SE 05 3 9E 05 7 3E06 4 IE 05 4 1 E-06 1 2E 06 1 9E05 1 9E-05 3 9E 04 0 OE+00 1 5E05 1 5E-05 2 0E04 4 6E-07
Diphenylamine 1 OOE+03 1 2E-05 2 7E 10 1 2E 05 1 6E 05 1 3E-05 7SE05 3 9E-05 7 3E-06 4 1 E-05 4 1 E-06 1 2E 06 1 9E05 1 9E 05 3 9E-04 0 OE+00 1 5E 05 1 5E 05 2 0E 04 4BE-07
Ethylbenzene 4 33E+04 7 6E05 1 7E-09 7 4E 05 9 8E05 8 4E 05 4 9E-04 2 5E 04 4 6E05 2 BE-04 2 6E 05 7 3E06 1 2E04 1 2E-04 2 4E-03 0 OE+OO 9 BE 05 9 BE 05 1 3E-03 2 9E-06
Hexachlorobenzene 2 OOE-01 1 9E 04 4 2E 09 1 BE 04 2 4E04 2 IE 04 1 2E-03 B1E-04 1 IE 04 6 4E-04 B4E-05 1 BE 05 BOE 04 3 OE-04 6 OEOB 0 OE+OO 2 3E04 2 3E04 3 IE 03 7 2E-06
Hexachlorocyclopentadiene 1 OOE+OO 2 4E 04 5 4E 09 2 4E-04 3 IE 04 2 7E 04 1 6E 03 7 BE 04 1 5E 04 S3E04 8 3E05 2 3E05 3 8E-04 BBE 04 7 8E03 0 OE+00 BOE 04 3 OE-04 4 OE-03 9 2E 06
Hexane 1 76E+05 2 0E 04 4 5E 09 2 0E04 2 BE 04 2 2E 04 1 3E03 BBE 04 1 2E 04 7 0E04 7 OE-05 2 OE-05 3 2E-04 3 2E04 6 5E03 0 OE+OO 2 5E04 2 5E 04 BBE 03 7 7E-06
Lead 5 OOE+00 2 7E-04 9 4E 09 2 9E-04 B5E 06 3 2E-04 2BE-03 1 2E-03 1 4E-04 1 2E-03 7 9E 05 1 5E 04 3 5E 04 3 5E04 1 7E 04 3 BE 03 4 9E-04 4 9E04 9 0E 05 2 4E 02
Manganese 2 OOE+01 2 7E03 B 1E-0B 2 7E 03 3 5E-03 3 0E 03 1 BE-02 BBE-03 1 6E03 9 3E-03 9 3E-04 2 6E-04 4 3E03 4 3E03 8 7E-02 0 OE+00 3 3E-03 3 3E03 4 5E 02 1 OE 04
Mercury 2 50E+00 1 7E 06 23E 11 1 7E 06 2 3E0B 1 9E 06 1 IE 05 5 6E06 1 1E-06 BOE 06 BOE 07 1 7E07 2SE06 2 BE 06 5 6E05 0 OE+OO 2 IE 06 2 1E06 2 9E-05 BBE 08
Methacryionitnle 2 74E+02 9 4E05 2 IE 09 9 2E 05 1 2E-04 1 0E04 6 0E04 3 OE-04 5 7E05 3 2E04 3 2E-05 9 0E 06 1 5E 04 1 5E-04 3 OE-03 0 OE+00 1 1E04 1 1E-04 1 5E 03 3 6E 06
Methyl Methacrylate 2 04E+04 3 2E 05 7 2E 10 3 2E05 4 2E 05 3 6E 05 2 IE 04 1 OE-04 2 OE-05 1 1E04 1 IE 05 3 1E-06 5 IE 05 5 IE 05 1 OEOB 0 OE+OO 4 0E05 4 OE-05 5 3E04 1 2E 06
Naphthalene 5 23E+03 3 4E 04 7 6E 09 3 4E 04 4 4E 04 3 BE 04 2 2E03 1 1E-03 2 1E-04 1 2E-03 1 2E04 3 3E-05 5 5E 04 5 5E04 1 1E-02 0 OE+OO 4 2E 04 4 2E 04 5 6E 03 1 3E-05
Nickel 1 50E+02 6 0E04 2 IE 08 6 3E-04 1 9E05 7 2E04 6 1E-03 2 7E 03 3 1E 04 2 7E 03 1 BE 04 3 4E 04 7 7E 04 7 7E-04 4 7E04 B4E 03 1 IE 03 1 1E03 2 5E 04 5 4E 02
Nitrobenzene 5 02E+02 1 4E 05 3 1E 10 1 3E-05 1 8E-05 1 5E 05 8 9E 05 4 4E 05 B3E0B 4 7E 05 4 7E06 1 3E06 2 2E-05 2 2E05 4 4E 04 0 OE+00 1 7E 05 1 7E-05 2 3E04 5 2E07
Pentachlorophenol 5 OOE+01 6 OE-04 1 3E 08 5 9E-04 7 8E04 6 6E 04 3 9E03 1 9E03 3 6E-04 2 1E03 2 IE 04 5 BE 05 9 6E04 9 6E04 1 9E 02 0 OE+00 7 4E04 7 4E 04 9 9E-03 2 3E-05
Phenol 1 92E+03 6 6E 05 1 5E-09 6 4E 05 8 5E05 7 2E05 4 2E-04 21E04 4 0E05 2 2E-04 2 2E05 6 3E 06 1 OE-04 1 0E04 2 1E-03 0 OE+00 8 OE-05 BOE 05 1 1E-03 2 5E-0B
Phosphorus 1 OOE+01 1 SE 03 6 5E 08 2 OEOB 0 OE+00 2 2E 03 1 9E-02 8 2E 03 9 6E-04 8 4E 03 5 4E 04 1 IE 03 2 3E 03 2 3E03 2 6E05 2 6E02 3 4E 03 3 4E-03 5 0E05 1 7E 01
Pyndine 3 23E+02 1 8E-05 4 0E 10 1 7E-05 2 3E05 2 0E 05 1 2E-04 5 BE 05 1 1E-05 B1E05 6 IE 06 1 7E06 2 BE 05 2 BE 05 5 7E04 0 OE+00 2 2E05 2 2E05 2 9E04 BBE-07
Selenium 2 OOE+01 2 5E05 8 9E 10 2 7E-05 0 OE+00 3 OE-05 2 6E 04 1 1E04 1 3E05 1 IE 04 7 3E06 1 4E 05 3 2E 05 3 2E-05 3 5E07 3 6E-04 4 6E-05 4 6E05 6 9E 07 2 3E 03
Sliver 1 OOE+01 1 4E05 48E 10 1 5E05 4 3E-07 1 7E 05 1 4E 04 6 2E-05 7 2E-06 6 2E 05 4 0E 06 7 8E-06 1 8E05 1 BE 05 1 1E-05 1 9E-04 2 5E-05 2 5E05 5 BE-06 1 2E 03
Styrene 8 50E+03 1 8E05 3 9E 10 1 7E05 2 3E 05 1 9E-05 1 1E-04 5 7E 05 1 IE 05 BOE 05 6 OE-06 1 7E-06 2 BE 05 2 BE 05 5 6E-04 0 OE+00 2 2E-05 2 2E-05 2 9E 04 B7E07
Tetrahydrofuran 1 47E+04 2 1E05 4 6E 10 2 OE-05 2 7E-05 2 3E05 1 3E-04 6 6E-05 1 2E05 7 0E 05 7 OEOB 2 OE-06 3 3E05 BBE 05 6 6E04 0 OE+OO 2 5E 05 2 5E-05 3 4E 04 7BE-07
Thallium 1 OOE+01 3 4E05 1 2E 09 3 6E-05 1 IE 06 4 IE 05 3 5E 04 1 5E 04 1 BE-05 1 5E-04 1 OE-05 1 9E-05 4 4E-05 4 4E-05 2 7E 05 4 8E04 6 2E05 6 2E05 1 4E 05 3 1E03
Toluene 7 52E+03 51E04 1 IE OS 4 9E04 6 5E04 5 6E-04 3 3E-03 1 6E 03 3 IE 04 1 7E03 1 7E 04 4 8E-05 8 OE-04 8 OE-04 1 6E-02 0 OE+OO 6 2E 04 6 2E 04 BSE 03 1 9E 05
Vinyl Chlonde 2 55E+02 1 2E 04 2 7E-09 1 2E04 1 6E-04 1 4E 04 8 0E04 4 0E 04 7 4E05 4 2E-04 4 2E 05 1 2E05 2 0E04 2 0E04 3 9E-03 0 OE+00 1 5E 04 1 5E 04 2 0E 03 4 7E06
Xylene o 4 33E+04 9 7E-05 2 2E09 9 5E 05 1 3E04 1 IE 04 6 3E-04 31E-04 5 9E-05 3 3E04 3 3E-05 9 3E-06 1 5E 04 1 5E 04 3 IE 03 0 OE+00 1 2E04 1 2E04 1 6E-03 3 7E 06
Zinc 2 OOE+02 1 8E04 6 3E09 1 9E04 5 OE-06 2 2E04 1 BE 03 8 IE 04 9 5E 05 8 2E04 5 3E 05 1 0E04 2 3E 04 2 3E04 1 3E-04 2 5E 03 3 BE 04 BBE 04 6 BE 05 1 BE-02
trans 1 3 Dichloropropene 4 53E+02 1 3E-05 2SE 10 1 2E 05 1 6E05 1 4E-05 8 2E 05 4 IE 05 7 7E 06 4 3E05 4 3E0B 1 2E06 2 0E05 2 OE-05 41E04 0 OE+OO 1 6E05 1 6E05 2 IE 04 4 BE 07
Notes
1 Acute Toxic Screening Level = ACGIH TLV divided by 10
ACGIH TLVs from 2003 TLVs and BEls for Chemical Substances and Physical Agents Amencan Council of Government Industnal Hygienists (ACGIH)
Shading indicates that Toxic Screening Level was exceeded
NA No value available
TABLE 33
COMPARISON OF TOTAL ONE HOUR AIR CONCENTRATIONS (ug/m') TO UDAQ TOXIC SCREENING LEVELS MAXIMUM EMISSION RATES
THIOKOL PROULSION INC
BRIGHMAN CITY UTAH
Chemical
Chronic/
Carcinogenic
Toxic
Screening
Level (1)
Adams
Ranch Autoliv Blue Creek Boundary # Boundary #. 2 Boundary #. 3 Boundary # J Chnstensen
Ranch
Holmgren
Ranch Pond Howe Dairy Thiokol
Ranch Pone
M 136
Offsite
Maximum
Gaseous
M 136
Offsite
Maximum
Particulate
M 225
Offsite
Maximum
Gaseous
M 225
Offsite
Maximum
Particulate
M 136
Onsite
Maximum
Gaseous
M 136
Onsite
Maximum
Particulate
M 225
Onsite
Maximum
Gaseous
M 225
Onsite
Maximum
Particulate
2 Methylnapthaiene 2 90E+02 1 5E 04 3 0E04 1 4E-04 1 9E-04 1 6E-04 9 5E04 4 7E 04 8 9E05 5 0E04 5 0E05 1 4E 05 2SE-04 2SE-04 4 7E OS 0 OE+OO 1 BE 04 1 BE 04 2 4E 03 S6E0B
Acetone 1 18E+05 1 BE 03 3 2E 03 1 6E-03 2 IE-OS 1 7E-03 1 0E02 5 IE 03 9 6E04 5 4E 03 5 4E-04 1 5E 04 2 5E 03 2 5E-03 5 IE 02 0 OE+00 1 9E-0S 1 9E03 2 BE 02 6 0E-0S
Acetonitnle 3 35E+03 4 3E04 8 7E-04 4 2E04 5 BE 04 4 7E 04 2 8E03 1 4E-0S 2 6E04 1 5E 03 1 5E 04 41 E-05 6SE04 BSE 04 1 4E 02 0 OE+00 5 3E04 5 BE 04 7 OEOB 1 6E05
Acetophenone 4 90E+03 1 2E 04 2 5E 04 1 2E 04 1 6E04 1 4E 04 SOE 04 4 OE-04 7 5E-05 4 2E-04 4 2E 05 1 2E 05 2 0E04 2 0E04 4 0E OS 0 OE+00 1 SE 04 1 SE-04 2 OE-OB 4 7E-06
Acrylonitnle 4 33E+02 3 9E 04 7 8E 04 3 8E04 BOE 04 4 3E 04 2 5E-03 1 2E-03 2 3E04 1 3E-03 1 BE 04 3 7E 05 6 2E-04 6 2E 04 1 2E 02 0 OE+OO 4 8E04 4 BE 04 6 4E-03 1 5E 05
Aluminum 1 OOE+02 2 7E+00 5 4E+00 2 BE+OO 3 4E+00 2 9E+00 1 7E+01 8 6E+00 1 6E+00 9 1E+00 9 1E01 2 5E01 4 2E+00 4 2E+00 8 5E+01 0 OE+OO 3 BE+OO B 3E+00 4 4E+01 1 OE-01
Aniline 7 60E+02 3 0E04 BOE 04 2 9E04 3 9E-04 3 3E-04 1 9E03 9 6E04 1 BE 04 1 OEOB 1 OE 04 2 9E-05 4 7E 04 4 7E-04 9 5E-03 0 OE+OO 3 6E04 S6E04 4 9E 03 1 1E0S
Antimony 5 OOE+01 1 BE 03 2 7E-03 1 3E03 1 7E0S 1 4E-03 8 5E 03 4 2E03 7 9E04 4 5E 03 4 5E 04 1 3E04 2 1E-03 2 IE 03 4 2E02 0 OE+OO 1 6E 03 1 6E0S 2 2E-02 SOE 05
Arsenic 1 OOE+00 5 3E0B 1 6E-05 5 BE 06 1 IE 07 6 3E06 5 4E 05 2 4E-05 2 BE 06 2 4E-05 1 5E-0B BOE 06 6 8E06 6 BE 06 2 8E-06 7 5E05 9 6E06 9 6E06 1 SE 06 4 BE 04
Banum 5 OOE+01 1 2E-04 BSE 04 1 BE 04 3 9E0B 1 5E 04 1 3E0S 5 5E-04 6 5E05 5 6E04 3 BE 05 7 0E05 1 6E 04 1 6E04 9 7E 05 1 7E 03 2 3E-04 2 BE 04 S2E-05 1 IE 02
Benzene 1 59E+02 2 IE 03 4 2E 03 2 0E 03 2 7E03 2 BE 03 1 BE 02 6 7E 03 1 2E03 7 IE 03 7 IE 04 2 0E 04 3 3E 03 3 3E 03 6 6E 02 0 OE+OO 2 5E 03 2 5E-03 3 4E02 7 9E-05
Beryllium 2 OOE 01 2 9E-06 8 7E 06 3 1 E-06 8 9E 08 3 5E 06 2 9E-05 1 SE05 1 5E-06 1 3E05 S4E 07 1 6E06 B7E-06 3 7E 06 2 3E06 4 OE-05 S2E0B 5 2E06 1 2E-06 2 6E04
Cadmium 1 OOE+OO BOE 06 2 4E 05 8 5E-06 2 5E 07 9 BE 06 B1E05 3 BE 05 4 2E06 BBE 05 2 BE 06 4 5E 06 1 0E05 1 OE 05 6 BE 06 1 IE 04 1 SE 05 1 SE05 S4E-06 7 2E04
Carbon disulfide 311E+02 1 OE 03 2 IE 03 1 OE 03 1 SE OS 1 IE 03 6 6E03 S3E-03 6 2E04 S5E-03 S5E 04 9 BE 05 1 6E 03 1 6E 03 SSE-02 0 OE+00 1 BE 03 1 3E03 1 7E 02 B9E0S
Carbon tetrachloride 314E+0B 7 2E 04 1 5E 03 7 0E 04 9SE04 7 9E04 4 6E 03 2 3E03 4 3E-04 2 5E-0B 2 5E 04 6 9E 05 1 IE 03 1 IE 03 2 3E02 0 OE+00 8 BE-04 BBE 04 1 2E 02 2 7E0S
Chlorobenzene 4 59E+03 1 2E-04 2 4E-04 1 1E04 1 5E-04 1 3E-04 7 5E-04 3 7E 04 7 OE-05 4 OE-04 4 0E05 1 IE 05 1 BE 04 1 BE 04 3 7E OS 0 OE+00 1 4E 04 1 4E 04 1 9E 03 4 4E06
Chromium 5 OOE+01 3 3E 04 9 9E 04 3 5E 04 1 OE 05 3 9E-04 3 3E-03 1 5E 03 1 7E 04 1 5E 03 9 6E05 1 8E04 4 2E-04 4 2E-04 2 6E 04 4 6E-03 5 9E 04 5 9E04 1 4E-04 2 9E 02
Cobalt 2 OOE+OO 2 4E 05 4 9E 05 2 4E-05 3 2E-05 2 7E 05 1 6E04 7 9E05 1 5E-05 B4E-05 8 4E 06 2SE06 S9E-05 3 9E05 7 8E-04 0 OE+00 BOE 05 3 0E-0S 4 0E 04 9 BE 07
Copper 1 OOE+02 3 BE 04 1 2E03 4 0E 04 0 OE+OO 4 6E04 3 9E03 1 7E 03 2 0E04 1 7E OS 1 1E-04 2 2E04 4 9E04 4 9E04 5 BE 06 5 5E03 7 0E 04 7 0E04 1 OE-05 BSE 02
Dichlorobenzene 1 2 6 OOE+03 1 6E-05 3 2E-05 1 6E05 2 1E05 1 BE 05 1 OE-04 5 2E-05 9 7E 06 5 5E-05 5 5E 06 1 5E06 2 5E 05 2 5E05 5 1E-04 0 OE+00 2 0E05 2 0E05 2 6E04 6 IE 07
Dichloroethane 1 1 4 04E+04 1 1E-05 2 2E05 1 IE 05 1 4E05 1 2E05 7 0E05 BSE 05 6 5E-06 S7E-05 3 7E 06 1 OE-06 1 7E 05 1 7E-05 B5E-04 0 OE+00 1 3E-05 1 BEOS 1 BE 04 4 1E-07
Dichloroethylene cis 1 2 7 91E+04 1 6E05 3 1E05 1 5E-05 2 OE-05 1 7E-05 1 OE-04 SOE 05 9 4E-06 5 BE 05 5SE 06 1 5E 06 2 5E05 2 5E 05 SOE 04 0 OE+00 1 9E-05 1 9E 05 2 6E04 5 9E07
Dichloroethylene 1 2 (trans) 7 91E+04 2 5E 05 5 0E 05 2 4E-05 3 2E 05 2 7E 05 1 6E04 SOE 05 1 5E 05 8 4E-05 8 4E-06 2 4E-06 3 9E-05 3 9E 05 7 9E04 0 OE+OO 3 0E 05 SOE 05 41E04 9 4E 07
Diethyl phthalate 5 OOE+02 BOE 05 6 OE-05 2 9E05 3 9E05 3 3E-05 1 9E04 9 BE 05 1 8E05 1 OE-04 1 0E05 2 9E06 4 7E05 4 7E05 9 5E-04 0 OE+00 3 6E05 3 6E-05 4 9E-04 1 IE 06
Dimethyl phthalate 5 OOE+02 2 OE-05 4 1E05 2 0E 05 2 6E-05 2 2E-05 1 BE 04 6 6E05 1 2E-05 7 0E05 7 0E06 2 0E 06 3 2E05 3 2E 05 6 5E-04 0 OE+OO 2 5E-05 2 5E0S 3 BE-04 7 7E 07
Diphenylamine 1 OOE+03 2 0E05 4 IE 05 2 OE-05 2 BE-05 2 2E05 1 3E-04 6 6E05 1 2E-05 7 0E 05 7 0E06 2 OE-06 3 2E-05 3 2E-05 6 5E 04 0 OE+00 2SE 05 2 5E 05 BSE 04 7 7E-07
Ethylbenzene 4 S3E+04 1 BE 04 2 7E 04 1 3E-04 1 7E-04 1 5E 04 8 7E 04 4 3E-04 B 1E-05 4 6E04 4 6E05 1 SE 05 2 IE 04 2 1E-04 4 3E-03 0 OE+OO 1 6E-04 1 BE 04 2 2E-03 5 1E-06
Hexachlorobenzene 2 OOE 01 4 8E04 9 7E 04 4 7E-04 6 2E-04 5SE04 3 IE 03 1 5E-03 2 9E-04 1 6E-03 1 6E04 4 BE-05 7 6E-04 7 6E-04 1 SE 02 0 OE+00 5 9E 04 S9E 04 7SE03 1 8E05
Hexachlorocyclopentadiene 1 OOE+OO 4 IE 04 8 2E04 4 0E04 5 BE 04 4 5E-04 2 BE 03 1 3E-03 2 5E 04 1 4E-03 1 4E-04 S9E05 6 4E-04 6 4E-04 1 SE 02 0 OE+00 5 OE-04 SOE 04 6 7E 03 1 5E-05
Hexane 1 76E+05 4 1E-04 8 3E 04 4 0E 04 5 BE 04 4 5E04 2 6E03 1 3E-03 2 5E 04 1 4E 03 1 4E-04 3 9E-05 6 5E04 6 5E04 1 3E 02 0 OE+00 SOE 04 SOE 04 6 7E OB 1 6E 05
Lead 5 OOE+00 4 9E 04 1 5E-0B 5 2E 04 1 2E05 5 8E-04 5 OE-03 2 2E03 2 5E 04 2 2E-03 1 4E 04 2 7E 04 B2E04 B2E-04 3 OE-04 B9E-03 S8E-04 8 BE 04 1 6E04 4 4E 02
Manganese 2OOE+01 6 9E-03 1 4E 02 6 7E 03 8 9E-03 7 5E03 4 4E 02 2 2E02 4 1E-0B 2 3E 02 2 3E-03 6 6E-04 1 IE 02 1 IE 02 2 2E01 0 OE+OO B 4E-0B B4E-03 1 IE 01 2 6E 04
Mercury 2 50E+00 3 IE 06 6 BE 06 BOE 06 4 OEOB S4E 06 2 0E05 1 OE 05 1 9E-06 1 IE 05 1 IE 06 BOE 07 4 9E0B 4 9E 06 1 OE 04 0 OE+00 BSE 06 3 BE 06 S IE 05 1 2E-07
Methacryionitnle 2 74E+02 1 IE 04 2 2E04 1 1E-04 1 4E-04 1 2E-04 7 0E04 3 5E 04 6 5E 05 3 7E 04 3 7E 05 1 OE-05 1 7E 04 1 7E04 3 SE-03 0 OE+00 1 3E-04 1 SE04 1 8E OS 4 IE 06
Methyl Methacrylate 2 04E+04 5 2E05 1 IE 04 5 1E-05 6 BE 05 5 8E05 3 4E 04 1 7E-04 S2E 05 1 8E04 1 SE 05 5 0E 06 8 BE 05 B3E05 1 7E03 0 OE+00 6 4E 05 B4E 05 8 6E 04 2 OEOB
Naphthalene 5 23E+03 6 IE 04 1 2E03 5 9E04 7 8E04 6 7E 04 3 9E03 1 9E 03 3 7E 04 2 IE-OS 2 IE 04 5 BE 05 9 BE-04 9 6E04 1 9E-02 0 OE+OO 7 4E 04 7 4E-04 9 9E 03 2 BEOS
Nickel 1 50E+02 1 IE 03 3 2E03 1 IE 03 3 3E05 1 SE-03 1 IE 02 4 8E-03 5 BE 04 4 BE OS 3 1E-04 BOE 04 1 4E-03 1 4E03 8 4E-04 1 5E-02 1 9E03 1 9E 03 4 5E04 9 6E02
Nitrobenzene 5 02E+02 2SE 05 4 7E05 2 3E 05 BOE 05 2 5E-05 1 5E 04 7 4E-05 1 4E 05 7 9E 05 7 9E 06 2 2E06 3 7E05 B7E05 7 4E 04 0 OE+00 2 8E-05 2 8E-05 3 BE 04 BBE 07
Pentachlorophenol 5 OOE+01 1 OE-03 2 IE 03 9 9E 04 1 3E03 1 IE 03 6 6E-03 BBE 03 6 IE 04 B5E OS 3 5E-04 9 7E 05 1 BEOS 1 BE 03 3 3E-02 0 OE+OO 1 2E0B 1 2E03 1 7E-02 3 9E OS
Phenol 1 92E+03 9 0E 05 1 8E-04 BBE 05 1 2E04 9 9E-05 5 8E-04 2 9E04 5 4E 05 3 IE 04 3 IE 05 S6E06 1 4E 04 1 4E 04 2 9E-03 0 OE+OO 1 IE 04 1 IE 04 1 SE 03 3 4E 06
Phosphorus 1 OOE+01 21E-03 6 5E-03 2 3E03 0 OE+00 2 6E-03 2 2E 02 9SE 03 1 1E-03 9 7E-03 6 2E-04 1 2E-03 2 7E-0S 2 7E0S 3 0E 05 3 IE 02 3 9E 03 B9E 03 5 BE 05 2 0E01
Pyndine 3 23E+02 BOE 05 6 IE 05 2 9E-05 3 9E05 3 BE 05 1 9E 04 9 7E 05 1 8E-05 1 OE 04 1 0E05 2 9E-06 4SE05 4 BE 05 9 6E04 0 OE+00 3 7E 05 3 7E-0S 4 9E04 1 IE 06
Selenium 2 OOE+01 4 IE 05 1 3E04 4 4E05 0 OE+00 4 9E05 4 2E 04 1 BE 04 2 IE 05 1 9E04 1 2E05 2 4E 05 5 2E 05 5 2E05 S7E-07 S9E04 7 5E OS 7SE05 1 IE 06 3 8E 03
Silver 1 OOE+01 2 9E-05 B7E-05 3 OE-05 8 9E 07 3 4E05 2 9E 04 1 BE 04 1 5E05 1 3E 04 8 4E 06 1 6E 05 3 7E05 3 7E-05 2 2E-05 4 OE-04 5 2E 05 5 2E-0S 1 2E0S 2 6E 03
Styrene 8 50E+03 2 IE 05 4 3E05 2 IE 05 2 8E05 2 3E05 1 4E 04 6 9E05 1 SE 05 7 3E05 7 3E-06 2 0E06 3 4E 05 3 4E 05 BSE 04 0 OE+00 2 6E-05 2 BE OS 3 5E-04 8 IE 07
Tetrahydrofuran 1 47E+04 3 2E 05 6 4E 05 3 1E05 4 IE 05 3 5E05 2 1E 04 1 0E04 1 9E-05 1 1E-04 1 1E-05 3 1 E-06 51E05 5 IE 05 1 OE 03 0 OE+OO 3 9E 05 3 9E05 S2E04 1 2E 06
Thallium 1 OOE+01 5 BE-05 1 7E 04 5 9E05 1 7E-06 6 7E 05 5 7E 04 2 5E04 2 9E05 2 5E 04 1 6E 05 3 2E05 7 2E05 7 2E05 4 4E-0S 7 9E 04 1 0E04 1 0E04 2 4E 05 SOE OS
Toluene 7 52E+03 9 4E 04 1 9E03 9 2E04 1 2E03 1 OEOB 6 IE 03 3 0E 03 5 7E 04 3 2E-03 3 2E04 9 0E05 1 5E 03 1 5E03 BOE 02 0 OE+00 1 2E03 1 2E03 1 5E02 3 6E05
Vinyl Chlonde 2 55E+02 2 5E-04 5 0E04 2 4E-04 3 2E-04 2 7E 04 1 6E 03 BOE 04 1 5E-04 B5E04 B 5E 05 2 4E 05 4 0E04 4 0E 04 8 OE-03 0 OE+00 3 1E04 3 IE 04 4 IE-OS 9 5E06
Xylene o 4 33E+04 1 7E 04 3 3E04 1 6E04 2 IE 04 1 BE 04 1 IE-OS 5 3E04 1 OE 04 5 BE 04 5 BE 05 1 BE-05 2 BE 04 2 6E04 5 BE 03 0 OE+00 2 0E04 2 0E 04 2 7E 03 6 3E06
Zinc 2 OOE+02 3 5E 04 1 IE 03 3 7E 04 9 6E-0B 4 2E04 3 5E 03 1 5E03 1 8E-04 1 BE 03 1 0E04 2 0E04 4 5E04 4 5E-04 2 4E 04 4 9E03 6 BE 04 BSE 04 1 SE 04 3 IE 02
trans 1 3 Dichloropropene 4 53E+02 2 1E05 4 2E05 2 0E05 2 7E 05 2 3E-05 1 SE 04 6 7E-05 1 3E05 7 IE 05 71E06 2 0E 06 3 3E-05 BBE 05 BBE 04 0 OE+00 2SE 05 2 5E 05 3 4E 04 7 9E 07
Notes
1 Acute Toxic Screening Level = ACGIH TLV divided by 10
ACGIH TLVs from 2003 TLVs and BEls for Chemical Substances and Physical Agents Amencan Council of Government Industnal Hygienists (ACGIH)
Shading indicates that Toxic Screening Level was exceeded
NA No value available
TABLE 34
COMPARISON OF TOTAL 24 HOUR AIR CONCENTRATIONS (ug/m') TO UDAQ TOXIC SCREENING LEVELS AVERAGE EMISSION RATES
THIOKOL PROULSION INC
BRIGHMAN CITY UTAH
Chemical
Chronic/
Carcinogenic
Toxic
Screening
Level (1)
Adams
Ranch Autoliv Blue Creek Boundary #' Boundary #. I Boundary #'. ) Boundary #' J Chnstensen
Ranch
Holmgren
Ranch Pond Howe Dairy Thiokol
Ranch Pone
M 136
Offsite
Maximum
Gaseous
M 136
Offsite
Maximum
Particulate
M 225
Offsite
Maximum
Gaseous
M 225
Offsite
Maximum
Particulate
M 136
Onsite
Maximum
Gaseous
M 136
Onsite
Maximum
Particulate
M 225
Onsite
Maximum
Gaseous
M 225
Onsite
Maximum
Particulate
2 Methylnapthaiene 9 67E+01 8 7E 10 1 SE09 1 5E09 1 0E09 9 2E 10 1 7E 09 7 4E 10 4 9E 10 1 1E09 68E 10 1 9E 10 1 BE 09 1 6E 09 SOE 09 0 OE+00 3 BE 09 BSE 09 6 1E08 3 5E 11
Acetone 3 95E+04 8 7E 09 1 8E-0B 1 5E OS 1 OE 08 9 2E09 1 7E 08 7 3E09 4 BE-09 1 IE 08 6 7E 09 1 9E 09 1 BE 08 1 6E0B BOE-OB 0 OE+00 BBE 08 3SE08 6 IE 07 S5E 10
Acetonitnle 1 12E+03 2 8E-09 5SE09 4 7E-09 3 4E-09 SOE 09 5 4E-09 2 4E 09 1 BE 09 3 6E 09 2 2E09 B2E 10 SOE 09 SOE 09 2 6E08 0 OE+00 1 IE 08 1 IE 08 1 9E07 1 IE 10
Acetophenone 1 63E+03 9 5E 10 2 0E09 1 6E-09 1 1E09 1 OE-09 1 9E09 8 1E 10 5 BE 10 1 2E-09 7 4E 10 21E10 1 7E-Q9 1 7E09 8 8E09 0 OE+OO 3 6E09 S6E-09 B7E-0B S9E11
Acry/onitn/e 4B1E+01 2 4E 09 5 IE 09 41E09 2 9E09 2 BE 09 4 8E-09 21E09 1 4E 09 3 IE 09 1 9E09 5 4E 10 4 4E 09 4 4E 09 2 2E0B 0 OE+OO 9 2E09 9 2E09 1 7E 07 99E 11
Aluminum 3 SSE+01 2 2E0S 4 5E-0S 3 7E 05 2 BE 05 2SE05 4 3E05 1 8E05 1 2E05 2 BE 05 1 7E05 4 9E06 3 9E05 3 9E0S 2 0E 04 0 OE+00 8 3E-0S 8 3E0S 1 SE 03 BBE 07
Aniline 8 4SE+01 1 9E-09 3 9E-09 3 2E09 2 BE 09 2 0E09 3 7E 09 1 6E 09 1 1E-09 2 4E09 1 5E 09 42E 10 3 4E-09 3 4E09 1 7E-08 0 OE+00 7 2E-09 7 2E09 1 3E-07 76E 11
Antimony 1 B7E+01 7 6E-09 1 6E-0B 1 3E08 9 IE 09 BOE 09 1 5E-08 6 4E-09 4 2E09 9 BE 09 5 9E 09 1 7E 09 1 4E-0S 1 4E0S 7 0E08 0 OE+00 2 9E0S 2 9E 08 SBE 07 3 1E 10
Arsenic 1 11E-01 7 BE 11 1 SE 10 1 SE 10 B9E 13 S3E 11 1 9E 10 7 7E 11 4 5E 11 1 OE 10 2SE 11 1 BE 11 1 BE 12 1 BE 12 68E 12 2 4E 10 2 8E 12 2 BE 12 S2E 11 BOE 14
Banum 1 67E+01 1 4E 09 2 7E-09 2 8E 09 2 4E 11 1 SE-09 3 3E09 1 4E 09 8 IE 10 1 BE 09 4 5E 10 2 BE 10 3 SE 11 BSE 11 1 BE 10 4 2E 09 7SE 11 7 5E 11 1 4E 09 BOE IS
Benzene 1 77E+01 1 3E-0B 2SE-08 2 2E08 1 BE 08 1 4E 08 2 6E-0B 1 1E-08 7 4E 09 1 7E08 1 OE-08 3 0E 09 2 4E OS 2 4E 08 1 2E 07 0 OE+OO SOE 08 5 OE-08 9 BE 07 5 4E 10
Beryllium 2 22E 02 B2E 11 6 IE 11 6 3E 11 S4E 13 3 4E 11 7 BE 11 3 IE 11 1 8E 11 4 2E 11 1 OE 11 5 3E 12 8 IE 13 8 1E IS 42E 12 9 BE 11 1 7E 12 1 7E 12 3 IE 11 1 BE 14
Cadmium 1 11E01 BBE 11 1 7E 10 1 BE 10 1 5E 12 9 4E 11 2 IE 10 87E 11 51E11 1 2E 10 2 9E 11 1 5E 11 2 3E 12 2 3E 12 1 2E 11 2 7E 10 4 BE 12 4 BE 12 BBE 11 51E 14
Carbon disulfide 1 04E+02 4 BE 09 9 5E09 7 7E09 5 5E-09 4 BE 09 B9E-09 SOE 09 2 5E 09 S9E 09 S5E 09 1 OE-09 B2E09 8 2E09 4 2E08 0 OE+00 1 7E-08 1 7E-0B S2E 07 1 9E 10
Carbon tetrachlonde 3 49E+02 6 4E 09 1 3E-08 1 IE 08 7 7E09 6 8E-09 1 BE 08 5 4E-09 BBE 09 8 SE 09 SOE 09 1 4E 09 1 2E 08 1 2E08 5 9E08 0 OE+OO 2 4E 08 2 4E-08 4 5E07 2 6E 10
Chlorobenzene 1 53E+0S 6 6E 10 1 4E 09 1 1E-09 79E 10 70E 10 1 SE09 56E 10 3 7E 10 BSE 10 S1E 10 1 SE 10 1 2E 09 1 2E09 B 1E-09 0 OE+OO 2 5E 09 2 SE-09 4 BE 08 2 7E 11
Chromium 5 56E+00 4 BE 09 9 4E-09 9 6E-09 8 3E 11 51E-09 1 2E08 4BE-09 2 BE 09 6 4E 09 1 6E09 B IE 10 1 2E 10 1 2E 10 BBE 10 1 5E 08 2 6E 10 2 6E 10 4 8E-09 2 BE 12
Cobalt 2 22E-01 1 5E 10 3 IE 10 2 5E 10 1 8E 10 1 6E 10 2 9E 10 1 3E 10 8 4E 11 1 9E 10 1 2E 10 3 4E 11 2 7E 10 2 7E 10 1 4E 09 0 OE+OO 5 7E 10 S7E 10 1 IE OB 61E 12
Copper 3 33E+01 4 4E 09 BSE 09 S7E-09 0 OE+00 4 7E09 1 OE 08 4 BE 09 2 BE 09 5 BE 09 1 4E-09 ^ 7 3E 10 0 OE+OO 0 OE+00 0 OE+00 1 3E08 0 OE+OO 0 OE+00 0 OE+00 0 OE+00
Dichlorobenzene 1 2 2 OOE+03 1 OE 10 2 2E 10 1 BE 10 1 3E 10 1 IE 10 2 IE 10 8 9E 11 5 9E 11 1 4E 10 82E 11 23E 11 1 9E 10 1 9E 10 9 7E 10 0 OE+00 40E 10 4 0E 10 7 BE 09 4 3E 12
Dichloroethane 1 1 4 49E+03 71E 11 1 5E 10 1 2E 10 BSE 11 7SE 11 1 4E 10 6 0E 11 B9E 11 92E 11 S5E 11 1 BE 11 1 BE 10 1 BE 10 BSE 10 0 OE+00 2 7E 10 2 7E 10 4 9E09 2 9E 12
Dichloroethylene cis 1 2 2 64E+04 1 OE 10 21E 10 1 7E 10 1 2E 10 1 1E 10 2 0E 10 86E 11 S7E 11 1 SE 10 7 9E 11 2SE 11 1 BE 10 1 8E 10 9 4E 10 0 OE+OO 3 9E 10 3 9E 10 7 1E09 41E 12
Dichloroethylene 1 2 (trans) 2 64E+04 1 6E 10 B4E 10 2 7E 10 2 0E 10 1 7E 10 B2E 10 1 4E 10 9 1E 11 2 IE 10 1 SE 10 SBE 11 29E 10 2 9E 10 1 5E 09 0 OE+OO 6 2E 10 6 2E 10 1 1E0B BBE 12
Diethyl phthalate 1 67E+02 1 9E 10 4 0E 10 BSE 10 23E 10 21E 10 3 BE 10 1 6E 10 1 IE 10 2 5E 10 1 5E 10 4 3E 11 BSE 10 BSE 10 1 8E 09 0 OE+OO 7 4E 10 7 4E 10 1 4E 08 7 9E 12
Dimethyl phthalate 1 67E+02 1 BE 10 2 7E 10 22E 10 1 BE 10 1 4E 10 2 5E 10 1 IE 10 72E 11 1 7E 10 1 OE 10 29E 11 2SE 10 2SE 10 1 2E09 0 OE+00 4 9E 10 49E 10 9 0E09 5 2E 12
Diphenylamine S SSE+02 1 SE 10 2 7E 10 2 2E 10 1 BE 10 1 4E 10 2 5E 10 1 IE 10 72E 11 1 7E 10 1 OE 10 29E 11 2 BE 10 2 3E 10 1 2E-09 0 OE+00 4 9E 10 4 9E 10 9 0E 09 52E 12
Ethylbenzene 4 81E+03 B1E 10 1 7E 09 1 4E 09 9 8E 10 8 BE 10 1 6E09 B9E 10 4 5E 10 1 1E09 6 BE 10 1 8E 10 1 SE 09 1 5E-09 7SE 09 0 OE+OO 3 IE 09 3 IE 09 5 7E OB SBE 11
Hexachlorobenzene 2 22E 02 2 OE-09 4 2E-09 3 4E-09 2 4E 09 2 1E 09 3 9E09 1 7E 09 1 1E09 2 6E-09 1 6E-09 45E 10 3 BE 09 3 6E-09 1 9E08 0 OE+00 7 6E09 7 6E09 1 4E-07 B2E 11
Hexachlorocyclopentadiene 3 BBE 01 2 6E09 5 4E 09 4 4E-09 3 1E-09 2 7E-09 5 IE 09 2 2E-09 1 4E-09 3 4E 09 2 OE-09 SBE 10 4 7E 09 4 7E 09 2 4E OS 0 OE+00 9 BE 09 9 BE-09 1 8E-07 1 1E 10
Hexane 5 B6E+04 2 2E09 4 5E-09 S7E 09 2 BE 09 2BE-09 4 3E 09 1 BE-09 1 2E-09 2 8E09 1 7E 09 4 9E 10 3 9E 09 3 9E09 2 OEOB 0 OE+OO 8 SE 09 B BE-09 1 SE 07 BBE 11
Lead 5 5BE-01 4 9E 09 9 4E 09 9 7E-09 BSE 11 5 2E09 1 2E 08 4 BE 09 2 BE 09 6 5E09 1 6E-09 8 2E 10 9 7E 11 9 7E 11 SOE 10 1 SE 08 2 IE 10 2 IE 10 B BE-09 2 2E 12
Manganese 6 67E+00 2 9E08 6 IE 08 4 9E-0B BSE 08 3 IE 08 5 7E 08 2 5E 08 1 6E-08 BSE 08 2 BEOS B5E-09 5 2E0B 5 2E08 2 7E 07 0 OE+00 1 IE 07 1 1E-07 2 0E06 1 2E 09
Mercury 8 BBE 01 1 2E 11 2 3E 11 2BE 11 0 OE+OO 1 2E 11 2 BE 11 1 2E 11 6 9E 12 1 6E 11 3 7E 12 2 0E 12 0 OE+00 0 OE+00 0 OE+00 SBE 11 0 OE+00 2 0E 17 0 OE+OO 0 OE+00
Methacryionitnle 913E+01 1 OE 09 2 IE 09 1 7E09 1 2E-09 1 1E-09 2 OE-09 8SE 10 5 6E 10 1 BE-09 7 8E 10 2 2E 10 1 8E 09 1 8E09 9 2E-09 0 OE+00 BSE 09 3 BE 09 7 0E 08 41E 11
Methyl Methacrylate 6 B1E+0S S4E 10 7 2E 10 58E 10 4 2E 10 3 7E 10 BBE 10 2 9E 10 1 9E 10 4SE 10 2 7E 10 7 7E 11 6 2E 10 B2E 10 3 2E09 0 OE+00 1 SE 09 1 3E09 2 4E 08 1 4E 11
Naphthalene S81E+02 S7E-09 7 BE 09 6 2E 09 4 4E 09 3 9E09 7 2E09 S1E09 2 0E09 4 SE-09 2 9E-09 82E 10 6 6E-09 6 6E-09 3 4E 08 0 OE+00 1 4E 08 1 4E OS 2 BE 07 1 SE 10
Nickel 1 67E+01 1 IE 08 2 1E08 2 IE 08 1 BE 10 1 IE-OS 2 BE 08 1 1E0B 6 3E09 1 4E 08 BSE 09 1 BE 09 2 8E 10 28E 10 1 4E-09 BBE-OB 5 SE 10 5SE 10 1 IE 08 6 2E 12
Nitrobenzene 1 67E+02 1 5E 10 3 IE 10 2 5E 10 1 8E 10 1 BE 10 2 9E 10 1 2E 10 8 2E 11 1 9E 10 1 IE 10 33E 11 2 6E 10 2 6E 10 1 4E 09 0 OE+OO SBE 10 SBE 10 1 OE-08 6 0E 12
Pentachlorophenol 5 56E+00 6 4E-09 1 3E-08 1 1E 08 7 BE 09 6 BE 09 1 SE 08 5 4E 09 3 6E 09 8 4E 09 SOE 09 1 4E 09 1 2E 08 1 2E0B 5 9E08 0 OE+00 2 4E0S 2 4E-08 4 5E 07 2 6E 10
Phenol B 40E+02 70E 10 1 5E09 1 2E09 8 4E 10 7 4E 10 1 4E 09 5 9E 10 3 9E 10 9 1E 10 S4E 10 1 6E 10 1 BE 09 1 BE-09 6 5E-09 0 OE+00 2 7E 09 2 7E-09 4 9E 08 2 BE 11
Phosphorus 3 33E+00 3 4E 08 6 5E-08 6 7E 08 0 OE+00 3 6E-0B SOE 08 3 BE 08 2 OE-OB 4 5E-0B 1 1E0B 5 6E 09 0 OE+00 0 OE+00 0 OE+00 1 OE 07 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Pyndine 1 08E+02 1 9E 10 40E 10 3 2E 10 2 BE 10 2 0E 10 S7E10 1 BE 10 1 IE 10 2 SE 10 1 5E 10 4SE 11 3 4E 10 3 4E 10 1 BE 09 0 OE+00 7 2E 10 72E 10 1 BEOS 7 7E 12
Selenium B B7E+00 46E 10 B9E 10 91E 10 0 OE+00 49E 10 1 1E-09 4 5E 10 2 7E 10 6 1E 10 1 5E 10 7 7E 11 0 OE+00 0 OE+OO 0 OE+00 1 4E 09 0 OE+OO 0 OE+00 0 OE+OO 0 OE+00
Silver 3 33E+00 2 5E 10 4 BE 10 SOE 10 4 3E 12 2 7E 10 6 0E 10 2 5E 10 1 SE 10 BSE 10 8 1E 11 42E 11 6 4E 12 6 4E 12 3 BE 11 76E 10 1 BE 11 1 3E 11 2 5E 10 1 4E 13
Styrene 2 83E+03 1 9E 10 39E 10 B2E 10 2 3E 10 2 0E 10 S7E 10 1 6E 10 1 OE 10 2 4E 10 1 5E 10 42E 11 3 4E 10 3 4E 10 1 7E 09 0 OE+00 7 IE 10 71E 10 1 BE 08 7BE 12
Tetrahydrofuran 1 63E+03 2 2E 10 46E 10 3 7E 10 2 6E 10 2 BE 10 4 BE 10 1 SE 10 1 2E 10 2 8E 10 1 7E 10 49E 11 3 9E 10 S9E 10 2 0E09 0 OE+00 8 3E 10 8SE 10 1 5E-0B B9E 12
Thallium 1 OOE+02 6 2E 10 1 2E 09 1 2E09 1 IE 11 6 6E 10 1 5E09 61E10 3 6E 10 B2E 10 2 0E 10 1 OE 10 1 6E 11 1 6E 11 S1E11 1 9E 09 BBE 11 33E 11 6 IE 10 B6E 13
Toluene 2 51E+03 5 4E 09 1 1E08 9 IE 09 6 5E 09 5 7E09 1 1E08 46E 09 SOE 09 7 0E 09 4 2E 09 1 2E 09 9 7EQ9 9 7E09 5 OE-08 0 OE+00 2 0E08 2 OEOB 3 8E 07 2 2E 10
Vinyl Chlonde 2 B3E+01 1 BE 09 2 7E-09 2 2E-09 1 6E09 1 4E 09 2 6E09 1 1E-09 7 3E 10 1 7E 09 1 OE-09 2 9E 10 2 4E-09 2 4E-09 1 2E-0S 0 OE+00 SOE 09 5 OE-09 9 2E08 S3E 11
Xylene o 1 44E+04 1 OE 09 2 2E 09 1 8E-09 1 2E09 1 1E-09 2 OE-09 BSE 10 5 8E 10 1 3E09 B1E 10 2 BE 10 1 9E09 1 9E-09 9 BE 09 0 OE+00 B9E09 3 9E09 7 BE 08 4 2E 11
Zinc 6 67E+01 BSE 09 6SE-09 6 5E 09 SOE 11 3 5E-09 7SE 09 3 2E 09 1 9E 09 4 BE 09 1 IE 09 5SE 10 7 4E 11 7 4E 11 3 8E 10 9 9E09 1 6E 10 1 6E 10 2 9E09 1 7E 12
trans 1,3 Dichloropropene 5 03E+01 1 4E 10 2 8E 10 2 3E 10 1 6E 10 1 4E 10 2 7E 10 1 1E 10 76E 11 1 8E 10 1 IE 10 SOE 11 2 4E 10 2 4E 10 1 2E09 0 OE+00 S IE 10 51E 10 9SE09 5 5E 12
Notes
1 Chronic/Carcinogenic Toxic Screening Level = ACGIH TLV divided by 30 for noncarcinogens and 90 for carcinogens
ACGIH TLVs from 2003 TLVs and BEls for Chemical Substances and Physical Agents Amencan Council of Government Industrial Hygienists (ACGIH)
Shading indicates that Toxic Screening Level was exceeded
TABLE 35
COMPARISON OF TOTAL 24 HOUR AIR CONCENTRATIONS (ug/m') TO UDAQ TOXIC SCREENING LEVELS MAXIMUM EMISSION RATES
THIOKOL PROULSION INC
BRIGHMAN CITY UTAH
Chronic/
Carcinogenic
Toxic
Screening
Level (1)
M 136 M 136 M 225 M 225 M 136 M 136 M225 M 225
Chemical
Chronic/
Carcinogenic
Toxic
Screening
Level (1)
Adams
Ranch Autoliv Blue Creek Boundary # Boundary #. I Boundary #. 3 Boundary #' ^ Christenser
Ranch
Holmgren
Ranch Pond Howe Dairy Thiokol
Ranch Pond
Offsite
Maximum
Offsite
Maximum
Offsite
Maximum
Offsite
Maximum
Onsite
Maximum
Onsite
Maximum
Onsite
Maximum
Onsite
Maximum
Chronic/
Carcinogenic
Toxic
Screening
Level (1) Gaseous Particulate Gaseous Particulate Gaseous Particulate Gaseous Particulate
2 Methylnapthaiene 9 B7E+01 1 BE 09 BSE 09 2 6E 09 1 9E-09 1 7E-09 3 IE 09 1 3E 09 8 7E 10 2 0E09 1 2E09 BSE 10 2 8E09 2 8E-09 1 4E 08 0 OE+00 BOE 09 BOE 09 1 1E07 6 4E 11
Acetone 3 95E+04 1 7E 08 BSE 08 2 9E08 2 OEOB 1 8E-08 3 BE OS 1 4E 08 9 5E-09 2 2E08 1 3E0S 3 8E09 3 1E 08 3 IE 08 1 6E-07 0 OE+00 6 4E-08 6 4E0B 1 2E-0B B9E 10
Acetonitnle 1 12E+03 4 6E 09 9 5E09 7 7E 09 SSE09 4 9E09 9 OE-09 3 9E-09 2 6E09 S9E-09 SBE 09 1 OE-09 8 2E09 8 2E09 4 2E-0B 0 OE+OO 1 7E 08 1 7E08 3 2E07 1 9E 10
Acetophenone 1 63E+03 1 3E09 2 BE 09 2 2E-09 1 6E09 1 4E09 2 BE 09 1 1E-09 7 4E 10 1 7E 09 1 0E09 SOE 10 2 4E-09 2 4E09 1 2E 08 0 OE+00 SOE 09 SOE 09 9 2E0B S4E 11
Acrylonitnle 4 81E+01 4 IE 09 BBE 09 7 0E 09 5 OE-09 4 4E 09 B1E09 3 SE-09 2 SE-09 S4E-09 3 2E-09 9 2E 10 7 4E 09 7 4E 09 SBE 08 0 OE+00 1 BE 08 1 6E 08 2 9E07 1 7E 10
Aluminum 3 BBE+01 2 BEOS 5 9E0S 4 BE-05 S4E 05 3 OEOS 5 5E 05 2 4E OS 1 6E05 3 7E0S 2 2E-05 BSE 06 5 IE OS 5 IE 05 2 6E04 0 OE+00 1 1E-04 1 IE 04 2 OEOS 1 2E06
Aniline 8 45E+01 3 2E-09 6 6E09 5 4E 09 3 BE 09 3 4E-09 6 2E09 2 7E09 1 8E-09 41E09 2 5E09 71E 10 5 7E-09 5 7E09 2 9E08 0 OE+00 1 2E08 1 2E-08 2 2E07 1 BE 10
Antimony 1 67E+01 1 4E 08 2 9E08 2 4E-0B 1 7E OS 1 SE 08 2 7E-0B 1 2E0B 7 BE 09 1 BE 08 1 1E-08 3 1E-09 2SE 08 2 5E 08 1 BE 07 0 OE+00 S3E 08 SSE 08 9 BE 07 S7E 10
Arsenic 1 11E01 9 5E 11 1 SE 10 1 9E 10 1 IE 12 1 OE 10 2 BE 10 9 4E 11 SBE 11 1 SE 10 3 IE 11 1 6E 11 1 6E 12 1 BE 12 B4E 12 2 9E 10 B4E 12 3 4E 12 BSE 11 3 7E 14
Banum 1 67E+01 2 2E09 4 4E 09 4SE 09 BBE 11 2 4E 09 5 4E09 2 2E 09 1 3E09 3 OE-09 7BE 10 SBE 10 57E 11 5 7E 11 2 9E 10 6 BE-09 1 2E 10 1 2E 10 2 2E09 1 SE 12
Benzene 1 77E+01 2 2E 08 4 6E 08 3 7E 08 2 7E08 2 3E-08 4SE08 1 9E08 1 2E-0B 2 9E-08 1 7E 08 4 9E09 4 OEOS 4 0E 08 2 0E07 0 OE+00 S4E-08 B4E 08 1 SE 06 9 0E 10
Beryllium 2 22E-02 52E 11 1 OE 10 1 OE 10 S9E 13 S5E 11 1 2E 10 S IE 11 3 0E 11 69E 11 1 7E 11 BBE 12 1 SE 12 1 BE 12 6 8E12 1 BE 10 2 BE 12 2 BE 12 52E 11 SOE 14
Cadmium 1 11E01 1 4E 10 2 8E 10 2 9E 10 2 5E 12 1 SE 10 BSE 10 1 4E 10 B4E 11 1 9E 10 4 7E 11 2 4E 11 3 7E 12 3 7E 12 1 9E 11 4 4E 10 78E 12 78E 12 1 4E 10 BBE 14
Carbon disulfide 1 04E+02 1 IE 08 2 BE 08 1 SEOB 1 3E 08 1 2E08 2 IE 08 9 2E09 6 1E-09 1 4E 08 BSE 09 2 4E-09 2 0E 08 2 0E OS 1 OE 07 0 OE+00 4 IE 08 4 IE-OB 7 BE 07 4 4E 10
Carbon tetrachlonde 3 49E+02 7 7E 09 1 OEOS 1 3E08 9 3E 09 8 2E09 1 SE08 B SE-09 4 3E09 1 OEOB BOE 09 1 7E 09 1 4E OS 1 4E OS 71E-0B 0 OE+00 2 9E-08 2 9E08 5 4E-07 B1E 10
Chlorobenzene 1 SSE+OS 1 2E-09 2 6E-09 2 1E-09 1 5E-09 1 3E-09 2 4E 09 1 OE-09 6 9E 10 1 6E-09 9 BE 10 2 8E 10 2 2E 09 2 2E-09 1 1E0B 0 OE+00 4 7E 09 4 7E-09 8 7E08 SOE 11
Chromium 5 SBE+OO 5 9E09 1 1E08 1 2E-08 1 OE 10 6 SE-09 1 4E-0B 5 BE 09 3 5E-09 7 9E-09 1 9E09 1 OE 09 1 SE 10 1 SE 10 7 7E 10 1 8E08 S2E 10 3 2E 10 S9E-09 3 4E 12
Cobalt 2 22E-01 2 6E 10 5 4E 10 4 4E 10 3 IE 10 2 8E 10 5 IE 10 2 2E 10 1 SE 10 3 4E 10 2 0E 10 S8E 11 47E 10 4 7E 10 2 4E-09 0 OE+00 9 9E 10 9 9E 10 1 SEOB 1 IE 11
Copper 3 33E+01 6 9E 09 1 3E-08 1 4E 08 0 OE+OO 7 4E 09 1 7E 08 6 BE 09 4 1E09 9 2E-09 2 2E09 1 2E-09 0 OE+00 0 OE+OO 0 OE+00 2 1E-08 0 OE+00 0 OE+00 0 OE+00 0 OE+00
Dichlorobenzene 1 2 2 OOE+03 1 7E 10 SOE 10 2 9E 10 2 IE 10 1 8E 10 BBE 10 1 4E 10 9SE 11 2 2E 10 1 BE 10 38E 11 3 IE 10 3 1E 10 1 6E09 0 OE+00 BSE 10 6 5E 10 1 2E-08 6 9E 12
Dichloroethane 1 1 4 49E+0S 1 2E 10 2 4E 10 1 9E 10 1 4E 10 1 2E 10 2 BE 10 9 7E 11 6 4E 11 1 SE 10 9 0E 11 2 6E 11 2 IE 10 2 IE 10 1 IE 09 0 OE+00 4 4E 10 4 4E 10 8 IE 09 4 7E 12
Dichloroethylene cis 1 2 2 64E+04 1 7E 10 3 5E 10 2 8E 10 2 0E 10 1 BE 10 B2E 10 1 4E 10 9 3E 11 2 2E 10 1 3E 10 3 7E 11 SOE 10 SOE 10 1 SE09 0 OE+00 BSE 10 6 BE 10 1 2E 08 6 7E 12
Dichloroethylene 1 2 (trans) 2 64E+04 2 6E 10 S5E 10 4SE 10 3 2E 10 2 BE 10 5 2E 10 2 2E 10 1 SE 10 3 4E 10 2 0E 10 5 9E 11 4 7E 10 4 7E 10 2 4E-09 0 OE+00 1 0E09 1 OE-09 1 BE 08 1 IE 11
Diethyl phthalate 1 67E+02 3 2E 10 6 6E 10 5 4E 10 3SE 10 B4E 10 6 2E 10 2 7E 10 1 SE 10 41E 10 2SE 10 71E 11 5 7E 10 S7E 10 2 9E 09 0 OE+00 1 2E09 1 2E-09 2 2E 08 1 SE 11
Dimethyl phthalate 1 67E+02 2 2E 10 4 5E 10 3 7E 10 2 6E 10 2SE 10 43E 10 1 8E 10 1 2E 10 2 BE 10 1 7E 10 4 9E 11 S9E 10 3 9E 10 2 0E 09 0 OE+00 8SE 10 SSE 10 1 SE-OB BBE 12
Diphenylamine 3 33E+02 2 2E 10 4 5E 10 3 7E 10 2 6E 10 2 BE 10 43E 10 1 BE 10 1 2E 10 2 8E 10 1 7E 10 4 9E 11 3 9E 10 3 9E 10 2 OE-09 0 OE+OO BSE 10 8 3E 10 1 5E 08 8 8E 12
Ethylbenzene 4 81E+03 1 4E 09 3 OE-09 2 4E 09 1 7E 09 1 SE 09 2 BE 09 1 2E-09 BOE 10 1 9E-09 1 1E-09 3 2E 10 2 6E-09 2 BE-09 1 SE-OB 0 OE+00 5 4E-09 5 4E 09 1 0E07 SBE 11
Hexachlorobenzene 2 22E-02 5 IE 09 1 1E 08 B6E-09 B 1E-09 5 4E-09 1 OEOS 4 BE 09 2 BE 09 6 6E09 4 0E 09 1 1E-09 9 2E 09 9 2E 09 4 7E-0B 0 OE+00 1 9E0B 1 9E 08 B6E-07 2 IE 10
Hexachlorocyclopentadiene 3 BBE 01 4 BE 09 9 0E 09 7 3E09 5 2E 09 4 6E09 BSE 09 B7E 09 2 4E 09 5 6E-09 S4E 09 9 7E 10 7 8E-09 7SE 09 4 0E 08 0 OE+00 1 6E-oe 1 6E 08 SOE 07 1 BE 10
Hexane 5 86E+04 4 4E-09 9 IE 09 7 4E 09 S2E-09 4 6E 09 BSE 09 S7E 09 2 4E09 5 6E-09 3 4E 09 9 7E 10 7SE09 7 BE 09 4 0E OS 0 OE+00 1 7E OB 1 7E-08 3 OE-07 1 8E 10
Lead 5 56E 01 8 BE 09 1 7E OS 1 7E 08 1 2E 10 9 4E 09 2 IE 08 8 7E-09 5 IE 09 1 2E-08 2 8E-09 1 SE 09 1 7E 10 1 7E 10 9 0E 10 2 7E-0B 3 7E 10 3 7E 10 6 BE 09 3 9E 12
Manganese 6 67E+00 7 3E-08 1 SE07 1 2E07 8 8E-0B 7 8E-08 1 4E 07 6 2E 08 4 IE-OS 9 5E 08 5 7E08 1 6E 08 1 BE 07 1 BE-07 6 7E-07 0 OE+00 2 BE 07 2 8E07 5 IE 06 3 OE-09
Mercury 8 SBE 01 21E 11 41E 11 42E 11 0 OE+OO 2 2E 11 SOE 11 2 IE 11 1 2E 11 28E 11 6 6E 12 BSE 12 0 OE+OO 0 OE+00 0 OE+00 6 4E 11 0 OE+00 3SE 17 0 OE+00 0 OE+00
Methacryionitnle 913E+01 1 2E09 2 4E 09 1 9E09 1 4E 09 1 2E09 2 3E09 9 7E 10 6 4E 10 1 SE 09 9 0E 10 2 6E 10 2 IE 09 2 IE 09 1 IE 08 0 OE+00 4 4E-09 4 4E 09 8 IE 08 4 7E 11
Methyl Methacrylate B81E+03 SBE 10 1 2E09 9SE 10 6 7E 10 5 9E 10 1 IE 09 4 7E 10 3 IE 10 7 2E 10 43E 10 1 2E 10 1 0E09 1 0E09 5 2E-09 0 OE+00 2 1E09 2 IE 09 3 9E-08 2 3E 11
Naphthalene 5 81E+02 BSE 09 1 3E08 1 IE 08 7 8E09 6 8E-09 1 SEOB 5 5E-09 J6E09 B4E 09 SOE 09 1 4E-09 1 2E 08 1 2E 08 6 OE-08 0 OE+00 2 5E 08 2SE-08 4 5E-07 2 BE 10
Nickel 1 67E+01 1 9E0S 3 7E 08 SBE 08 BBE 10 2 IE 08 4 6E OS 1 9E-08 1 1E-08 2 6E-08 6 3E-09 3 3E 09 49E 10 4 9E 10 2SE09 5 9E-0B 1 0E09 1 0E09 1 9E08 1 IE 11
Nitrobenzene 1 B7E+02 2SE 10 51E10 42E 10 SOE 10 2 6E 10 4BE 10 2 IE 10 1 4E 10 S2E 10 1 9E 10 5 5E 11 4 4E 10 4 4E 10 2 BE-09 0 OE+00 9 4E 10 9 4E 10 1 7E-08 1 OE 11
Pentachlorophenol 5 56E+00 1 IE 08 2 3E-08 1 BE 08 1 BE 08 1 2E08 2 IE-OB 9 2E09 B 1E-09 1 4E-08 8 4E-09 2 4E 09 2 OE-08 2 OEOB 1 OE-07 0 OE+00 4 IE 08 4 IE 08 7 6E 07 4 4E 10
Phenol 6 40E+02 OBE 10 2 0E 09 1 6E-09 1 2E 09 1 0E09 1 9E 09 8 1E 10 5 4E 10 1 2E09 7SE 10 2 2E 10 1 7E-09 1 7E 09 8 9E09 0 OE+00 3 7E-09 3 7E 09 6 7E 08 3 9E 11
Phosphorus 3 33E+00 S9E 08 7SE 08 7 7E 08 0 OE+00 4 IE 08 9 BE OS 3 BE 08 2 BE OS S2E-08 1 2E0B 6SE 09 0 OE+00 0 OE+00 0 OE+00 1 2E07 0 OE+00 0 OE+00 0 OE+OO 0 OE+00
Pyndine 1 08E+02 3 2E 10 6 7E 10 S4E 10 3 9E 10 3 4E 10 BBE 10 2 7E 10 1 BE 10 41E 10 2 5E 10 7 2E 11 SBE 10 SBE 10 3 OE-09 0 OE+00 1 2E09 1 2E-09 2 2E08 1 BE 11
Selenium 6 B7E+00 7SE 10 1 4E-09 1 5E 09 0 OE+00 BOE 10 1 8E09 7 4E 10 4 4E 10 9 9E 10 2 4E 10 1 BE 10 0 OE+00 0 OE+OO 0 OE+OO 2 3E 09 0 OE+00 0 OE+00 0 OE+OO 0 OE+00
Silver S 33E+00 5 2E 10 1 OE-09 1 OE-09 B9E 12 S5E 10 1 2E 09 5 IE 10 3 0E 10 6 9E 10 1 7E 10 8 7E 11 1 BE 11 1 BE 11 6SE 11 1 BE 09 2 BE 11 2 BE 11 5 IE 10 SOE 13
Styrene 2 83E+03 2 BE 10 4 7E 10 3 8E 10 2 7E 10 2 4E 10 4 4E 10 1 9E 10 1 SE 10 2 9E 10 1 BE 10 51E 11 4 IE 10 41E10 2 1E-09 0 OE+00 BBE 10 BBE 10 1 6E 08 9 2E 12
Tetrahydrofuran 1 63E+03 S4E 10 7 IE 10 S7E 10 4 IE 10 SOE 10 B7E 10 2 9E 10 1 9E 10 4 4E 10 2 BE 10 76E 11 6 IE 10 B 1E 10 3 IE 09 0 OE+00 1 BE 09 1 3E-09 2 4E08 1 4E 11
Thallium 1 OOE+02 1 0E09 2 0E 09 2 0E 09 1 7E 11 1 IE 09 2 4E 09 1 OE 09 S9E 10 1 BE 09 3 3E 10 1 7E 10 2 6E 11 2 BE 11 1 SE 10 3 IE 09 SSE 11 SSE 11 1 0E09 SBE IB
Toluene 2 51E+0S 1 OEOS 2 IE 08 1 7E 08 1 2E0B 1 IE 08 2 OEOS BSE 09 5 BE 09 1 3E 08 7 BE 09 2 2E09 1 SEOB 1 SEOB 9 2E0S 0 OE+00 BSE 08 3 BE 08 7 OE-07 41E 10
Vinyl Chlonde 2 83E+01 2 7E 09 5SE 09 4 5E 09 3 2E-09 2 8E09 5 2E09 2 2E09 1 5E09 S4E 09 2 1E09 59E 10 4 8E09 4 8E-09 2 5E OS 0 OE+00 1 OEOB 1 OE 08 1 9E07 1 1E 10
Xylene o 1 44E+04 1 BE 09 3 7E 09 BOE 09 2 IE 09 1 9E 09 BSE 09 1 SE 09 9 8E 10 2 3E-09 1 4E 09 S9E 10 S2E 09 3 2E 09 1 6E-08 0 OE+00 6 7E 09 6 7E 09 1 2E07 7 2E 11
Zinc 6 67E+01 BBE 09 1 2E08 1 2E OS 9 5E 11 B7E 09 1 SE-OB 6 2E09 3 7E 09 S3E09 2 OE-09 1 1E09 1 4E 10 1 4E 10 73E 10 1 9E-08 SOE 10 SOE 10 SSE 09 S2E 12
trans 1 3 Dichloropropene 5 03E+01 2 2E 10 46E 10 3 7E 10 2 7E 10 2 3E 10 4 3E 10 1 9E 10 1 2E 10 2 9E10 1 7E 10 4 9E 11 40E 10 4 0E 10 2 OE-09 0 OE+00 8 4E 10 B4E 10 1 SE 08 9 0E 12
Notes
1 Chronic/Carcinogenic Toxic Screening Level = ACGIH TLV divided by 30 for noncarcinogens and 90 for carcinogens
ACGIH TLVs from 2003 TLVs and BEls for Chemical Substances and Physical Agents Amencan Council of Government Industnal Hygienists (ACGIH)
Shading indicates that Toxic Screening Level was exceeded
COST/SCHEDULE-AREA Tetra Tech NUS, Inc.
M-136 TREATMENT UNIT
3 KILOMETER GENERAL RECEPTOR GRID
100 METER INCREMENT
ATK
BRIGHAM CITY, UTAH
CONTRACT NO,
112001966
APPROVED flY
APPROVED BY
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CHECKED BY DATE
J. LUCAS 04/09/09
REVISED BY DATE
COST/SC HEDULE-AREA Tetra Tech NUS, Inc.
I P /.V-j AIL
M-225 TREATMENT UNIT
3 KILOMETER GENERAL RECEPTOR GRID
100 METER INCREMENT
ATK
BRIGHAM CITY, UTAH
CONTRACT NO
112C01966
APPROVED BY
APPROVED BY
WIND ROSE PLOT;
ATK Launch Systems
Brigham City, UT
DISPLAY.
Wind Speed
Direction (blowing from)
WIND SPEED
(m/s)
• >= 11.1
•1 8.8-11.1
5.7 - 8.8
3.6- 6.7
2 1 • 3.6 • 0.5 - 2.1
Calms 0 00%
COMMENTS: DATA PERIOD-COMPANY NAME:
1997 Onsite Meteorological Data 1997 Tetra Tech Figure 6
Jan 1 - Dec 31
00:00 - 23:00
CALM WINDS TOTAL COUNT.
0.00% 8760 hrs.
AVG WIND SPEED: DATE: PROJECT NO.:
4.03 m/s 4/8/2009 112C01986
WRPLOT View - Lakes Environmental Soltware
REVISED BY
COST^SCH E DULE-AREA Tetra Tech NUS, Inc.
PRELIMINARY ANALYSES
M-136 MAXIMUM ONSITE AND OFFSITE C3AS AND PARTICULATE
AIR CONCENTRATION AND DEPOSITION PHASE RECEPTORS
ATK
BRIGHAM CITY, UTAH
APPROVED BY
DRAWING NO
LEGEND
• • Discrete Receptor
Treatment Unit
Facility Boundary
P^GlSt'ml0«0LUkPRtT>llOKOL.APR U235 zoos PfCUMlNARYAMALVSES LAYOUT 0«1(»B JEE
LUCAS 0«/1iy09
REVISED BY DATE
COST/SCHE DULE-AREA Tetra Tech NUS, Inc.
A. •
PUfH A IL
PRELIMINARY ANALYSES
M-225 MAXIMUM ONSITE AND OFFSITE C3AS MD PARTICULATE
AIR CONCENTRATION AND DEPOSITION PHASE RECEPTORS
ATK
BRIGHAM CITY, UTAH
CONTRACT NO.
112C01966
APPROVED BY
APPROVED BY