DSHW-2018-003791 - 0901a06880805ddd

AECOM 756 E Winchester Street
Suite 400
Salt Lake City UT, 84107
www.aecom.com
801 904 4000 tel [phone] fax
\ A ( 7
Div of Was'.e !Vlanagement
and Radlatlon Control
APR 3 0 2018
DSRW-20(8 -00379'
AECOM
April 27, 2018
Attention: Mr. Phil Burns
Utah Division of Solid and Hazardous Waste
195 North 1950 West
PO Box 144880
Salt Lake City, Utah 84114-4880
RE: Payson Landfill 2017 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Mr. Burns:
AECOM is pleased to submit this 2017 Monitoring Program Groundwater Monitoring Report —
Fourth Quarter: March 2018 on behalf of Payson City Corporation.
The sampling described in this document was performed to assist the City of Payson in
complying with regulatory requirements specified by UDSHW. Currently, UDSHW requires that
groundwater samples be collected quarterly from monitoring wells MW-4, MW-5, and
MW-6 and analyzed for assessment monitoring criteria, and that monitoring well MW-3 be
sampled on a semi-annual basis for detection monitoring criteria, as defined by UDSHW.
Groundwater samples were analyzed for the constituents specified in Solid and Hazardous
Waste Rule R315-308-4 and 40 CFR Part 258 Appendix 11. The sampling results are included in
this document. Please direct any correspondence related to this document directly to Mr. Kent
Fowden, Payson City Corporation Landfill Manager.
Sincerely,
AECOM
Lawrence Cannon
Project Manager
encl: Quarterly Monitoring Report
cc; Kent Fowden
Landfill Manager, Payson City Corporation
PAYSON CITY LANDFILL
2017 / 2018 MONITORING PROGRAM
GROUNDWATER MONITORING REPORT ps4W-2015 -00379 (
FOURTH QUARTER: March 2018
Prepared for
Payson City Corporation
April 2018
Prepared by A=COM
AECOM
756 East Winchester Street, Suite 400
Salt Lake City, Utah 84107
Project 60544100
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page i
TABLE OF CONTENTS
1.0 INTRODUCTION 1
2.0 GROUNDWATER DATA COLLECTION 2
2.1 GROUNDWATER MEASUREMENT 2
2.2 FIELD SAMPLING METHODOLOGY 2
2.3 GROUNDWATER DATA QUALITY 3
2.4 CHANGE NOTICES 3
3.0 DATA EVALUATION 4
3.1 GROUNDWATER ELEVATION TRENDS 4
3.2 WATER QUALITY TRENDS 4
3.2.1 Detection Monitoring (MW-3) 5
3.2.2 Assessment Monitoring (MW-4, MW-5 and MW-6) 5
3.3 REGULATORY SUMMARY FOR ASSESSMENT MONITORING 7
3.4 QA/QC ANALYSIS 7
3.4.1 Sensitivity 7
3.4.2 Accuracy 8
3.4.3 Precision 8
3.4.4 Completeness 8
3.4.5 Representativeness 8
3.4.6 Comparability 9
4.0 STATISTICAL ANALYSIS 10
4.1 ANALYSIS OF MW-3 (DETECTION MONITORING) 10
4.2 ANALYSIS OF MW-4, MW-5, AND MW-6 (ASSESSMENT MONITORING) 10
4.2.1 Well MW-4 11
4.2.2 Well MW-5 11
4.2.3 Well MW-6 11
5.0 DISCUSSION AND FINDINGS 13
5.1 GROUNDWATER ELEVATION DATA 13
5.2 ANALYTICAL DATA 13
6.0 REFERENCES 14
AECOM
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page ii
LIST OF TABLES
Table 1-1 — 2017/2018 Monitoring Program Quarterly Groundwater Sampling Schedule
Table 3-1 — Analytical Results for General Chemistry Analytes in Groundwater
Table 3-2 — Analytical Results for Metals in Groundwater
Table 3-3 — Analytical Results for Organic Compounds in Groundwater
Table 3-4 — Assessment Monitoring Detection Summary
Table 4-1 — Assessment Monitoring Confidence Limits for Wells MW-4, MW-5, and MW-6
LIST OF FIGURES
Figure 1-1 — Regional Overview Map
Figure 1-2 — Site Map
Figure 3-1 — Groundwater Elevation Trends
Figure 3-2 — Organic Compound Concentration Trends for Monitoring Well MW-4
Figure 3-3 — Organic Compound Concentration Trends for Monitoring Well MW-5
Figure 3-4 — Organic Compound Concentration Trends for Monitoring Well MW-6
LIST OF APPENDICES
Appendix A — Regulatory Requirements
Appendix B — Field Sampling Logs
Appendix C — Data Validation Report and Analytical Laboratory Reports
Appendix D — Statistical Analyses Information
AECOM
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 1
1.0 INTRODUCTION
This report is a summary of the results for the fourth quarter of the 2017/2018 groundwater
monitoring program conducted at the Payson City Landfill on March 7, 2018.
The Payson City Landfill is located approximately four miles west of the city of Payson in Utah
County, Utah (see Figure 1-1). The site is located on the eastern side of West Mountain, in the
northwest corner of Section 14, Township 9 South, Range 1 East, Salt Lake Base and Meridian.
AECOM performs quarterly groundwater monitoring at the Payson City Landfill in accordance
with the schedule provided in Table 1-1. The monitoring well locations at the Payson City
Landfill are shown on Figure 1-2. Monitoring well MW-3 is located east of the landfill;
monitoring well MW-4 is located south of the landfill; and monitoring wells MW-5 and MW-6
are located on the north boundary of the landfill property.
Groundwater monitoring at the Payson City Landfill includes quarterly assessment monitoring
and semi-annual detection monitoring. Groundwater samples are to be collected quarterly from
monitoring wells MW-4, MW-5, and MW-6 and analyzed for assessment monitoring criteria;
and collected semi-annually from monitoring well MW-3 and analyzed for detection monitoring
criteria.
Groundwater sampling was performed in accordance with the Payson City Landfill Ground
Water Monitoring Plan (URS, 2003) and the Utah Solid and Hazardous Waste Permitting and
Management Rule under Utah Administrative Code (UAC) R315-308. During the fourth quarter,
groundwater samples were collected from wells MW-4, MW-5, and MW-6 and analyzed for the
constituents specified in UAC R315-308-4 and detected constituents listed in the Code of
Federal Regulations, Title 40, Part 258 (40 CFR Part 258) Appendix II, as required by UAC
R315-308-2(12)(d) (see Appendix A).
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 2
2.0 GROUNDWATER DATA COLLECTION
There are a total of six monitoring wells at the Payson City Landfill. Five of the wells (MW-1,
MW-3, MW-4, MW-5, and MW-6) are completed in unconsolidated materials. Unconsolidated
materials appear to be late Pleistocene Bonneville Formation, which is composed of thin beds of
offshore clay, silt, and fine sand; and Provo Formation and younger lake bottom clay, silt, and
some offshore sandbars. Well MW-2 is an exception and is completed in the Permian-
Pennsylvanian Oquirrh Formation, which is composed of sandstone, quartzite, and limestone.
Groundwater samples were collected from all required monitoring wells (MW-4, MW-5, and
MW-6) during the fourth quarter sampling event. Field parameters were measured and recorded
during the sampling of each monitoring well. Field sampling logs are provided in Appendix B.

2.1 GROUNDWATER MEASUREMENT
The depth to groundwater was measured to the nearest hundredth of a foot at each well, with the
exception of MW-1, using an electronic water level indicator. It is not possible to measure the
depth to groundwater in MW-1 because a sampling pump is lodged approximately halfway down
the well and cannot be removed. Depth to water was referenced to a surveyed measuring point at
the top of the casing to determine the water table elevation. To prevent potential cross-
contamination between monitoring points the water level indicator was decontaminated prior to
use at each well with paper towels and a solution of Alconox® detergent and tap water, followed
by a triple rinse with deionized water. Also, prior to measuring the groundwater elevation at each
well, the field sampler donned a new pair of clean nitrile gloves.

2.2 FIELD SAMPLING METHODOLOGY
Each monitoring well was purged and sampled using a dedicated sampling pump. Purge water
was discharged to the ground surface away from the wellhead. Water quality parameters were
measured in the field and included conductivity, turbidity, temperature, and pH. Water quality
parameters were measured using an Horiba U-52 multi-parameter water quality meter, the
measurements were recorded on the field sampling log forms (Appendix B). Three well casing
volumes of water were purged from each well prior to collecting the groundwater sample. The
necessary purge volume for each well was calculated based on the well casing diameter and
height of the water column in the well.
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 3
All sample containers were labeled with the proper identification at the time of sample collection
using water resistant ink. After collection, sample containers were immediately placed on ice in
an insulated cooler for preservation. A chain-of-custody record was initiated in the field and
accompanied the samples during collection, storage, transportation, and delivery to the analytical
laboratory (Appendix B). The samples were either in the possession of the field sampler or
securely stored at all times. At the end of the sampling day, groundwater samples were delivered
in custody-sealed coolers to American West Analytical Laboratories (AWAL) in Salt Lake City,
Utah for analysis. AWAL is a Utah-certified laboratory.
2.3 GROUNDWATER DATA QUALITY
To evaluate overall data quality, the following quality assurance/quality control (QA/QC)
samples were analyzed during this sampling event:
• Trip Blank — one trip blank was placed in the cooler containing samples for volatile organic
compound (VOC) analyses, and was analyzed for VOCs only;
• Field Blank — one field blank was analyzed for VOCs;
• Blind Duplicate — one sample was duplicated and analyzed for all parameters; and
• Matrix Spike/Matrix Spike Duplicate (MS/MSD) — one MS/MSD sample was analyzed for
all parameters.
The cooler temperature was measured at the time of receipt at the analytical laboratory.
2.4 CHANGE NOTICES
This section of the report is provided to present a discussion of changed conditions, deviations
from the planned work, or other events that occurred during the quarter. There were no
deviations from the monitoring plan this quarter.
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 4
3.0 DATA EVALUATION
The analytical results for monitoring wells MW-4, MW-5, and MW-6 are discussed in
Section 3.2 and the laboratory analytical report is included in Appendix C. A regulatory
summary of the quarterly monitoring is provided in Section 3.3. A data QA/QC analysis (data
validation) summary with respect to project data quality objectives is provided in Section 3.4,
with the data validation report included in Appendix C.
3.1 GROUNDWATER ELEVATION TRENDS
Figure 1-2 shows the potentiometric surface contours for the Payson City Landfill during the
fourth quarter (March 2018). Groundwater elevation data from March 2018 have been
interpreted to indicate a condition of radial flow beneath the landfill. All water level
measurements conducted in association with groundwater sampling at the Payson City Landfill
have shown similar potentiometric surface contours.
Figure 3-1 is a hydrograph that shows the groundwater elevation trend for the last twelve
sampling events (March 2014 through March 2018). Groundwater elevations in March 2018
ranged between 4,533.24 to 4,533.78 feet (ft) above mean sea level (amsl). The groundwater
elevation decreased since the last sampling event in December 2017. Over the past twelve
sampling events, groundwater elevations ranged from approximately 4,533 to 4,538 ft amsl. A
linear trendline for the groundwater elevation measurements is depicted in Figure 3-1. The
trendline is based on groundwater elevations at MW-4, the well with the groundwater elevations
at the median for most quarters. The linear trendline shows that, including seasonal fluctuations,
the groundwater elevation in MW-4 has been increasing by 0.0008 ft/day (0.1095 ft/yr).
3.2 WATER QUALITY TRENDS
The detected general chemistry analytes, total metal analytes, and organic compounds in this
quarter's groundwater samples are summarized in Tables 3-1 through 3-3, respectively. All
analytical data were validated by the project chemist and are provided in Appendix C. Results
were compared to the Utah Groundwater Protection Standards (UGWPS) in UAC R315-308-4
and UAC R315-308-5 (Appendix A). The analytical results are discussed further in Sections
3.2.1 and 3.2.2.
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018 Page 5
3.2.1 Detection Monitoring (MW-3)
Detection monitoring of well MW-3 occurs on a semi-annual basis, during the first and third
quarters. A groundwater sample was not collected at MW-3 during the fourth quarter (March
2018).
3.2.2 Assessment Monitoring (MW-4, MW-5 and MW-6)
The samples collected from wells MW-4, MW-5, and MW-6 were analyzed for the constituents
specified in UAC R315-308-4 and in 40 CFR Part 258 Appendix II (see Appendix A). Various
general chemistry analytes, metal analytes, and organic compounds were detected, as
summarized in Tables 3-1, 3-2, and 3-3, and as discussed below.
3.2.2.1 General Chemistry and Total Metal Analytes
General chemistry results for the groundwater samples collected from wells MW-4, MW-5, and
MW-6 are presented in Table 3-1. Only cyanide has an established UGWPS. Analysis for
cyanide in groundwater from assessment wells during the fourth quarter was not required
because it was not detected during the first quarter. The pH in these samples ranged from 6.62 to
7.36. Metals results are presented in Table 3-2. Of the 23 metals analyzed for in the groundwater
samples, 14 metals were detected. All metal results were below their respective UGWPS.
3.2.2.2 Organic Compounds
UAC R315-308-4 VOCs. The results for detected VOCs are presented in Table 3-3. The
groundwater samples from MW-4 and MW-6 had no detectable VOCs. In the sample from
MW-5, the cis-1,2-dichloroethene concentration was 5.18 µg/L, below the UGWPS of 70 µg/L,
and the methylene chloride concentration was 2.56 µg/L, below the UGWPS of 5 ttg/L. No other
VOCs were detected in the sample from well MW-5.
40 CFR Part 258 Appendix II Semi-Volatile Organic Compounds (SVOCs). The results for
detected SVOCs are presented in Table 3-3. The groundwater samples from MW-4 and MW-5
had no detectable SVOCs. In the sample from MW-6, the acetophenone concentration was 12.8
ttg/L. There is no UGWPS for acetophenone. No other SVOCs were detected in the sample from
well MW-6.
40 CFR Part 258 Appendix II Herbicides, Pesticides, and Polychlorinated Biphenyls (PCBs).
Analysis for herbicides, pesticides, and polychlorinated biphenyls (PCBs) in groundwater from
assessment wells during the fourth quarter was not required because these analytes were not
detected during the first quarter.
AECOM
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 6
3.2.2.3 Organic Compound Concentration Trends
Organic compounds that are repeatedly detected in groundwater are tracked using trend graphs.
Figures 3-2 through 3-4 show concentration trends for organic compounds detected over the past
three years (March 2014 through March 2018) for wells MW-4, MW-5, and MW-6.
Well MW-4. Organic compounds detected in groundwater samples from well MW-4
over the past three years include bis(2-ethylhexyl)phthalate (UGWPS of 6 µg/L).
Bis(2-ethylhexyl)phthalate has occasionally been detected in groundwater samples from well
MW-4; however, it was not detected this quarter. Concentration trends over the past three years
for these analytes are presented on Figure 3-2.
Well MW-5. Organic compounds detected in groundwater samples from well MW-5 over the
past three years include cis-1,2-dichloroethene, methylene chloride, bis(2-ethylhexyl)phthalate,
and 1,1-dichloroethane. Concentration trends over the past three years for these constituents are
presented on Figure 3-3.
Concentrations of cis-1,2-dichloroethene and methylene chloride in well MW-5 fluctuate
seasonally and appear to inversely correlate with groundwater levels. The cis-1,2-dichloroethene
concentrations have remained at or below 9.69 µg/L, below the UGWPS of 70 µg/L. Over the
past three years, the methylene chloride concentrations have decreased from 7.72 to 2.56 µg/L, a
concentration below the UGWPS of 5 µWI—
Over the past twelve sampling events, bis(2-ethylhexyl)phthalate was detected five times
between 5.8 µg/L and 10.2 µg/L, the UGWPS for bis(2-ethylhexyl)phthalate is 6 µg/L, however,
it was not detected this quarter. Bis(2-ethylhexyl)phthalate is known to be a common laboratory
contaminant. 1,1-dichlorethane was detected in September 2014 and September 2015 at
concentrations below the UGWPS of 4,000 µg/L, and has decreased to non-detectable levels
since.
Well MW-6. Organic compounds detected in samples collected from well MW-6 over the past
three years include bis(2-ethylhexyl)phthalate. The concentration trend over the past three years
is presented on Figure 3-4. Bis(2-ethylhexyl)phthalate has occasionally been detected in
groundwater samples from well MW-6; however, it was not detected for this quarter.
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 7

3.3 REGULATORY SUMMARY FOR ASSESSMENT MONITORING
As required by Utah Solid and Hazardous Waste Permitting and Management Rules for
Groundwater Monitoring Requirements under UAC R315-308-2(12)(d)(ii), assessment
monitoring wells are sampled quarterly for the full list of constituents in UAC R315-308-4 and
annually for the full list of constituents in 40 CFR Part 258 Appendix II. Constituents on the
Appendix II list detected in assessment wells will be analyzed in subsequent quarterly sampling
events. As required, assessment monitoring during the first quarter of each year will resume with
the full list of constituents in UAC R315-308-4 and in 40 CFR Part 258 Appendix II. Based on
the detections of Appendix II constituents in assessment wells during first quarter sampling, the
planned monitoring at assessment wells for 2017/2018 is presented in Table 3-4.

3.4 QA/QC ANALYSIS
The 2017/2018 monitoring program fourth quarter Payson City Landfill data are considered
acceptable for use in meeting project objectives, as qualified. A general overall assessment of
data quality indicators is provided below and described in more detail in the Data Validation
Report (DVR) in Appendix C.
3.4.1 Sensitivity
With the exceptions list below, the reporting limits satisfied the ground water protection
standards required in the Utah Solid Hazardous Waste Permitting and Management Rules R315-
308-4 and R315-308-5.
The dinoseb (a herbicide) reporting limit for the samples associated with this data package
exceeded the groundwater protection standard of 7.00 1.1g/L required for Utah Solid Hazardous
Waste Permitting and Management Rules R315-308-5. As the dinoseb results were reported as
non-detect with reporting limits above the required concentration, these results will need to be
evaluated by the end-user with respect to project objectives.
Due to method blank contamination, the bis(2-ethylhexyl)phthalate reporting limit for sample
MW-5 exceeded the groundwater protection standard of 6.00 [tg/L required for Utah Solid
Hazardous Waste Permitting and Management Rules R315-308-5. As the bis(2-
ethylhexyl)phthalate result was reported as non-detect with a reporting limit above the required
concentration, this result will need to be evaluated by the end-user with respect to project
objectives.
AECOM
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter' March 2018
Page 8
3.4.2 Accuracy
Accuracy is defined as the degree of agreement of a measurement to an accepted reference or
true value. Accuracy was measured as the percent recovery (%R) of an analyte in a reference
standard or spiked sample. The laboratory control sample (LCS) spike recoveries and surrogate
recoveries satisfied the evaluation criteria.
With the exceptions listed in Section 3 of the DVR, the MS/MSD recoveries for parameters
spiked at an appropriate level (greater than or equal to 25% of the parent sample concentration)
satisfied the evaluation criteria. The overall level of accuracy demonstrated by the analyses is
considered acceptable.
3.4.3 Precision
Precision is defined as the agreement between a set of replicate measurements without
assumption or knowledge of the true value. Precision of laboratory measurements was evaluated
by the comparison of method duplicate results and matrix spike (MS) to matrix spike duplicate
(MSD) results.
With the exception listed in Section 3 of the DVR, the MS/MSD results for parameters spiked at
an appropriate level (greater than or equal to 25% of the parent sample concentration) satisfied
the precision evaluation criteria. Method duplicate results satisfied the precision evaluation
criteria and the overall level of precision demonstrated by total dissolved solids (TDS) and pH
analyses are considered acceptable. The field duplicate results satisfied the precision evaluation
criteria. As such, the overall level of precision with respect to the matrix is considered
acceptable.
3.4.4 Completeness
Completeness is defined as the ratio of the number of valid analytical results (valid analytical
results include values qualified as estimated) to the total number of analytical results requested
on samples submitted for analysis. The results were considered usable for meeting project
objectives. As such, the overall analytical completeness was 100%.
3.4.5 Representativeness
Representativeness is the degree to which data accurately and precisely represent a characteristic
of a population, parameter variations at a sampling point, or an environmental condition.
Representativeness was maintained during the sampling effort by completing the sampling using
similar sampling procedures.
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 9
3.4.6 Comparability
Comparability expresses the confidence with which one data set can be compared to another.
Comparability can be related to accuracy and precision because these quantities are measures of
data reliability. Data are comparable if collection techniques, measurement procedures, methods
and reporting are equivalent for the samples within a sample set. To maximize comparability, all
samples covered by this report were collected and analyzed in accordance with prescribed
quality assurance and quality control measures. Additionally, as acceptable levels of overall
accuracy and precision were attained, the data within this set are considered comparable to one
another.
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 10
4.0 STATISTICAL ANALYSIS
Beginning in December 2001, semi-annual detection sampling has been conducted for well
MW-3 as specified in UAC R315-308-2(4), and quarterly assessment monitoring sampling has
been conducted for wells MW-4, MW-5 and MW-6 as specified in UAC R315-308-2(12)(d).
Both rules require a statistical analysis of the analytical data derived from the sampling, but for
different purposes. The purpose of the detection monitoring data is to determine whether there is
a statistically significant increase over background concentrations in any of the sample analytes,
whereas the analysis of the assessment monitoring data is meant to provide a comparison of
sample concentrations against the UGWPS listed in UAC R315-308-4 and UAC R315-308-5.
4.1 ANALYSIS OF MW-3 (DETECTION MONITORING)
Detection monitoring of well MW-3 occurs on a semi-annual basis, during the first and third
quarters. A groundwater sample was not collected at well MW-3 during the fourth quarter
(March 2018) therefore, a statistical evaluation for well MW-3 was not performed.
4.2 ANALYSIS OF MW-4, MW-5, AND MW-6 (ASSESSMENT MONITORING)
To assess the potential site impact due to apparent releases, detected analytes were considered on
the basis of individual wells. When the measured concentration of a constituent in a particular
well was equal to or exceeded the UGWPS in any of the four most recent sampling events, a
confidence interval was computed for the well/constituent using the measured concentrations for
the four most recent samples from the well. Calculations were made using the SanitasTM software.
The Sanitas built-in default statistical settings based on the recommendations of the Unified
Guidance (USEPA, 2009) were used for the statistical evaluation of data. When goodness-of-fit
testing indicates a lack of statistical evidence for rejecting a hypothesis of normality for either
the data themselves or a transform of the data (e.g., the logarithm of the data), the calculations
are based on the single sample t-test for the mean (Gilbert, 1987; Sanitas Technologies, 2009)
using the default level of significance of a=0.01. When a hypothesis of normality can be
rejected, the confidence interval is computed non-parametrically with the seven most recent
samples using a test based on the binomial distribution (Conover, 1999; Sanitas Technologies,
2009). Results of the statistical analysis are summarized in Table 4-1.
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 11
4.2.1 Well MW-4
Analytes with concentrations that exceeded the UGWPS during the most recent four sampling
events at MW-04 include nickel. The nickel concentrations during this period ranged from 0.058
to 0.118 mg/L, with two result exceeding the UGWPS of 0.1 mg/L. Therefore, statistical
evaluations were completed for MW-4 nickel results.
The data for nickel were normally distributed so the confidence intervals were computed
parametrically. The lower confidence limit (LCL) for the mean was 0.01886 mg/L, below the
UGWPS of 0.1 mg/L. The statistical analysis indicated that the landfill is in compliance with
UAC R315-308 for nickel at well MW-4. Details of the statistical analysis are provided in
Appendix D.
4.2.2 Well MW-5
Bis(2-ethylhexyl)phthalate was the only analyte with a concentration that exceeded the UGWPS
during the most recent four sampling events at MW-5. The bis(2-ethylhexyl)phthalate
concentrations ranged from non-detect to 10.2 µg/L, with one result exceeding the UGWPS of 6
µg/L. Therefore, statistical evaluations were completed for MW-5 bis(2-ethylhexyl)phthalate
results.
The bis(2-ethylhexyl)phthalate data were normally distributed so the confidence interval was
computed parametrically. The LCL for the mean was -2.629 µg/L, below the UGWPS of 6 µg/L.
The statistical analysis indicated that the landfill is in compliance with UAC R315-308 for
bis(2-ethylhexyl)phthalate at well MW-5. Details of the statistical analysis are provided in
Appendix D.
4.2.3 Well MW-6
Analytes with concentrations that exceeded the UGWPS during the most recent four sampling
events at MW-06 include chromium and nickel. The chromium concentrations ranged from
0.00652 to 0.108 mg/L, with one result exceeding the UGWPS of 0.1 mg/L. The nickel
concentrations ranged from 0.0257 to 0.107 mg/L, with one result exceeding the UGWPS of
0.1 mg/L. Therefore, statistical evaluations were completed for MW-6 chromium and nickel.
The data for chromium and nickel were normally distributed so the confidence intervals were
computed parametrically. For chromium, the LCL of the mean was -0.06435 mg/L, below the
UGWPS of 0.1 mg/L. For nickel, the LCL for the mean was -0.0324 mg/L, below the UGWPS
of 0.1 mg/L. The statistical analysis indicated that the landfill is in compliance with
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 12
UAC R315-308 for chromium and nickel at well MW-6. Details of the statistical analysis are
provided in Appendix D.
AECOM
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 13
5.0 DISCUSSION AND FINDINGS
The findings for the fourth quarter of the 2017/2018 monitoring program groundwater elevation
data, analytical data review, and statistical analysis are presented in the sections below.
5.1 GROUNDWATER ELEVATION DATA
Groundwater elevation data continue to support the hypothesis of radial flow beneath the landfill
(see Figure 1-2). Groundwater elevations ranged from 4,533.24 to 4,533.78 ft amsl this quarter;
and ranged from approximately 4,533 and 4,538 ft amsl over the past twelve sampling events.
The groundwater elevation trends show seasonal fluctuation with an overall slight decrease in
groundwater level (see Figure 3-1).
5.2 ANALYTICAL DATA
The fourth quarter 2017/2018 analytical data were considered
acceptable for use in meeting project objectives, as qualified
(see Appendix C).
Detection monitoring samples were not collected from well
MW-3 this quarter.
Assessment monitoring samples were collected from wells
MW-4, MW-5, and MW-6; and analyzed for the constituents
specified in UAC R315-308-4 and 40 CFR Part 258 Appendix
II. All detected analytes had concentrations below the
Detection Monitoring
MW-3
• No sample collected at MW-3
this quarter.
AssessmeOlylonitoying
MW-4
UGWPS were exceeded this
quarter.
MW-5
• No UGWPS were exceeded this
quarter. „ MW-6
• No UGWPS wai'exceeded this
qtarter. „
UGWPS this quarter (see Tables 3-1, 3-2 and 3-3). A statistical analysis was performed on
analytes for MW-4, MW-5, and MW-6 with results equal to or exceeding the UGWPS over the
most recent four sampling events. The LCLs of the means were below the UGWPS in each
statistically analyzed case.
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
Page 14
6.0 REFERENCES
Conover, W.J., 1999. Practical Nonparametric Statistics. John Wiley & Sons, New York.
Gilbert, R.O., 1987. Statistical Methods for Environmental Pollution Monitoring. John Wiley &
Sons, New York.
Sanitas Technologies, 2009. Sanitas Statistical Software Version 9.0.
United States Environmental Protection Agency (USEPA), 2009. Statistical Analysis of
Groundwater Monitoring Data at RCRA Facilities—Unified Guidance. EPA 530-R-09-0007.
March 2009.
URS, 2003. Payson City Landfill Ground Water Monitoring Plan, April 2003.
AECOM
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
TABLES
AECOM
NUM in MTh MO MI
TABLE 1-1
2017-2018 Monitoring Program Quarterly Groundwater Sampling Schedule
,‘•
SamphzgSebedl r ,
, pa* Da . • :- ..,?' 1W41 'A
First Quarter June 2017
UAC R315-308-4 full list X X X X
40 CFR Part 258 Appendix II full list X X X
Second Quarter September 2017
UAC R315-308-4 full list X X X
40 CFR Part 258 Appendix II; detects only X X X
Third Quarter December 2017
UAC R315-308-4 full list X X X X
40 CFR Part 258 Appendix II; detects only X X X
Fourth Quarter March 2018
UAC R315-308-4 full list X X X
40 CFR Part 258 Appendix II; detects only X X X
Notes:
I Well MW-3 is scheduled for semi-annual detection monitoring.
2 Wells MW-4, MW-5, and MW-6 are scheduled for quarterly groundwater assessment monitoring.
In OM —118— SW MI MI MN —MO— MN MI
TABLE 3-1
Analytical Results for General Chemistry Analytes in Groundwater
Analyte
Coneentration2 (Log/L)
UGWPS1 MW-3 MW-4 MW-5 MW-6
NS 3/7/2018 3/7/2018 3/7/2018
Ammonia (as N) None NS < 0.0500 0.126 J 0.096 J
Bicarbonate (as CaCO3) None NS 326 748 436
Carbonate (as CaCO3) None NS < 10.0 < 10.0 < 10.0
Chemical Oxygen Demand (COD) None NS < 10.0 26 < 10.0
Chloride None NS 91.2 252 178
Nitrate (as N) None NS 1.02 J 13.1 J 0.514 J
pH (pH units) None NS 7.36 6.62 6.81
Sulfate None NS 58 322 82.6
Total Dissolved Solids (TDS) None NS 472 1620 828
Total Organic Carbon (TOC) None NS 1.36 11.7 1.74
Notes:
UGWPS from Utah Administrative Code R315-308-4 and -5.
2 Non-detected results are reported as less than the reporting limit.
mg/L — milligrams per liter
NS — not sampled
UGWPS — Utah Groundwater Protection Standard
Data Qualifiers:
J — The associated value is an estimated quantity.
U — The analyte was analyzed for, but was not detected above the level of the
associated value. The associated value is either the sample quantitation limit or the
sample detection limit.
UJ — The analyte was analyzed for, but was not detected. The associated value is an
estimate and may be inaccurate or imprecise.
OM MI MI MI MI MI MI SIMONINIMIIIMMIINIIIMION
TABLE 3-2
Analytical Results for Metals in Groundwater
Analyte
Concentration (ing/L)2'3
13GWPS1 MW-3 MW-4 MW-5 MW-6
NS 3/7/2018 , 3f1/2018 37i20t 8
Antimony 0.006 NS < 0.00200 < 0.00200 < 0.00200
Arsenic 0.01 NS < 0.00200 0.00575 < 0.00200
Barium 2 NS 0.109 0.0717 0.0686
Beryllium 0.004 NS < 0.00200 < 0.00200 < 0.00200
Cadmium 0.005 NS < 0.000500 < 0.000500 < 0.000500
Calcium None NS 93 209 132
Chromium 0.1 NS 0.00277 < 0.00200 0.0543
Cobalt 2 NS < 0.00400 < 0.00400 < 0.00400
Copper 1.3 NS < 0.00200 0.00511 0.0042
Iron None NS 0.401 < 0.100 0.826
Lead 0.015 NS < 0.00200 < 0.00200 < 0.00200
Magnesium None NS 34.6 107 49.5
Manganese None NS 0.0429 0.0725 0.0419
Mercury 0.002 NS < 0.000150 < 0.000150 < 0.000150
Nickel 0.1 NS 0.058 0.0256 0.0584
Potassium None NS 10.3 44 13.4
Selenium 0.05 NS < 0.00200 < 0.00200 0.00252
Silver 0.1 NS < 0.00200 < 0.00200 < 0.00200
Sodium None NS 68.9 212 105
Thallium 0.002 NS < 0.00200 < 0.00200 < 0.00200
Tin 21.9 NS < 0.500 < 0.500 < 0.500
Vanadium 0.3 NS < 0.00500 0.00857 < 0.00500
Zinc 5 NS < 0.00500 0.0115 0.0228
Notes
UGWPS from Utah Administrative Code R315-308-4 and -5
2 Non-detected results are reported as less than the reporting limit
3 Bolded and highlighted results meet or exceed the UGWPS
mg/L - milligrams per liter
NS - not sampled
UGWPS - Utah Groundwater Protection Standard
Data Qualifiers
J - The associated value is an estimated quantity
U - The analyte was analyzed for, but was not detected above the level of the
associated value The associated value is either the sample quantitation limit
or the sample detection limit
UJ - The analyte was analyzed for, but was not detected The associated
value is an estimate and may be inaccurate or imprecise
MI SIM MI MB OM
TABLE 3-3
Analytical Results for Organic Compounds in Groundwater
Analytel
Concentration (p, '4 '
UGIVPS2 MW-3 I MW-4 MW-5 MW-6
NS 3/7/2018 3/7/2018 3/7/2018
VOCs
cis -1,2-Dichloroethene 70 NS < 2.00 5.18 < 2.00
Methylene Chloride 5 NS < 2.00 2.56 < 2.00
SVOCs
Acetophenone None NS < 9.69 < 9.69 12.8
Notes:
Only analytes detected at or above the report limit are listed.
2 UGWPS from Utah Administrative Code R315-308-4 and -5.
3 Non-detected results are reported as less than the reporting limit.
4 Bolded and highlighted results meet or exceed the UGWPS.
pig/L — micrograms per liter
NS — not sampled
SVOCs — semi-volatile organic compounds
UGWPS — Utah Groundwater Protection Standard
VOCs — volatile organic compounds
Data Qualifiers:
J — The associated value is an estimated quantity.
U — The analyte was analyzed for, but was not detected above the level of the
associated value. The associated value is either the sample quantitation limit
or the sample detection limit.
UJ — The analyte was analyzed for, but was not detected. The associated
value is an estimate and may be inaccurate or imprecise.
MN MTh MI Ili INNIONIM MI MOM OW MOM-
TABLE 3-4
Assessment Monitoring Detection Summary
Analyte Group
ist Qtr
Jun-17
2nd Qtr
Sep-17
3rd Qtr
Det-17
4th Qtr
Mar-18
MW-4 MW-5 MW-6 MW-4 MW-5 MW-6 MW-4 MW-5 MW-6 MW-4 MW-5 MW-6
Required Quarterly General Chemistry
Metals
VOCs
V
V
0
V
V
V
V
V
0
V
V
0
V
V
V
V
V
0
V
V
0
V
V
V
V
V
0
V
V
0
V
V
V
V
V
0
40 CFR Part 258
Appendix II
SVOCs
Herbicides
Pesticides
PCBs
Cyanide
Sulfide
V
0
0
0
0
0
V
0
0
0
0
0
V 0 V 0 0 V 0 0 V 0
Notes:
NS — will not be sampled
PCBs — polychlorinated biphenyls
SVOCs — semi-volatile organic compounds
VOCs — volatile organic compounds
V detected
0 not detected
was not sampled
as am mum— AM
TABLE 4-1
Assessment Monitoring Confidence Limits for Wells MW-4, MW-5, and MW-6
Well Constituent UGWPS
Number
of
Samples
Sample
Mean
Samp le
Std Ðev UCL LCL
LCL
exceeded
UGWPS?
MW-4 Nickel 0.1 mg/L 4 0.08535 mg/L 0.02929 mg/L 0.1518 mg/L 0.01886 mg/L No
MW-5 Bis(2-ethylhexyl)
phthalate 6 ug/L 4 5.434 ug/L 3551 tig/L 13.5 ug/L -2.629 tig/L No
MW-6 Chromium 0.1 mg/L 4 0.04431 mg/L 0.04786 mg/L 0.153 mg/L -0.06435 mg/L No
MW-6 Nickel 0.1 mg/L 4 0.0544 mg/L 0.03823 mg/L 0.1412 mg/L -0.0324mg/L No
otes:
Statistics were performed when the measured concentration was equal to or exceeded the UGWPS in any of the four most recent sampling events.
mg/L — milligrams per liter
pg/L — micrograms per liter
LCL — lower confidence limit
Std Dev — standard deviation
UCL — upper confidence limit
UGWPS — Utah groundwater protection standard
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
FIGURES
AECOM
- - -- ---- - --- - ----
FIGURE 3-2
Organic Compound Concentration Trends for Monitoring Well MW-4
10
8
-~ t)J) 6 ::1. -= .5; .... ~ i. .... = 4 ~ ~ = 0 u
2
0
Mar-14 Jun-14 Sep-14 Dec-14 Mar-1 5 Jun-1 5 Sep-1 5 Dec-1 5 Mar-16 Jun-1 6 Sep-1 6 Dec-1 6 Mar-17 Jun-17 Sep-1 7 Dec-17 Mar-1 8
Notes:
ft amsl -feet above mean sea level
µg/L -micrograms per liter
1. Concentrations less than the reporting limit are plotted as half of the reporting limit.
2. Bis(2-ethylhexyl)phthalate is a 40 CFR Part 258 Appendix II listed semi-volatile
organic compound, which is not analyzed every quarter. For more information on the
analysis of these compounds, refer to the respective quarterly monitoring report.
3. The Utah Groundwater Protection Standards are listed in the legend.
Date
-+-Bis(2-ethylhexyl)phthalate (6 µg/L)
-a-Groundwater Elevation
- --
4,540
4,538
4,536
~
4,534 :., -~ .,
t"'" 4,532 ~ < ~
4,530 t_'!"j ;-< :.,
4,528 -o· = -4,526 :::,
:.,
9 r,,
4,524 --
4,522
4,520
- - -- --- -- --------
FIGURE 3-3
Organic Compound Concentration Trends for Monitoring Well MW-5
20 4,540
18 4,538
16 4,536
~
14 4,534 ~ -..... ('I) ~ "'I
~ t"" :::1. 12 4,532 ('I)
'-" < = ('I) --~ M .... 10 4,530 c,: ;-I. < .... ~ = ..... Qi 8 4,528 o· (j = = 0 -u 6 4,526 ::;.,
~
9 ~ 4 4,524 '-"
2 4,522
0 4,520
Mar-1 4 Jun-14 Sep-1 4 Dec-1 4 Mar-1 5 Jun-15 Sep-1 5 Dec-15 Mar-16 Jun-16 Sep-1 6 Dec-16 Mar-17 Jun-17 Sep-1 7 Dec-1 7 Mar-18
Notes:
ft amsl -feet above mean sea level
µg/L-micrograms per liter
1. Concentrations less than the reporting limit are plotted as half of the reporting limit.
2. Bis(2-ethylhexyl)phthalate is a 40 CFR Part 258 Appendix II listed semi-volatile
organic compound, which is not analyzed every quarter. For more information on the
analysis of this compound, refer to the respective quarterly monitoring report.
3. The Utah Groundwater Protection Standards are listed in the legend.
Date
-B-I, 1-Dichloroethane (4,000 µg/L) --+-cis-1 ,2-Dichloroethene (70 µg/L)
~ Methylene chloride (5 µg/L) --e--Bis(2-ethylhexyl)phthalate (6 µg/L)
--a-Groundwater Elevation
--
- - ------ - --- - ----
FIGURE 3-4
Organic Compound Concentration Trends for Monitoring Well MW-6
20 4,540
18 4,538
16 4,536
14 4,534 -~ bl) 12 4,532 :::1.. '-" = .;; IO 4,530 -~ --8 = 4,528
~ tJ = 0 6 4,526 u
4 4,524
2 4,522
0 +---T---T---.-----,.-----,----,----,,----,.----,-----,---.......---...... --...... --...... --....------'-4,520
Mar-1 4 Jun-14 Sep-14 Dec-14 Mar-15 Jun-15 Sep-15 Dec-1 5 Mar-16 Jun-16 Sep-1 6 Dec-16 Mar-17 Jun-17 Sep-1 7 Dec-17 Mar-1 8
Notes:
ft amsl -feet above mean sea level
µg/L -micrograms per liter
1. Concentrations less than the reporting limit are plotted as half of the reporting limit.
2. Bis(2-ethylhexyl)phthalate is a 40 CFR Part 258 Appendix II listed semi-volatile
organic compound, which is not analyzed every quarter. For more information on the
analysis of this compound, refer to the respective quarterly monitoring report.
3. The Utah Groundwater Protection Standards are listed in the legend.
Date
_._ Bis(2-ethylhexyl)phthalate (6 µg/L) ~Groundwater Elevation
~ ~ -fD '"I
~ fD < ~
tr:! ;-< ~ -s· = -=-~
3 "' C:
--
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
APPENDIX A
REGULATORY REQUIREMENTS
AECOM
R315. Environmental Quality, Waste Management and Radiation Control,
Waste Management.
R315-308. Ground Water Monitoring Requirements.
R315-308-1. Applicability.
(1) Each existing landfill, pile, or land treatment disposal
facility that is required to perform ground water monitoring shall
comply with the ground water monitoring requirements according to the
compliance schedule as established by the Director during the
permitting or the permit renewal process.
(2) Prior to the acceptance of waste, each new landfill, pile,
or land treatment disposal facility that is required to perform ground
water monitoring shall have:
(a) a site specific ground water monitoring plan approved by
the Director; and
(b) the ground water monitoring system complete and operational.
(3) Ground water monitoring requirements may be waived by the
Director if the owner or operator of a solid waste disposal facility
can demonstrate that there is no potential for migration of hazardous
constituents from the facility to the ground water during the active
life of the facility and the post-closure care period. This
demonstration must be certified by a qualified ground-water scientist
and approved by the Director, and must be based upon:
(a) site-specific field collected measurements, sampling, and
analysis of physical, chemical, and biological processes affecting
contaminant fate and transport; and
(b) contaminant fate and transport predictions that maximize
contaminant migration and consider impacts on human health and the
environment.
(4) Once a ground water monitoring system and program has been
established at a disposal facility, ground water monitoring shall
continue to be conducted throughout the active life, closure, and
post-closure care periods as specified by the Director.
(5) A facility that has a ground water monitoring alternative
approved under Subsection R315-302-1(2) (e)(vi) is subject to the
standards specified in Subsection R315-303-2(1) and the approved
alternative shall be revoked by the Director if the operation of the
facility impacts groundwater.
R315-308-2. Ground Water Monitoring Requirements.
(1) Each facility owner or operator that is required to conduct
ground water monitoring shall formulate a ground water monitoring plan
that addresses the requirements of Section R315-308-2.
(2) The ground water monitoring system must consist of at least
one background or upgradient well and two downgradient wells, installed
at appropriate locations and depths to yield groundwater samples from
the uppermost aquifer and all hydraulically connected aquifers below
the facility, cell, or unit. The downgradient wells shall be
designated as the point of compliance and must be installed at the
closest practicable distance hydraulically down gradient from the unit
boundary not to exceed 150 meters (500 feet) and must also be' on the
property of the owner or operator:
(a) the upgradient well must represent the quality of background
water that has not been affected by leakage from the active area; and
(b) the downgradient wells must represent the quality of ground
water passing the point of compliance. Additional wells may be
required by the Director in complicated hydrogeological settings or
to define the extent of contamination detected.
(3) All monitoring wells must be cased in a manner that maintains
the integrity of the monitoring well bore hole. This casing must allow
collection of representative ground water samples. Wells must be
constructed in such a manner as to prevent contamination of the samples,
the sampled strata, and between aquifers and water-bearing strata.
All monitoring wells and all other devices and equipment used in the
monitoring program must be operated and maintained so that they perform
to design specifications throughout the life of the monitoring program.
(4) The ground water monitoring program must include at a
minimum, procedures and techniques for:
(a) well construction and completion;
(b) decontamination of drilling and sampling equipment;
(c) sample collection;
(d) sample preservation and shipment;
(e) analytical procedures and quality assurance;
(f) chain of custody control or sample tracking, as approved
by the Director; and
(g) procedures to ensure employee health and safety during well
installation and monitoring.
(5) Each facility shall utilize a laboratory, that is certified
by the state for the test methods used, to complete tests, using methods
with appropriate detection levels, on samples for the following:
(a) during the first year of facility operation after wells are
installed or an alternative schedule as approved by the Director, a
minimum of eight independent samples from the upgradient and four
independent samples from each downgradient well for all parameters
listed in Section R315-308-4 to establish background concentrations;
(b) after background levels have been established, a minimum of one sample, semiannually, from each well, background and
downgradient, for all parameters listed in Section R315-308-4 as a
detection monitoring program;
(i) In the detection monitoring program, the owner or operator
must determine ground water quality at each monitoring well on a
semiannual basis during the life of an active area, including the
closure period, and the post-closure care period.
(ii) The owner or operator must express the groundwater quality at each monitoring well in a form appropriate for the determination
of statistically significant changes;
(c) field-measured pH, water temperature, and water conductivity
must accompany each sample collected;
(d) analysis for the heavy metals and the organic constituents
from Section R315-308-4 shall be completed on unfiltered samples; and
(e) the Director may specify additional or fewer constituents
depending upon the nature of the ground water or the waste on a site
specific basis considering:
(i) the types, quantities, and concentrations of constituents
in wastes managed at the landfill;
(ii) the mobility, stability, and persistence of waste
constituents or their reaction products in the unsaturated zone beneath
the landfill;
(iii) the detectability of indicator parameters, waste
constituents, and reaction products in the ground water; and
(iv) the background concentration or values and coefficients
of variation of monitoring parameters or constituents in the ground
water.
(f) The following information shall be placed in the facility's
operating record and a copy submitted to the Director as the ground
water monitoring results to be included in the annual report required
by Subsection R315-302-2(4):
(i) a report on the procedures, including the quality
control/quality assurance, followed during the collection of the ground
water samples;
(ii) the results of the field measured parameters required by
Subsections R315-308-2(5) (c) and R315-308-2(7);
(iii) a report of the chain of custody and quality
control/quality assurance procedures of the laboratory;
(iv) the results of the laboratory analysis of the constituents
specified in Section R315-308-4 or an alternative list of constituents
approved by the Director:
(A) the results of the laboratory analysis shall list the
constituents by name and CAS number; and
(B) a list of the detection limits and the test methods used;
and
(v) the statistical analysis of the results of the ground water
monitoring as required by Subsection R315-308-2(8).
(vi) The results of the ground water monitoring may be submitted
in electronic format.
(6) After background constituent levels have been established,
a groundwater quality protection standard shall be set by the Director
which shall become part of the ground water mo-nitoring plan. The ground
water quality protection standard will be set as follows.
(a) For constituents with background levels below the standards
listed in Section R315-308-4 or as listed in Section R315-308-5, which
presents the ground water protection standards that are available for
the constituents listed as Appendix II in 40 CFR 258, the ground water
quality standards of Sections R315-308-4 and R315-308-5 shall be the
ground water quality protection standard.
(b) If a constituent is detected and a background level is
established but the ground water quality standard for the constituent
is not included in Section R315-308-4 or Section R315-308-5 the ground
water quality protection standard for that constituent shall be set
according to health risk standards.
(c) If a constituent is detected and a background level is
established and the established background level is higher than the
value listed in Section R315-308-4, R315-308-5 or the level established
according to Subsection R315-308-2(6) (b), the ground water quality
protection standard shall be the background concentration.
(7) The ground water monitoring program must include a
determination of the ground water surface elevation each time ground
water is sampled.
(8) The owner or operator shall use a statistical method for
determining whether a significant change has occurred as compared to
background. The Director will approve such a method as part of the
ground water monitoring plan. Possible statistical methods include:
(a) a parametric analysis of variance (ANOVA) followed by
multiple comparisons procedures to identify statistically significant
evidence of contamination. The method must include estimation and
testing of the contrasts between each compliance well's mean and the
background mean levels for each constituent;
(b) an analysis of variance (ANOVA) based on ranks followed by
multiple comparisons procedures to identify statistically significant
evidence of contamination. The method must include estimation and
testing of the contrasts between each compliance well's median and
the background median levels for each constituent;
(c) a tolerance or prediction interval procedure in which an
interval for each constituent is established from the distribution
of the background data, and the level of each constituent in each
compliance well is compared to the upper tolerance or prediction limit;
(d) a control chart approach that gives control limits for each
constituent; or
(e) another statistical test method approved by the Director.
(9) For both detection monitoring, as described in Subsection
R315-308-2(5), and assessment monitoring, as described in Subsection
R315-308-2(12), the Director may specify additional or fewer sampling
and analysis events, no less than annually, depending upon the nature
of the ground water or the waste on a site-specific basis considering:
(a) lithology of the aquifer and unsaturated zone;
(b) hydraulic conductivity of the aquifer and unsaturated zone;
(c) ground water flow rates;
(d) minimum distance between upgradient edge of the landfill
unit and downgradient monitoring well screen (minimum distance of
travel); and
(e) resource value of the aquifer.
(10) The owner or operator must determine and report the ground
water flow rate and direction in the upper most aquifer each time the
ground water is sampled.
(11) If the owner or operator determines that there is a
statistically significant increase over background in any parameter
or constituent at any monitoring well at the compliance point, the
owner or operator must:
(a) within 14 days of the completion of the statistical analysis
of the sample results and within 30 days of the receipt of the sample
results, enter the information in the operating record and notify the
Director of this finding in writing. The notification must indicate
what parameters or constituents have shown statistically significant
changes; and
(b) immediately resample the ground water in all monitoring
wells, both background and downgradient, or in a subset of wells
specified by the Director, and determine:
(i) the concentration of all constituents listed in Section
R315-308-4, including additional constituents that may have been
identified in the approved ground water monitoring plan;
(ii) if there is a statistically significant increase over
background of any parameter or constituent in any monitoring well at
the compliance point; and
(iii) notify the Director in writing within seven days of the
completion of the statistical analysis of the sample results.
(c) The owner or operator may demonstrate that a source other
than the solid waste disposal facility caused the contamination or
that the statistically significant change resulted from error in
sampling, analysis, statistical evaluation, or natural variation in
ground water quality. A report documenting this demonstration must
be certified by a qualified ground-water scientist and approved by
the Director and entered in the operating record. If a successful
demonstration is made and documented, the owner or operator may continue
monitoring as specified in Subsection R315-308-2(5) (b). (12) If, after 90days, a successful demonstration as stipulated
in Subsection R315-308-2(11) (c) is not made, the owner or operator
must initiate the assessment monitoring program required as follows:
(a) within 14 days of the determination that a successful
demonstration is not made, take one sample from each downgradient well
and analyze for all constituents listed as Appendix II in 40 CFR Part 258, 2001 ed., which is adopted and incorporated by reference.
(b) for any constituent detected from Appendix II, 40 CFR Part
258, in the downgradient wells a minimum of four independent samples
from the upgradient and four independent samples from each downgradient
well must be collected, analyzed, and statistically evaluated to
establish background concentration levels for the constituents; and
(c) within 14 days of the completion of the statistical analysis
of the sample results and within 30 days of the receipt of the sample
results, place a notice in the operation record and notify the Director
in writing identifying the Appendix II, 40 CFR Part 258, constituents
and their concentrations that have been detected as well as background
levels. The Director shall establish a groundwater quality protection
standard pursuant to Subsection R315-308-2(6) for any Appendix II,
40 CFR Part 258, constituent detected in the downgradient wells.
(d) The owner or operator shall thereafter resample:
(i) at a minimum, all downgradient wells on a quarterly basis
for all constituents in Section R315-308-4, or the alternative list
that may have been approved as part of the permit, and for those
constituents detected from Appendix II, 40 CFR Part 258;
(ii) the downgradient wells on an annual basis for all
constituents in Appendix II, 40 CFR Part 258; and
(iii) statistically analyze the results of all ground water
monitoring samples.
(e) The Director may specify additional or fewer constituents
depending upon the nature of the ground water or the waste on a site
specific basis considering:
(i) the types, quantities, and concentrations of constituents
in wastes managed at the landfill;
(ii) the mobility, stability, and persistence of waste
constituents or their reaction products in the unsaturated zone beneath
the landfill;
(iii) the detectability of indicator parameters, waste
constituents, and reaction products in the ground water; and
(iv) the background concentration or values and coefficients
of variation of monitoring parameters or constituents in the ground
water.
(f) If after two consecutive sampling events, the concentrations
of all constituents being analyzed in Subsection R315-308-2(12) (d) (i)
are shown to be at or below established background values, the owner
or operator must notify the Director of this finding and may, upon
the approval of the Director, return to the monitoring schedule and
constituents as specified in Subsection R315-308-2(5) (b).
(13) If one or more constituents from Section R315-308-4 or the
approved alternative list, or from those detected from Appendix II,
40 CFR Part 258, are detected at statistically significant levels above
the ground water quality protection standard as established pursuant
to Subsection R315-308-2 ( 6) in any sampling event, the owner or operator
must:
(a) within 14days of the receipt of this finding, place a notice
in the operating record identifying the constituents and concentrations
that have exceeded the groundwater quality standard. Within the same
time period, the owner or operator must also notify the Director and
all appropriate local governmental and local health officials that
the ground water quality standard has been exceeded;
(b) characterize the nature and extent of the release by
installing additional monitoring wells as necessary;
(c) install at least one additional monitoring well at the
facility boundary in the direction of contaminant migration and sample
this well and analyze the sample for the constituents in Section
R315-308-4 or the approved alternative list and the detected constituents from Appendix II, 40 CFR Part 258; and
(d) notify all persons who own the land or reside on the land
that directly overlies any part of the plume of contamination if
contaminants have migrated off-site as indicated by sampling of wells
in accordance with Subsections R315-308-2(13) (b) and (13)(c).
(e) The owner or operator may demonstrate that a source other
than the solid waste disposal facility caused the contamination or
that the statistically significant change resulted from error in
sampling, analysis, statistical evaluation, or natural variation in
ground water quality. A report documenting this demonstration must
be certified by a qualified ground-water scientist and approved by
the Director and entered in the operating record. If a successful
demonstration is made, documented and approved, the owner or operator
may continue monitoring as specified in Subsection R315-308-2(12) (d)
or Subsection R315-308-2(12) (e) when applicable.
R315-308-3. Corrective Action Program.
(1) If, within 90 days, a successful demonstration as stated
in Subsection R315-308-2(13) (e) is not made, the owner or operator
must:
(a) continue to monitor as required in Subsection
R315-308-2(12) (d).
(b) take any interim measures as required by the Director or
as necessary to ensure the protection of human health and the
environment; and
(c) assess possible corrective action measures for the current
conditions and circumstances of the disposal facility, addressing at
least the following:
(i) the performance, reliability, ease of implementation, and
potential impacts of appropriate potential remedies, including safety impacts, cross-media impacts, and control exposure to any residual.
contamination;
(ii) time required to begin and complete the remedy;
(iii) the costs of remedy implementation;
(iv) public health or environmental requirements that may
substantially affect implementation of the remedy; and
(v) prior to the selection of a remedy, discuss the results of
the corrective measures assessment in a public meeting with interested
and affected parties.
(d) Based on the results of the corrective measures assessment
conducted and the comments received in the public meeting, the owner
or operator must select a remedy which shall be submitted to the
Director.
(i) The corrective action remedy must: (A) be protective of human health and the environment;
(B) use permanent solutions that are within the capability of
best available technology;
(C) attain the established ground water quality standard;
(D) control the sources of release so as to reduce or eliminate,
to the maximum extent practicable, further releases of contaminants into the environment that may pose a threat to human health or the
environment; and
(E) be approved by the Director.
(ii) Within 14 days after the selection of the remedy the owner
or operator must:
(A) amend the corrective action program required by Subsection
R315-302-2(2) (e) if necessary and send a report to the Director for
approval describing the selected remedy and amendments, along with
a schedule of implementation and estimated time of completion; and
(B) put in place the financial assurance mechanism as required
by Rule R315-309 for corrective action and notify the Director of the
financial assurance mechanism and its effective date.
(2) Upon approval of the selected corrective action remedy, the
Director will notify the owner or operator of such approval and will
require that the corrective action plan proceed according to the
approved schedule.
(a) The Director may also require facility closure if the ground
water quality standard is exceeded and, in addition, may revoke any
permit and require reapplication.
(b) The Director or the owner or operator may determine, based
on information developed after implementation of the corrective action
plan, that compliance with the requirements of Subsection
R315-308-3(1) (d) (i) of this section are not being achieved through
the remedy selected. In such a case, the owner or operator must
implement other methods or techniques, upon approval by the Director,
that could practicably achieve compliance with the requirements.
(c) Upon completion of the remedy, the owner or operator shall
notify the Director. The notification shall contain certification
signed by the owner or operator and a qualified ground-water scientist
that the concentration of contaminant constituents have been reduced
to levels below the specified limits of the ground water quality
standard for a period of three years or an alternative length of time
specified by the Director. Upon approval of the Director the owner or operator shall:
(i) terminate corrective action measures;
(ii) continue detection monitoring as required in Subsection
R315-308-2(5) (b); and
(iii) be released from the requirements of financial assurance for corrective action.
R315-308-4. Constituents for Detection Monitoring.
The table lists the constituents for detection monitoring as
specified by Subsection R315-308-2(5), the CAS number for the
constituents, and the ground water quality standard for the
constituents for any facility that is required to monitor groundwater
under Rule R315-308
TABLE
Constituents for Detection Monitoring
Ground Water
Protection Standard
Inorganic Constituents CAS (mg/1)
Ammonia (as N) 7664-41-7
Carbonate/Bicarbonate
Calcium
Chemical Oxygen Demand (COD)
Chloride
Iron 7439-89-6
Magnesium
Manganese 7439-96-5
Nitrate (as N
pH
Potassium
Sodium
Sulfate
Total Dissolved Solids (TDS)
Total Organic Carbon (TOC)
Heavy Metals
Antimony 7440-36-0 0.006
Arsenic 7440-38-2 0.01
Barium 7440-39-3 2
Beryllium 7440-41-7 0.004 Cadmium 7440-43-9 0.005
Chromium 0.1
Cobalt 7440-48-4 2
Copper 7440-50-8 1.3
Lead 0.015
Mercury 7439-97-6 0.002
Nickel 7440-02-0 0.1 Selenium 7782-49-2 0.05
Silver 7440-22-4 0.1 Thallium 0.002 Vanadium 7440-62-2 0.3
Zinc 7440-66-6 5
Organic Constituents
Acetone 67-64-1 4
Acrylonitrile 107-13-1 0.1
Benzene 71-43-2 0.005 Bromochloromethane 74-97-5 0.01
Bromodichloromethanel
Bromoform1
Carbon disulfide
Carbon tetrachloride
Chlorobenzene Chloroethane
Chloroform'
Dibromochloromethanel
1,2-Dibromo-3-chloropropane
1,2-Dibromoethane
1,2-Dichlorobenzene (ortho)
1,4-Dichlorobenzene (para)
trans-1,4-Dichloro-2-butene
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethylene
cis-1,2-Dichloroethylene
trans-1,2-Dichloroethylene
1,2-Dichloropropane
cis-1,3-Dichloropropene
trans-1,3-Dichloropropene
Ethylbenzene
2-Hexanone
Methyl bromide
Methyl chloride
Methylene bromide
Methylene chloride
Methyl ethyl ketone
Methyl iodide
4-Methy1-2-pentanone
Styrene
1,1,1,2-Tetrachloroethane
1,1,2,2-Tetrachloroethane
Tetrachloroethylene
Toluene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethylene
Trichlorofluoromethane 1,2,3-Trichloropropane
Vinyl acetate
Vinyl Chloride
Xylenes

75-27-4 0.1

75-25-2 0.1

75-15-0 4

56-23-5 0.005

108-90-7 0.1

75-00-3 15

67-66-3 0.1

124-48-1 0.1

96-12-8 0.0002

106-93-4 0.00005

95-50-1 0.6

106-46-7 0.075
110-57-6

75-34-3 4

107-06-2 0.005

75-35-4 0.007

156-59-2 0.07

156-60-5 0.1

78-87-5 0.005

10061-01-5 0.002

10061-02-6 0.002

100-41-4 0.7

591-78-6 1.5

74-83-9 0.01

74-87-3 0.003

74-95-3 0.4

75-09-2 0.005

78-93-3 0.17
74-88-4

108-10-1 3

100-42-5 0.1

630-20-6 0.07

79-34-5 0.005

127-18-4 0.005

108-88-3 1

71-55-6 0.2

79-00-5 0.005

79-01-6 0.005

75-69-4 10

96-18-4 0.04

108-05-4 37

75-01-4 0.002

1330-20-7 10
'The ground water protection standard of 0.1 mg/1 is for
the total of Bromodichloromethane, Bromoform, Chloroform, and
Dibromochloromethane.
R315-308-5. Solid Waste Ground Water Quality Protection Standards
for 40 CFR 258 Appendix II Constituents.
The table lists the CAS number for each constituent and the ground
water quality protection standards which are currently available for
the 40 CFR 258 Appendix II constituents required for assessment
monitoring of ground water at a solid waste facility as specified by
Subsection R315-308-2(12).
TABLE
Appendix II Protection Standards
Ground Water
Protection Standard
Appendix II Constituent CAS (mg/1)
2,4-D 94-75-7 0.07
2,4,5-T 93-76-5 0.37
2,4,5-TP 93-72-1 0.05
Anthracene 120-12-7 10
Benzo(a)pyrene 50-32-8 0.0002
bis(2-Ethylhexy)phthalate 117-81-7 0.006
Chlordane 57-74-9 0.002
Cyanide 57-12-5 0.2
Dinoseb 88-85-7 0.007
Endrin 72-20-8 0.002
Heptachlor 76-44-8 0.0004
Heptachlor epoxide 1024-57-3 0.0002
Hexachlorobenzene 118-74-1 0.001
Hexachlorocyclopentadiene 77-47-4 0.05
Lindane 58-89-9 0.0002 Methoxychlor 72-43-5 0.04
Pentachlorophenol 87-86-5 0.001
Polychlorinated biphenyls(PCBs) 1336-36-3 0.0005
Tin 7440-31-5 21.9
Toxaphene 8001-35-2 0.003
1,2,4-Trichlorobenzene 120-82-1 0.07
KEY: solid waste management, waste disposal
Date of Enactment or Last Substantive Amendment: April 25, 2013
Notice of Continuation: February 13, 2013
Authorizing, and Mmplemented or Interpreted Law: 19-6-105; 40
258
CFR
Wintoct ReflOal am gm Ns am as me sr am as dis ge 1 6
[Code of Federal Regulations]
[Title 40, Volume 21]
[Revised as of July 1, 2001]
From the U.S. Government Printing Office via GPO Access
[CITE: 40CFR258.751
[Page 426-434]
TITLE 40--PROTECTION OF ENVIRONMENT
AGENCY (CONTINUED)
PART 258--CRITERIA FOR MUNICIPAL SOLID WASTE LANDFILLS--Table of Contents
Subpart G--Financial Assurance Criteria
Sec. 258.75 Discounting.
The Director of an approved State may allow discounting of closure
cost estimates in Sec. 258.71(a), post-closure cost estimates in
Sec. 258.72(a), and/or corrective action costs in Sec. 258.73(a) up to
the rate of return for essentially risk free investments, net of
inflation, under the following conditions:
(a) The State Director determines that cost estimates are complete
and accurate and the owner or operator has submitted a statement from a
Registered Professional Engineer so stating;
(b) The State finds the facility in compliance with applicable and
appropriate permit conditions;
(c) The State Director determines that the closure date is certain
and the owner or operator certifies that there are no foreseeable
factors that will change the estimate of site life; and
[[Page 427]]
(d) Discounted cost estimates must be adjusted annually to reflect
inflation and years of remaining life.
[61 FR 60339, Nov. 27, 1996]
Appendix I to Part 258--Constituents for Detection Monitoring \1\
Common name \2\ CAS RN \3\
Inorganic Constituents:
(1) Antimony (Total)
(2) Arsenic (Total)
4/15/2008
WAIS Document Retrieval Page 2 of 16
(3) Barium
(4) Beryllium
(5) Cadmium
(6) Chromium
(7) Cobalt
(8) Copper
(9) Lead
(10) Nickel
(11) Selenium
(12) Silver
(13) Thallium
(14) Vanadium
(15) Zinc
Organic Constituents:
(16) Acetone
(17) Acrylonitrile
(18) Benzene
(19) Bromochloromethane
(20) Bromodichloromethane
(21) Bromoform; Tribromomethane
(22) Carbon disulfide
(23) Carbon tetrachloride
(24) Chlorobenzene
(25) Chloroethane; Ethyl chloride
(26) Chloroform; Trichloromethane
(27) Dibromochloromethane; Chlorodibromomethane
(28) 1,2-Dibromo-3-chloropropane; DBCP
(29) 1,2-Dibromoethane; Ethylene dibromide; EDB
(30) o-Dichlorobenzene; 1,2-Dichlorobenzene
(31) p-Dichlorobenzene; 1,4-Dichlorobenzene
(32) trans-1,4-Dichloro-2-butene
(33) 1,1-Dichloroethane; Ethylidene chloride
(34) 1,2-Dichloroethane; Ethylene dichloride
(35) 1,1-Dichloroethylene; 1,1-Dichloroethene; Vinylidene
chloride
(36) cis-1,2-Dichloroethylene; cis-1,2-Dichloroethene...
(37) trans-1,2-Dichloroethylene; trans-1,2-Dichloroethene
(38) 1,2-Dichloropropane; Propylene dichloride
(39) cis-1,3-Dichloropropene
(40) trans-1,3-Dichloropropene
(41) Ethylbenzene
(42) 2-Hexanone; Methyl butyl ketone
(43) Methyl bromide; Bromomethane
(44) Methyl chloride; Chloromethane
(45) Methylene bromide; Dibromomethane
(46) Methylene chloride; Dichloromethane
(47) Methyl ethyl ketone; MEK; 2-Butanone
(Total)
(Total)
(Total)
(Total)
(Total)
(Total)
(Total)
(Total)
(Total)
(Total)
(Total)
(Total)
(Total)
67-64-1
107-13-1
71-43-2
74-97-5
75-27-4
75-25-2
75-15-0
56-23-5
108-90-7
75-00-3
67-66-3
124-48-1
96-12-8
106-93-4
95-50-1
106-46-7
110-57-6
75-34-3
107-06-2
75-35-4
156-59-2
156-60-5
78-87-5
10061-01-5
10061-02-6
100-41-4
591-78-6
74-83-9
74-87-3
74-95-3
75-09-2
78-93-3
as an am tam am sr ---
111. MI In MIN In
(48) Methyl iodide; Iodomethane
MI MI MI MI MI 41111111 11111111ge MI6
74-88-4
(49) 4-Methy1-2-pentanone; Methyl isobutyl ketone 108-10-1
(50) Styrene 100-42-5
(51) 1,1,1,2-Tetrachloroethane 630-20-6
(52) 1,1,2,2-Tetrachloroethane 79-34-5
(53) Tetrachloroethylene; Tetrachloroethene; 127-18-4
Perchloroethylene
(54) Toluene 108-88-3
(55) 1,1,1-Trichloroethane; Methylchloroform 71-55-6
(56) 1,1,2-Trichloroethane 79-00-5
(57) Trichloroethylene; Trichloroethene 79-01-6
(58) Trichlorofluoromethane; CFC-11 75-69-4
(59) 1,2,3-Trichloropropane 96-18-4
(60) Vinyl acetate 108-05-4
(61) Vinyl chloride 75-01-4
(62) Xylenes 1330-20-7
\1\ This list contains 47 volatile organics for which possible
analytical procedures provided in EPA Report SW-846 "Test Methods for
Evaluating Solid Waste," third edition, November 1986, as revised
December 1987, includes Method 8260; and 15 metals for which SW-846
provides either Method 6010 or a method from the 7000 series of
methods.
\2\ Common names are those widely used in government regulations,
scientific publications, and commerce; synonyms exist for many
chemicals.
\3\ Chemical Abstracts Service registry number. Where "Total" is
entered, all species in the ground water that contain this element are
included.
Appendix II to Part 258--List of Hazardous Inorganic and
Organic Constituents \1\
Common Name \2\ CAS RN \3\ Chemical abstracts service
index name \4\
Suggested
methods \5\
PQL (<greek-
m> g/L) \6\
Acenaphthene 83-32-9 Acenaphthylene, 1,2-dihydro-. 8100 200
8270 10
Acenaphthylene 208-96-8 Acenaphthylene 8100 200
8270 10
Acetone 67-64-1 2-Propanone 8260 100
Acetonitrile; Methyl cyanide 75-05-8 Acetonitrile 8015 100
Acetophenone 98-86-2 Ethanone, 1-phenyl- 8270 10
2-Acety1aminof1uorene; 2-AAF 53-96-3 Acetamide, N-9H-fluoren-2-yl- 8270 20
Acrolein 107-02-8 2-Propenal 8030 5
4/15/2008
Page 4 of 16
8260 100
8030 5
8260 200
8080 0.05
8270 10
8010 5
8260 10
8270 20
8100 200
8270 10
6010 300
7040 2000
7041 30
6010 500
7060 10
7061 20
6010 20
7080 1000
8020 2
8021 0.1
8260 5
8100 200
8270 10
8100 200
8270 10
8100 200
8270 10
8100 200
8270 10
8100 200
8270 10
8270 20
6010 3
7090 50
7091 2
8080 0.05
8270 10
WAIS Document Retrieval
Acrylonitrile 107-13-1 2-Propenenitrile
Aldrin 309-00-2 1,4:5,8-Dimethanonaphthalene,
1,2,3,4,10,10-hexachloro-
1,4,4a,5,8,8a-hexahydro-
(1<greek-a>,4<greek-a>,4a<gr
e,5<greek-a>,8<greek-a>,8a<g
r)-
Allyl chloride 107-05-1 1-Propene, 3-chloro-
[[Page 428]]
4-Aminobiphenyl 92-67-1 [1,1\1\-Bipheny1]-4-amine....
Anthracene 120-12-7 Anthracene
Antimony (Total) Antimony
Arsenic (Total) Arsenic
Barium (Total) Barium
Benzene 71-43-2 Benzene
Benzo[a]anthracene; Benzanthracene... 56-55-3 Benz[a]anthracene
Benzo[b]fluoranthene 205-99-2 Benz[e]acephenanthrylene
Benzo[k]fluoranthene 207-08-9 Benzo[k]fluoranthene
Benzo[ghi]perylene 191-24-2 Benzo[ghi]perylene
Benzo[a]pyrene 50-32-8 Benzo[a]pyrene
Benzyl alcohol 100-51-6 Benzenemethanol
Beryllium (Total) Beryllium
alpha-BHC 319-84-6 Cyclohexane, 1,2,3,4,5,6-
hexachloro-, (1<greek-
a>,2<greek-a>,3<greek-b>,4(g
r,5<greek-b>,6<greek-b>)-.
irmson —as— r sr— 4"iiiii8 r
INN OfigtoctRal IMO OM gm
beta-BHC
delta-BHC
11111 IMO 1111 Mlle BM MI
319-85-7 Cyclohexane, 1,2,3,4,5,6-
hexachloro-, (1<greek-
a>,2<greek-b>,3<greek-a>,4<g
r,5<greek-a>,6<greek-b>)-.
319-86-8 Cyclohexane, 1,2,3,4,5,6-
hexachloro-, (1<greek-
a>,2<greek-a>,3<greek-a>,4<g
r,5<greek-a>,6<greek-b>)-.
MI
8080
8270
8080
8270
On 4111kgelMINI6
0.05
20
0.1
20
gamma-BHC; Lindane 58-89-9 Cyclohexane, 1,2,3,4,5,6- 8080 0.05
hexachloro-, (1<greek-
a>,2<greek-a>,3<greek-b>,4<g
r,5<greek-a>,6<greek-b>)-.
8270 20
Bis(2-chloroethoxy)methane 111-91-1 Ethane, 1,1\1\- 8110 5
[methylenebis(oxy)]bis[2-
chloro-.
8270 10
Bis(2-chloroethyl) ether; 111-44-4 Ethane, 1,1\1\-oxybis[2- 8110 3
Dichloroethyl ether. chloro-. 8270 10
Bis-(2-chloro-l-methylethyl) ether; 108-60-1 Propane, 2,2\1\-oxybis[1- 8110 10
2,2\1\-Dichlorodiisopropyl ether; chloro-. 8270 10
DCIP, See note 7
Bis(2-ethylhexyl) phthalate 117-81-7 1,2-Benzenedicarboxylic acid,
bis(2-ethylhexyl) ester.
8060 20
Bromochloromethane; 74-97-5 Methane, bromochloro- 8021 0.1
Chlorobromomethane. 8260 5
Bromodichloromethane; 75-27-4 Methane, bromodichloro- 8010 1
Dibromochloromethane 8021 0.2
8260 5
Bromoform; Tribromomethane 75-25-2 Methane, tribromo- 8010 2
8021 15
8260 5
4-Bromophenyl phenyl ether 101-55-3 Benzene, 1-bromo-4-phenoxy-.. 8110 25
8270 10
Butyl benzyl phthalate; Benzyl butyl
phthalate.
85-68-7 1,2-Benzenedicarboxy1ic acid,
butyl phenylmethyl ester.
8060
8270
5
10
Cadmium (Total) Cadmium 6010 40
7130 50
7131 1
Carbon disulfide 75-15-0 Carbon disulfide 8260 100
Carbon tetrachloride 56-23-5 Methane, tetrachloro- 8010 1
8021 0.1
8260 10
Chlordane See Note 8 4,7-Methano-1H-indene, 8080 0.1
1,2,4,5,6,7,8,8-octachloro- 8270 50
2,3,3a,4,7,7a-hexahydro-.
p-Chloroaniline 106-47-8 Benzenamine, 4-chloro- 8270 20
Chlorobenzene 108-90-7 Benzene, ch1oro- 8010 2
8020 2
4/15/2008
WAIS Document Retrieval
8021
Page 6 of 16
0.1
8260 5
[[Page 4291]
Chlorobenzilate 510-15-6 Benzeneacetic acid, 4-chloro- 8270 10
<greek-a>-(4-chloropheny1)-
<greek-a>-hydroxy-, ethyl
ester.
p-Chloro-m-cresol; 4-Ch1oro-3- 59-50-7 Phenol, 4-chloro-3-methyl-... 8040 5
methylphenol. 8270 20
Chloroethane; Ethyl chloride 75-00-3 Ethane, chloro- 8010 5
8021 1
8260 10
Chloroform; Trichloromethane 67-66-3 Methane, trichloro- 8010 0.5
8021 0.2
8260 5
2-Chloronaphthalene 91-58-7 Naphthalene, 2-chloro- 8120 10
8270 10
2-Chlorophenol 95-57-8 Phenol, 2-chloro- 8040 5
8270 10
4-Chlorophenyl phenyl ether 7005-72-3 Benzene, 1-chloro-4-phenoxy-. 8110 40
8270 10
Chloroprene 126-99-8 1,3-Butadiene, 2-chloro- 8010 50
8260 20
Chromium (Total) Chromium 6010 70
7190 500
7191 10
Chrysene 218-01-9 Chrysene 8100 200
8270 10
Cobalt (Total) Cobalt 6010 70
7200 500
7201 10
Copper (Total) Copper 6010 60
7210 200
7211 10
m-Cresol; 3-methylphenol 108-39-4 Phenol, 3-methy1- 8270 10
o-Cresol; 2-methylphenol 95-48-7 Phenol, 2-methyl- 8270 10
p-Cresol; 4-methylphenol 106-44-5 Phenol, 4-methyl- 8270 10
Cyanide 57-12-5 Cyanide 9010 200
2,4-D; 2,4-Dichlorophenoxyacetic acid 94-75-7 Acetic acid, (2,4-
dichlorophenoxy)-.
8150 10
4,4\1\ -DDD 72-54-8 Benzene 1,1\1\-(2,2- 8080 0.1
dichloroethylidene)bis[4-
chloro-.
8270 10
4,4\1\ -DDE 72-55-9 Benzene, 1,1\1\- 8080 0.05
ameasasemmemem—asemas 4".."
RAW MI MO MB MN WO MO INN 11111Lge ani6 gin
(dichloroethyenylidene)bis[4- 8270 10
chloro-.
4,4\1\-DDT 50-29-3 Benzene, 1,1\1\-(2,2,2- 8080 0.1
trichloroethylidene)bis[4- 8270 10
chloro-.
Diallate 2303-16-4 Carbamothioic acid, bis(1- 8270 10
methylethyl)-,S-(2,3-
dichloro-2-propenyl) ester.
Dibenz[a,h]anthracene 53-70-3 Dibenz[a,h]anthracene 8100 200
8270 10
Dibenzofuran 132-64-9 Dibenzofuran 8270 10
Dibromochloromethane; 124-48-1 Methane, dibromochloro- 8010 1
Chlorodibromomethane. 8021 0.3
8260 5
1,2-Dibromo-3-chloropropane; DBCP.... 96-12-8 Propane, 1,2-dibrome-3-ch1oro- 8011 0.1
8021 30
8260 25
1,2-Dibromoethane; Ethylene 106-93-4 Ethane, 1,2-dibromo- 8011 0.1
dribromide; EDB. 8021 10
8260 5
Di-n-butyl phthalate 84-74-2 1,2-Benzenedicarboxylic acid, 8060 5
dibutyl ester. 8270 10
o-Dichlorobenzene; 1,2- 95-50-1 Benzene, 1,2-dichloro- 8010 2
Dichlorobenzene. 8020 5
8021 0.5
8120 10
8260 5
8270 10
m-Dichlorobenzene; 1,3- 541-73-1 Benzene, 1,3-Dichloro- 8010 5
Dichlorobenzene. 8020 5
8021 0.2
8120 10
8260 5
8270 10
[[Page 430]]
p-Dichlorobenzene; 1,4-
Dichlorobenzene.
3,3\1\-Dichlorobenzidine
trans-1,4-Dichloro-2-butene
106-46-7 Benzene, 1,4-dichloro- 8010 2
8020 5
8021 0.1
8120 15
8260 5
8270 10
91-94-1 [1,1\1\-Bipheny1]-4,4\1\- 8270 20
diamine, 3,3\1\-dichloro-.
110-57-6 2-Butene, 1,4-dichloro-, (E)- 8260 100
4/15/2008
WAIS Document Retrieval Page 8 of 16
Dichlorodifluoromethane; CFC 12; 75-71-8 Methane, dichlorodifluoro-... 8021 0.5
8260 5
1,1-Dichloroethane; Ethyldidene 75-34-3 Ethane, 1,1-dichloro- 8010 1
chloride. 8021 0.5
8260 5
1,2-Dichloroethane; Ethylene 107-06-2 Ethane, 1,1-dichloro- 8010 0.5
dichloride. 8021 0.3
8260 5
1,1-Dichloroethylene; 1,1- 75-35-4 Ethene, 1,1-dichloro- 8010 1
Dichloroethene; Vinylidene chloride. 8021 0.5
8260 5
cis-1,2-Dichloroethylene; cis-1,2- 156-59-2 Ethene, 1,2-dichloro-, (Z)-.. 8021 0.2
Dichloroethene. 8260 5
trans-1,2-Dichloroethylene trans-1,2- 156-60-5 Ethene, 1,2-dichloro-, (E)-.. 8010 1
Dichloroethene. 8021 0.5
8260 5
2,4-Dichlorophenol 120-83-2 Phenol, 2,4-dichloro- 8040 5
8270 10
2,6-Dichlorophenol 87-65-0 Phenol, 2,6-dichloro- 8270 10
1,2-Dichloropropane; Propylene 78-87-5 Propane, 1,2-dichloro- 8010 0.5
dichloride. 8021 0.05
8260 5
1,3-Dichloropropane; Trimethylene 142-28-9 Propane, 1,3-dichloro- 8021 0.3
dichloride. 8260 5
2,2-Dichloropropane; Isopropylidene 594-20-7 Propane, 2,2-dichloro- 8021 0.5
chloride. 8260 15
1,1-Dichloropropene 563-58-6 1-Propene, 1,1-dichloro- 8021 0.2
8260 5
cis-1,3-Dichloropropene 10061-01-5 1-Propene, 1,3-dichloro-, (Z)- 8010 20
8260 10
trans-1,3-Dichloropropene 10061-02-6 1-Propene, 1,3-dichloro-, (E)- 8010 5
8260 10
Dieldrin 60-57-1 2,7:3,6-Dimethanonaphth[2,3- 8080 0.05
bloxirene, 3,4,5,6,9,9-hexa,
chloro-la,2,2a,3,6,6a,7,7a-
octahydro-, (1a<greek-
a>,2<greek-b>,2a<greek-a>,3<
g,6<greek-b>,6a<greek-a>,7<g
r,7a<greek-a>)-.
8270 10
Diethyl phthalate 84-66-2 1,2-Benzenedicarboxylic acid, 8060 5
diethyl ester. 8270 10
0,0-Diethyl 0-2-pyrazinyl 297-97-2 Phosphorothioic acid, 0,0- 8141 5
phosphorothioate; Thionazin. diethyl 0-pyrazinyl ester. 8270 20
Dimethoate 60-51-5 Phosphorodithioic acid, 0,0- 8141 3
dimethyl S-[2-(methylamino)- 8270 20
2-oxoethyl] ester.
p-(Dimethylamino)azobenzene 60-11-7 Benzenamine, N,N-dimethy1-4- 8270 10
ais am ems mar- --- -man um
Wilaocaiit RAW 11111 OM OM NIB OM MO MB 111In NIS
(phenylazo)-.
MI UM M1111 6
7,12-Dimethylbenz[a]anthracene 57-97-6 Benz[a]anthracene, 7,12-
dimethyl-.
8270 10
3,3\1\-Dimethylbenzidine 119-93-7 [1,1\1\-Bipheny1]-4,4\1\-
diamine, 3,3\1\-dimethyl-.
8270 10
2,4-Dimethylphenol; m-Xylenol 105-67-9 Phenol, 2,4-dimethyl- 8040 5
8270 10
Dimethyl phthalate 131-11-3 1,2-Benzenedicarboxylic acid, 8060 5
dimethyl ester. 8270 10
m-Dinitrobenzene 99-65-0 Benzene, 1,3-dinitro- 8270 20
4,6-Dinitro-o-cresol 4,6-Dinitro-2- 534-52-1 Phenol, 2-methy1-4,6-dinitro. 8040 150
methylphenol. 8270 50
2,4-Dinitrophenol; 51-28-5 Phenol, 2,4-dinitro- 8040 150
8270 50
2,4-Dinitroto1uene 121-14-2 Benzene, 1-methy1-2,4-dinitro- 8090 0.2
8270 10
2,6-Dinitrotoluene 606-20-2 Benzene, 2-methy1-1,3-dinitro- 8090 0.1
8270 10
Dinoseb; DNBP; 2-sec-Buty1-4,6- 88-85-7 Phenol, 2-(1-methylpropy1)- 8150 1
dinitrophenol. 4,6-dinitro-. 8270 20
[[Page 431]]
Di-n-octyl phthalate 117-84-0 1,2-Benzenedicarboxylic acid, 8060 30
dioctyl ester. 8270 10
Diphenylamine 122-39-4 Benzenamine, N-phenyl- 8270 10
Disulfoton 298-04-4 Phosphorodithioic acid, 0,0- 8140 2
diethyl S-[2- 8141 0.5
(ethylthio)ethyl] ester. 8270 10
Endosulfan I 959-98-8 6,9-Methano-2,4,3- 8080 0.1
benzodioxathiepin,
6,7,8,9,10,10-hexa- chloro-
8270 20
Endosulfan II 33213-65-9
1,5,5a,6,9,9a-hexahydro-, 3-
oxide,
6,9-Methano-2,4,3- 8080 0.05
benzodioxathiepin,
6,7,8,9,10,10-hexa- chloro-
8270 20
1,5,5a,6,9,9a-hexahydro-, 3-
oxide, (3<greek-a>,5a<greek-
a>,6<greek-b>,9<greek-b>,9a<
g)-.
Endosulfan sulfate 1031-07-8 6,9-Methano-2,4,3- 8080 0.5
benzodioxathiepin, 8270 10
6,7,8,9,10,10-hexa- chloro-
1,5,5a,6,9,9a-hexahydro-,3-3-
dioxide.
4/15/2008
WAIS Document Retrieval
Endrin 72-20-8 2,7:3,6-Dimethanonaphth[2,3-
b]oxirene, 3,4,5,6,9,9-
hexachloro-
la,2,2a,3,6,6a,7,7a-
octahydro-, (la<greek-a>,
2<greek-b>,2a<greek-b>,3<gre
e,6<greek-a>,6a<greek-b>,7<g
r,7a(greek-a>)-.
8080
8270
Page 10 of 16
0.1
20
Endrin aldehyde 7421-93-4 1,2,4- 8080 0.2
Methenocyclopenta[cd]pentale
ne-5-carboxaldehyde,
2,2a,3,3,4,7-
hexachlorodecahydro-,
(1<greek-a>,2<greek-b>,2a<gr
e,4<greek-b>,4a<greek-b>,5<g
r,6a<greek-b>,6b<greek-b>,7R
8270 10
*)_.
Ethylbenzene 100-41-4 Benzene, ethyl- 8020 2
8221 0.05
8260 5
Ethyl methacrylate 97-63-2 2-Propenoic acid, 2-methyl-, 8015 5
ethyl ester. 8260 10
8270 10
Ethyl methanesulfonate 62-50-0 Methanesulfonic acid, ethyl
ester.
8270 20
Famphur 52-85-7 Phosphorothioic acid, 0-[4- 8270 20
[(dimethylamino)sulfonyl]phe
nyl] 0,0-dimethyl ester.
Fluoranthene 206-44-0 Fluoranthene 8100 200
8270 10
Fluorene 86-73-7 9H-Fluorene 8100 200
8270 10
Heptachlor 76-44-8 4,7-Methano-1H-indene, 8080 0.05
1,4,5,6,7,8,8-heptachloro- 8270 10
3a,4,7,7a-tetrahydro-.
Heptachlor epoxide 1024-57-3 2,5-Methano-2H-indeno[1,2- 8080 1
b]oxirene, 2,3,4,5,6,7,7-
heptachloro-la,lb,5,5a,6,6a-
hexahydro-, (la<greek-a>,
lb<greek-b>, 2<greek-a>,
5<greek-a>, 5a<greek-b>,
6<greek-b>, 6a<greek-a›).
8270 10
Hexachlorobenzene 118-74-1 Benzene, hexachloro- 8120 0.5
8270 10
Hexachlorobutadiene 87-68-3 1,3-Butadiene, 1,1,2,3,4,4- 8021 0.5
hexachloro-. 8120 5
8260 10
as as am meamens --- an
Wilialboct Refifial als am am sue No am in
8270
as we 1 m6 as
10
Hexachlorocyclopentadiene 77-47-4 1,3-Cyclopentadiene, 8120 5
1,2,3,4,5,5-hexachloro-. 8270 10
Hexachloroethane 67-72-1 Ethane, hexachloro- 8120 0.5
8260 10
8270 10
Hexachloropropene 1888-71-7 1-Propene, 1,1,2,3,3,3-
hexachloro-.
8270 10
2-Hexanone; Methyl butyl ketone 591-78-6 2-Hexanone 8260 50
Indeno(1,2,3-cd)pyrene 193-39-5 Indeno(1,2,3-cd)pyrene 8100 200
8270 10
Isobutyl alcohol 78-83-1 1-Propanol, 2-methyl- 8015 50
8240 100
Isodrin 465-73-6 1,4,5,8- 8270 20
Dimethanonaphthalene,1,2,3,4 8260 10
,10,10- hexachloro-
1,4,4a,5,8,8a hexahydro-
(1<greek-a>,4<greek-a>,4a<gr
e,5<greek-b>,8<greek-b>,8a(g
r)-.
Isophorone 78-59-1 2-Cyclohexen-1-one, 3,5,5- 8090 60
trimethyl-. 8270 10
Isosafrole 120-58-1 1,3-Benzodioxole, 5-(1-
propeny1)-.
8270 10
Kepone 143-50-0 1,3,4-Metheno-2H-
cyclobuta[cd]pentalen-2-one,
1,1a,3,3a,4,5,5,5a,5b,6-
decachlorooctahydro-.
8270 20
[[Page 432]]
Lead (Total) Lead 6010 400
7420 1000
7421 10
Mercury (Total) Mercury 7470 2
Methacrylonitrile 126-98-7 2-Propenenitrile, 2-methyl-.. 8015 5
8260 100
Methapyrilene 91-80-5 1,2-Ethanediamine, N.N-
dimethyl-N\1\-2-pyridinyl-N1/
8270 100
2-thienylmethyl)-.
Methoxychlor 72-43-5 Benzene,1,1\1\- 8080 2
(2,2,2,trichloroethylidene)b
is[4-methoxy-.
8270 10
Methyl bromide; Bromomethane 74-83-9 Methane, bromo- 8010 20
8021 10
Methyl chloride; Chloromethane 74-87-3 Methane, chloro- 8010 1
4/15/2008
WAIS Document Retrieval
8021
Page 12 of 16
0.3
3-Methylcholanthrene 56-49-5 Benz[j]aceanthrylene, 1,2-
dihydro-3-methyl-.
8270 10
Methyl ethyl ketone; MEK; 2-Butanone. 78-93-3 2-Butanone 8015 10
8260 100
Methyl iodide; Iodomethane 74-88-4 Methane, iodo- 8010 40
8260 10
Methyl methacrylate 80-62-6 2-Propenoic acid, 2-methyl-, 8015 2
methyl ester. 8260 30
Methyl methanesulfonate 66-27-3 Methanesulfonic acid, methyl
ester.
8270 10
2-Methylnaphthalene 91-57-6 Naphthalene, 2-methyl- 8270 10
Methyl parathion; Parathion methyl 298-00-0 Phosphorothioic acid, 0,0- 8140 0 5
dimethyl. 8141 1
8270 10
4-Methy1-2-pentanone; Methyl isobutyl 108-10-1 2-Pentanone, 4-methyl- 8015 5
ketone. 8260 100
Methylene bromide; Dibromomethane 74-95-3 Methane, dibromo- 8010 15
8021 20
8260 10
Methylene chloride; Dichloromethane 75-09-2 Methane, dichloro- 8010 5
8021 0 2
8260 10
Naphthalene 91-20-3 Naphthalene 8021 0.5
8100 200
8260 5
8270 10
1,4-Naphthoquinone 130-15-4 1,4-Naphthalenedione 8270 10
1-Naphthylamine 134-32-7 1-Naphthalenamine 8270 10
2-Naphthylamine 91-59-8 2-Naphthalenamine 8270 10
Nickel (Total) Nickel 6010 150
7520 400
o-Nitroaniline; 2-Nitroaniline 88-74-4 Benzenamine, 2-nitro- 8270 50
m-Nitroaniline; 3-Nitroanile 99-09-2 Benzenamine, 3-nitro- 8270 50
p-Nitroaniline; 4-Nitroaniline 100-01-6 Benzenamine, 4-nitro 8270 20
Nitrobenzene 98-95-3 Benzene, nitro- 8090 40
8270 10
o-Nitrophenol; 2-Nitrophenol 88-75-5 Phenol, 2-nitro- 8040 5
8270 10
p-Nitrophenol; 4-Nitrophenol 100-02-7 Phenol, 4-nitro- 8040 10
8270 50
N-Nitrosodi-n-butylamine 924-16-3 1-Butanamine, N-butyl-N-
nitroso-.
8270 10
N-Nitrosodiethylamine 55-18-5 Ethanamine, N-ethyl-N-nitroso- 8270 20
N-Nitrosodimethylamine 62-75-9 Methanamine, N-methyl-N-
nitroso-.
8070 2
measesmaummmain-4111°8—
RAW MI On
N-Nitrosodiphenylamine
N-Nitrosodipropylamine; N-Nitroso-N-
dipropylamine; Di-n-
propylnitrosamine.
N-Nitrosomethylethalamine
N-Nitrosopiperidine
N-Nitrosopyrrolidine
5-Nitro-o-toluidine
86-30-6
621-64-7
10595-95-6
100-75-4
930-55-2
99-55-8
Benzenamine, N-nitroso-N-
phenyl-.
1-Propanamine, N-nitroso-N-
propyl-.
Ethanamine, N-methyl-N-
nitroso-.
Piperidine, 1-nitroso-
Pyrrolidine, 1-nitroso-
Benzenamine, 2-methy1-5-nitro-
8070
8070
8270
8270
8270
8270
Mai age 1=16
5
10
10
20
40
10
Parathion 56-38-2 Phosphorothioic acid, 0,0- 8141 0.5
diethyl 0-(4-nitrophenyl)
ester.
8270 10
Pentachlorobenzene 608-93-5 Benzene, pentachloro- 8270 10
Pentachloronitrobenzene 82-68-8 Benzene, pentachloronitro-... 8270 20
Pentachlorophenol 87-86-5 Phenol, pentachloro- 8040 5
8270 50
Phenacetin 62-44-2 Acetamide, N-(4-ethoxyphen1). 8270 20
Phenanthrene 85-01-8 Phenanthrene 8100 200
8270 10
[[Page 433]]
Phenol 108-95-2 Phenol 8040 1
p-Phenylenediamine 106-50-3 1,4-Benzenediamine 8270 10
Phorate 298-02-2 Phosphorodithioic acid, 0,0- 8140 2
diethyl S- 8141 0.5
[(ethylthio)methyl] ester. 8270 10
Polychlorinated biphenyls; PCBs; See Note 9 1,1'-Biphenyl, chloro 8080 50
Aroclors. derivatives. 8270 200
Pronamide 23950-58-5 Benzamide, 3,5-dichloro-N- 8270 10
(1,1-dimethy1-2-propyny1)-.
Propionitrile; Ethyl cyanide 107-12-0 Propanenitrile 8015 60
8260 150
Pyrene 129-00-0 Pyrene 8100 200
8270 10
Safrole 94-59-7 1,3-Benzodioxole, 5-(2-
propeny1)-.
8270 10
Selenium (Total) Selenium 6010 750
7740 20
7741 20
Silver (Total) Silver 6010 70
7760 100
7761 10
Silvex; 2,4,5-TP 93-72-1 Propanoic acid, 2-(2,4,5- 8150 2
4/15/2008
WAIS Document Retrieval
trichlorophenoxy)-.
Page 14 of 16
Styrene 100-42-5 Benzene, ethenyl- 8020 1
8021 0.1
8260 10
Sulfide 18496-25-8 Sulfide 9030 4000
2,4,5-T; 2,4,5-Trichlorophenoxyacetic
acid.
93-76-5 Acetic acid, (2,4,5-
trichlorophenoxy)-.
8150 2
1,2,4,5-Tetrachlorobenzene 95-94-3 Benzene, 1,2,4,5-tetrachloro- 8270 10
1,1,1,2-Tetrachloroethane 630-20-6 Ethane, 1,1,1,2-tetrachloro-. 8010 5
8021 0.05
8260 5
1,1,2,2-Tetrachloroethane 79-34-5 Ethane, 1,1,2,2-tetrachloro-. 8010 0.5
8021 0.1
8260 5
Tetrachloroethylene; 127-18-4 Ethene, tetrachloro- 8010 0.5
Tetrachloroethene; Perchloroethylene. 8021 0.5
8260 5
2,3,4,6-Tetrachlorophenol 58-90-2 Phenol, 2,3,4,6-tetrachloro-. 8270 10
Thallium (Total) Thallium 6010 400
7840 1000
7841 10
Tin (Total) Tin 6010 40
Toluene 108-88-3 Benzene, methyl- 8020 2
8021 0.1
8260 5
o-Toluidine 95-53-4 Benzenamine, 2-methyl- 8270 10
Toxaphene See Note 10 Toxaphene 8080 2
1,2,4-Trichlorobenzene 120-82-1 Benzene, 1,2,4-trichloro-.... 8021 0.3
8120 0.5
8260 10
8270 10
1,1,1-Trichloroethane; 71-55-6 Ethane, 1,1,1-trichloro- 8010 0.3
Methylchloroform. 8021 0.3
8260 5
1,1,2-Trichloroethane 79-00-5 Ethane, 1,1,2-trichloro- 8010 0.2
8260 5
Trichloroethylene; Trichloroethene 79-01-6 Ethene, trichloro- 8010 1
8021 0.2
8260 5
Trichlorofluoromethane; CFC-11 75-69-4 Methane, trichlorofluoro-.... 8010 10
8021 0.3
8260 5
2,4,5-Trichlorophenol 95-95-4 Phenol, 2,4,5-trichloro- 8270 10
2,4,6-Trichlorophenol 88-06-2 Phenol, 2,4,6-trichloro- 8040 5
8270 10
1,2,3-Trichloropropane 96-18-4 Propane, 1,2,3-trichloro-.... 8010 10
8021 5
misisen an —mom an sap
ON MI MI OM MO OM INN MI MO MN all 11111, 11111116 ION
8260 15 0,0,0-Triethyl phosphorothioate 126-68-1 Phosphorothioic acid, 0,0,0- 8270 10
triethylester. sym-Trinitrobenzene 99-35-4 Benzene, 1,3,5-trinitro- 8270 10
[[Page 434]]
Vanadium (Total) Vanadium 6010 80
7910 2000
7911 40 Vinyl acetate 108-05-4 Acetic acid, ethenyl ester... 8260 50 Vinyl chloride; Chloroethene 75-01-4 Ethene, chloro- 8010 2
8021 0.4
8260 10 Xylene (total) See Note 11 Benzene, dimethyl- 8020 5
8021 0.2
8260 5 Zinc (Total) Zinc 6010 20
7950 50
7951 0.5
Notes
\1\ The regulatory requirements pertain only to the list of substances; the right hand columns (Methods and PQL)
are given for informational purposes only. See also footnotes 5 and 6.
\2\ Common names are those widely used in government regulations, scientific publications, and commerce;
synonyms exist for many chemicals.
\3\ Chemical Abstracts Service registry number. Where —Total" is entered, all species in the ground water that contain this element are included.
\4\ CAS index are those used in the 9th Collective Index.
\5\ Suggested Methods refer to analytical procedure numbers used in EPA Report SW-846 "Test Methods for
Evaluating Solid Waste", third edition, November 1986, as revised, December 1987. Analytical details can be
found in SW-846 and in documentation on file at the agency. CAUTION: The methods listed are representative SW-
846 procedures and may not always be the most suitable method(s) for monitoring an analyte under the
regulations.
\6\ Practical Quantitation Limits (PQLs) are the lowest concentrations of analytes in ground waters that can be
realiably determined within specified limits of precision and accuracy by the indicated methods under routine
laboratory operating conditions. The PQLs listed are generally stated to one significant figure. PQLs are
based on 5 mL samples for volatile organics and 1 L samples for semivolatile organics. CAUTION: The PQL values
in many cases are based only on a general estimate for the method and not on a determination for individual
compounds; PQLs are not a part of the regulation.
\7\ This substance is often called Bis(2-chloroisopropyl) ether, the name Chemical Abstracts Service applies to
its noncommercial isomer, Propane, 2,2"-oxybis[2-chloro- (CAS RN 39638-32-9).
\8\ Chlordane: This entry includes alpha-chlordane (CAS RN 5103-71-9), beta-chlordane (CAS RN 5103-74-2), gamma-
chlordane (CAS RN 5566-34-7), and constituents of chlordane (CAS RN 57-74-9 and CAS RN 12789-03-6). PQL shown
is for technical chlordane. PQLs of specific isomers are about 20 <greek-m>g/L by method 8270.
\9\ Polychlorinated biphenyls (CAS RN 1336-36-3); this category contains congener chemicals, including
4/15/2008
WAIS Document Retrieval Page 16 of 16
constituents of Aroclor 1016 (CAS RN 12674-11-2), Aroclor 1221 (CAS RN 11104-28-2), Aroclor 1232 (CAS RN 11141-
16-5), Aroclor 1242 (CAS RN 53469-21-9), Aroclor 1248 (CAS RN 12672-29-6), Aroclor 1254 (CAS RN 11097-69-1),
and Aroclor 1260 (CAS RN 11096-82-5). The PQL shown is an average value for PCB congeners.
\10\ Toxaphene: This entry includes congener chemicals contained in technical toxaphene (CAS RN 8001-35-2),
i.e., chlorinated camphene.
\11\ Xylene (total): This entry includes o-xylene (CAS RN 96-47-6), m-xylene (CAS RN 108-38-3), p-xylene (CAS RN
106-42-3), and unspecified xylenes (dimethylbenzenes) (CAS RN 1330-20-7). PQLs for method 8021 are 0.2 for o-
xylene and 0.1 for m- or p-xylene. The PQL for m-xylene is 2.0 <greek-m>g/L by method 8020 or 8260.
PART 259 [Reserved]
NOM
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
APPENDIX B
FIELD SAMPLING LOGS
AECOM
—
Well
ID Time
Top of Casing
Elevation
(feet)
Depth to
Water
(feet)
GW
Elevation
(feLt)
Comments
MW-1 rt) AA 4760.47 A.) Pk
MW-2 g31-- 4944.73 Li 11 •Li ''S 4/ T33.3 o (vs Ns
MW-3 15-2, 4765.38 tS7.14 I-1533, tti vs Aos
MW-4 gy, 4846.20 _. IA' LeS-55,55- itzi 34
MW-5 S n 4803.60 7(3'4S 3
MW-6 q't: 4835.55 ,301.S 1 ti5.WiL-1 i9•60 11
j)
411-4. 1r
2s-c.2.;
.14.1
Payson City Landfill
Static Water Level Log
Date:
Note: The ground water elevation in the monitoring wells should be within two feet of each other.
4538
4537
4536
4535
4534
Lu
4533
4532
4531
4530
....z._ , V
v
_37 —7—
k_.
_
Mill
_
—
_
_ —
,........
_
— —
— _ _ _
— _ _
—
4760.47
D it/frI ft
4944.73
D 4i if ,9 3 ft
4765.38
D 732- 'ILI ft
4846.20
D 311-4C ft
4803.60
D 20•2z ft
4835.55
D 301.51 ft
Elev — ft Elev 11535•30 ft Elev 1'M.214 ft Elev45-33.4-5- ft Elev '14-33.1% ft Elev Lit-33:7`f ft
MW-1 MW-2 MW-3 MW-4 MW-5 MW-6
1
Payson Landfill
Static Water Level Log
Date: 3/-7/1
Monitoring Well and TOC (ft)
1
Payson City Landfill
Equipment Calibration Log
Event: "oe," 61,314,411
Date: -A
Tirne:
personnel: \J\ Weather: 0-crS
Temperature: n cey,
Humidity: Stiet,
Instrument (v5: ÇL 0( 44145-0
DO Meter
OVM/OVA
Explosimeter
pH Meter
HNU
Hydrolab
Conductivity
Turbidity
Eh rneter
Other
CALIBRATION AND CONTINUING CALIBRATION LOG
Date
'
Time Calibration
Standard
Calibration
Standard
Expiration Date
Calibration
Standard
Concentration
Meter
Reading
Observations/Comments
V-yli 4,(4;3 4dia CL) .
p ho ¿Lc> LI Mt)
CoJ ilal ( ek.4 IMli il .411
• otatt) 6 0 CD
NU ZLIo g/12,_ Vic., VI 0
Payson City Landfill
Monitoring Well Sampling Log
General Information Well Evacuation
Well Identification: A0-4 Purge Method: Li
Sampler: C Purge Rate: *
Date Sampled:
Climate:
3/-1/oci, Time Start Purge: //TV
dar Time End Purge: /j-zi
Ambient Temperature: svp Total Volume Purged: 3
Sampling Information
Sampling Rate: *
Time Start Sampling:
Time End Sampling:
QA/QC Sampling:

115/115

Well Condition / Remarks:
hi-
Purge Measurements
Parameter Readinl 1 Readinl 2 Reading 3 Reading 4 Reading 5 Reading 6
127..3
Time
1111-, lux) MN., 11-11_ I Z IS
Temperature (°C) 0 I pi4 1.6 IC, 3-1 /5-.65- /5-• 4 6 /5;6/
Conductivity (mS/cm) c),--)10 ei,-7r ,-f a 7 ol 0 ,s7 cy,' OY5-
Turbiclity (NTU) 21.'1 O.," ( . 7... I. I.
pH
Parameter Reading 7 Reading 8 Reading 9 Reading 10 Readiiig 11 Reading 12
Time
Temperature (°C) 1 f.l.t.
Conductivity (mS/cm) 67-10-5
Turbidity (NTU)
1 . 1
pH e-
1
Payson City Landfill
Monitoring Well Sampling Log
General Information
Well Identification:
Sampler:
Date Sampled:
Climate:
Ambient Temperature:
ktto-4;-
(14v—x.L1 3/1/I It sr
35.°F
Wen Evacuation

Purge Method: " (

Purge Rate: * i e
Time Start Purge: <7, I S
Tirne End Purge: qi
Total Volume Purged: -...
Sampling Information
Sampling Rate: *
Time Start Sampling:
Time End Sampling:
QA/QC Sampling:

/C)

cr.)040- e wso

Well Condition / Remarks:
Purge Measurements
Parameter Reading 1 Reading 2 Reading 3 Reading 4 Reading 5 Reading 6
Time i , 5 935-
Temperature (°C) Ice 1,--i. Conductivity (mS/cm) 2.37,
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Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
APPENDIX C
DATA VALIDATION REPORT AND ANALYTICAL LABORATORY REPORTS
AECOM
Data Validation Report
Payson City Landfill Data Review Report
2017 Monitoring Program
Fourth Quarter: March 2018
1.0 Introduction 1-1
2.0 Data Review Process 2-1
3.0 Data Review for Data Package 1803136 3-1
4.0 Overall Assessment 4-1
4.1 Sensitivity 4-1
4.2 Accuracy 4-1
4.3 Precision 4-1
4.4 Completeness 4-2
4.5 Representativeness 4-2
4.6 Comparability 4-2
List of Tables
Table 1-1 Analytical Methods for Groundwater Samples
Table 2-1 Data Review Qualifier Definitions
Table 2-2 Data Review Qualifier Codes
AECOM
Payson City Landfill Data Validation Report Page 1-1
1.0 INTRODUCTION
This report presents results of the data review conducted on analytical results for the Payson City
Landfill groundwater samples collected in March 2018 as part of the fourth quarter 2017
monitoring program. Groundwater samples were collected in accordance with Utah Solid
Hazardous Waste Permitting and Management Rules R315-308-4 and R315-308-5 and 40 CFR
Part 258 Appendix I and II, and were sent to American West Analytical Laboratories (AWAL) in
Salt Lake City, Utah for analysis.
The sample analytical results were reported in one AWAL data package. Table 1-1 presents the
analytical methods conducted and parameters analyzed. The samples were analyzed for some or
all of the parameters listed in Table 1-1 as specified in Utah Solid Hazardous Waste Permitting
and Management Rules R315-308-4, R315-308-5, and 40 CFR Part 258 Appendix II. Samples
Trip Blank and FB-030718 were only analyzed for volatile organic compounds (VOCs).
The data review procedures are summarized in Section 2. Section 3 provides the results of this
review for the groundwater samples. Section 4 provides an overall assessment of the data.
AECOM
1
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Payson City Landfill Data Validation Report Page 1-2
Table 1-1
Anal tical Methods for Groundwater Sam les
Parameter Sampling and Analysis Plan
Analytical Method Current Analytical Method2
Volatile Organic Compounds
(Appendix I & II) SW846 8260B SW846 8260C/ 5030C
Semivolatile Organic
Compounds SW846 8270C SW846 8270D/ 3510C
Ammonia (as N) EPA 350.1 EPA 350.1
Bicarbonate, Carbonate (as
CaCO3) EPA 310.1 5M2320B
Chloride 5M4500 CL B EPA 300.0
Chlorinated Herbicides SW846 8151A SW846 8151A
COD HACH HACH 8000
Cyanide EPA 335.4 EPA 335.4
EDB & DBCP EPA 504 SW846 8011
Organochlorine Pesticides SW846 8081B SW846 8081B/ 3510C
Mercury 5W846 7470A SW846 7470A
Metals (Total) 5W846 6010B SW846 6010D
Metals (Total) 5W846 6020/7841 SW846 6020B1
Nitrate (as N) EPA 353.2 EPA 353.2
Polychlorinated Biphenyls SW846 8082A SW846 8082A/ 3510C
pH EPA 150.1 SM4500-H+B
Sulfide EPA 376.1 SM4500-S2-D
Sulfate EPA 375.4 EPA 300.0
TDS EPA 160.1 SM2540C
TOC EPA 415.1 SM5310B
CaCO3 = Calcium Carbonate COD = Chemical Oxygen Demand DBCP = 1,2-Dibromo-3-Chloropropane
EDB = 1,2-Dibromoethane N = Nitrogen TDS = Total Dissolved Solids
TOC = Total Organic Carbon
Appendix I & II = Parameters from 40 CFR Part 258 and those specified in Utah Solid Hazardous Waste Permitting and Management Rules
R315-308-4,and R315-308-5 SW846 = Test Methods for Evaluating Solid Wastes, SW-846 Third Edition, Final Update V, August 2015
EPA = Methods for Chemical Analysis of Water and Wastes, February 2015
SM = Standard Methods for the Examination of Water and Wastewater, January 2014
HACH = USEPA Reactor Digestion Method, February 2009
Total Metals (6010D/6020B) = Barium, beryllium, cadmium, calcium, chromium, cobalt, copper, iron, magnesium, manganese, nickel,
potassium, silver, sodium, thallium, tin, vanadium, and zinc 'Additional metals reported and not listed in the Sampling and Analysis Plan (2003) (6020B) — Antimony, arsenic, lead, and selenium
'Equivalent and/or updated methods
MCOM
Payson City Landfill Data Validation Report Page 2-1
2.0 DATA REVIEW PROCESS
A quality control (QC) review was performed on the AWAL data using guidance from the US
Environmental Protection Agency (USEPA) Contract Laboratory Program National Functional
Guidelines for Inorganic Superfund Data Review (January 2017) and for Organic Methods Data
Review (January 2017). The parameters reviewed included the following: holding time, blank
contamination, laboratory control sample (LCS) and laboratory control sample duplicate (LCSD)
results, surrogate recoveries, matrix spike (MS) and matrix spike duplicate (MSD) results, field
duplicate agreement, and method duplicate agreement. The review did not include any
recalculations or transcription error checking. Associated QC results obtained were compared to
the acceptance limits provided in the Quality Assurance Project Plan (April 2003) (QAPP) or the
historic acceptance limits used by the laboratory when not referenced in the QAPP.
This data review narrative includes a summary of any QC results outside the acceptance limits,
an explanation of all assigned qualifiers as well as any professional judgment used to assess data
usability, and an overall assessment of the data.
During the data review process, the data reviewer annotated on the analytical data sheets any
data review qualifiers assigned ("U", "J", "Ur and "R") and the associated qualifier and bias
codes. Table 2-1 provides the definitions for the data review qualifiers and Table 2-2 provides
the definitions of the qualifier and bias codes assigned. The purpose of the qualifier codes is to
provide information with regard to the data quality condition(s) that resulted in the assigned
qualification. The bias code provides an indication of the bias direction of the results qualified
as estimated based on the data quality condition(s) that resulted in the data qualification and the
other associated quality control analyses. The data qualifier codes are followed by a hyphen and
then the applicable bias code. For example, a value qualified as estimated "PUP due to a
holding time exceedance which resulted in a potential low bias in the result has the following
code annotated on the data sheet, "HT-L". In the case of multiple data quality conditions
resulting in qualification, each qualifier code is listed and separated by a comma. For example, a
result qualified as estimated "J/UJ" due to low matrix spike recovery and poor field duplicate
precision would have the following codes annotated on the data sheet, "MS, FD-L".
Table 2-1
Data Review Qualifier Definitions'
Qualifier Definition
U The analyte was analyzed for, but was not detected above the level of the reported sample
quantitation limit.
J The result is an estimated quantity. The associated numerical value is the approximate
concentration of the analyte in the sample.
UJ The analyte was analyzed for, but was not detected. The reported quantitation limit is
approximate and may be inaccurate or imprecise.
R The data are unusable. The sample results are rejected due to serious deficiencies in
meeting QC criteria. The analyte may or may not be present in the sample.
'Definitions modified from the USEPA Contract Laboratory Program National Functional Guidelines for Inorganic Superfund Data Review,
January 2017
COM
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I Payson City Landfill Data Validation Report Page 2-2

Table 2-2
Data Review Qualifier Codes
Qualifier
Code
Data Quality Condition
Resulting In Assigned Qualification
General Use
HT Holding time requirement was not met
MB Method blank or preparation blank contamination
LC S Laboratory control sample evaluation criteria not met
FB Field blank contamination
TB Trip blank contamination
FD Field duplicate evaluation criteria not met
SQL Reported sample concentration is between the method detection limit and the
sample quantitation limit.
Inorganic Methods
PB Preparation blank contamination
D Laboratory duplicate precision evaluation criteria not met
MS Matrix spike recovery outside acceptance range
Organic Methods
SUR Surrogate recovery outside acceptance range
MS/SD Matrix spike/matrix spike duplicate accuracy and/or precision criteria not met
Bias Codes Bias Direction
H Bias in sample result likely to be high
L Bias in sample result likely to be low
I Bias in sample result is indeterminate
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< — Less Than
MB — Method Blank
U — Non-detect
ttg/L — Micrograms per Liter
SIM — Selective Ion Monitoring
I — Indeterminate Bias
SVOCs — Semivolatile Organic Compounds 1
Payson City Landfill Data Validation Report Page 3-1
1
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3.0 DATA REVIEW FOR DATA PACKAGE 1803136
The results for three groundwater samples, one field duplicate, one field blank sample, and one
trip blank sample were reported in AWAL data package 1803136. The table below lists the
samples reported in this data package, the corresponding laboratory identifications (IDs), and the
QC analyses conducted.
Field Identification Laboratory
Identification Quality Control Type
Trip Blank 1803136-001 Trip Blank (VOCs Only)
MW-X 1803136-002 MD — pH
Field Duplicate to sample MW-5
MW-5 1803136-003 MS/MSD — Chloride, Sulfate
MW-6 1803136-004
MW-4 1803136-005 MS/MSD — Alkalinity, Ammonia (as N), COD, EDB &
DBCP, Metals, Nitrate (as N), TOC, SVOCs1, SVOCs
SIM', VOCs'
MD — pH, TDS
FB-030718 1803136-006 Field Blank (VOCs only)
COD — Chemical Oxygen Demand DBCP — 1,2-Dibromo-3-chloropropane
EDB — 1,2-Dibromoethane MD — Method Duplicate
MS/MSD — Matrix Spike/Matrix Spike Duphcate SIM — Selective Ion Monitoring
SVOC — Semivolatile Organic Compounds N — Nitrogen
TDS — Total Dissolved Solids TOC — Total Organic Carbon
VOCs — Volatile Organic Compounds
'The MS/MSD for the SVOCs SIM, SVOC, and VOC lists did not contain all of the analytes reported in this data package This issue is further
addressed in the Matnx Spike/ Matrix Spike Duplicate Section
Overall Assessment — The data were considered acceptable for use in meeting project objectives
with the qualifications noted in the following narrative.
Sample Receipt — The samples were hand delivered to AWAL under chain-of-custody (COC)
and were received intact. The cooler was packaged with custody seals and the temperature upon
receipt was 4.3 degrees Celsius (°C), within the recommended <6°C temperature criterion.
Therefore, data qualification was not required.
Holding Time — Holding time criteria were met for the reported analyses. Therefore, data
qualification was not required.
Method Blanks —With the exception listed in the table below, target analytes were not detected in
any of the method or calibration blanks.
Associated Samples Analyte Concentration
(WL) Data Qualification
SVOCs SIM
MB-54502
MW-X
MW-5
MW-6
MW-4
Bis(2-ethylhexyl) phthalate 1.51
The associated sample results reported at
concentrations <10x the concentration of
the blank contamination were qualified as
non-detect (U MB-I).
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AECOM 1
Payson City Landfill Data Validation Report Page 3-2 I
H — High Bias MSD — Matrix spike duplicate recovery
SVOCs — Semivolatile Organic Compounds
% — Percent %R — Percent Recovery
J — Estimated MS — Matrix spike recovery outs de acceptance range
N — Nitrogen SIM — Selective Ion Monitoring
Bold text indicates results outside of acceptance criteria.
I — Indeterminate Bias
RPD — Relative Percent Difference
UJ — Estimated
Bold text indicates results outside of acceptance criteria.
MS/SD — Matrix spike matrix spike duplicate accuracy and/or precision criteria not met
SVOCs — Semi Volatile Organic Compounds
1
I AECOM
Trip Blank — During review of that data package, it was noted that the VOC results for the trip
blank sample were not reported. The laboratory revised and reissued the data package to include
the VOC results for the trip blank sample and no further action was required.
Target VOC analytes were not detected in the trip blank. Therefore, data qualification was not
required.
Field Blank — Target VOC analytes were not detected in the field blank. Therefore, data
qualification was not required.
Matrix Spike/Matrix Spike Duplicate — With the exceptions listed in the table below, the percent
recoveries (%Rs) for the MS/MSD results were within the laboratory acceptance ranges. The
MS/MSD recoveries for calcium, magnesium, and sodium were not appropriate for assessing
accuracy and precision as the sample results were greater than four times the spike amounts.
Analyte MS %R MSD %R Acceptance
Limits CYO
_
Data Qualification
Metals
Ammonia (as N) 111 114 90-110
Because sample MW-4 was the only site-
specific sample that an MS/MSD was
performed for ammonia (as N), the detected
analytical results for the site-specific samples
were qualified as estimated (J MS-H).
Inorganics
Nitrate (as N) 105 112 90-110
Because sample MW-4 was the only site-
specific sample that an MS/MSD was
performed for nitrate (as N), the detected analytical results for the site-specific samples
were qualified as estimated (J MS-H).
SVOCs SIM
Benzo(a)pyrene 170 146 15-169
As the potential bias was considered to be
high and the other site-specific sample results
were reported as non-detect, qualification was
not considered necessary.
With the exception listed in the table below, the relative percent differences (RPDs) between the
MS/MSD results were within the laboratory acceptance ranges.
Analyte RPD RPD Limit Data Qualification
SVOCs
4,6-Dinitro-2-methylphenol 44.9 25 As sample MW-4 was the only site-specific sample
that a duplicate was performed on for SVOCs, the
associated results for the site-specific samples were
qualified as estimated (UJ MS/SD-I). Pentachlorophenol 25.6 25
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Payson City Landfill Data Validation Report Page 3-3
The MS/MSD spike solutions used by the laboratory for the VOC and SVOC analyses contained
the minimum analyte list included in the respective method. Because only a subset of target
analytes for these analyses were included in the spike solution used by the laboratory, there is no
direct measure of accuracy with respect to the site-specific sample matrix for the other
compounds; however, an acceptable level of accuracy and precision with respect to the analytical
method and site-specific sample matrix can be inferred based on the laboratory control sample
(LCS), MS/MSD results for the spiked compounds, the surrogate recoveries, and the field
duplicate results for these analytes.
The MS/MSD analyses were performed on samples that were not requested on the COC. As the
MS/MSD frequency requirement was met, further action was necessary.
LCS — LCS and/or laboratory control sample duplicate (LCSD) samples were prepared and
analyzed at the proper frequency. The recoveries were within the laboratory's acceptance range.
The LCS spike solutions used by the laboratory for the SVOC SIM, SVOC, and VOC analyses
contained the minimum analyte list contained in the respective method. Because a subset of
target analytes for these analyses were included in the spike solution used by the laboratory,
there is no direct measure of the accuracy for the other compounds for these analyses; however,
an acceptable level of accuracy with respect to the analytical method can be inferred by
acceptable LCS and MS/MSD results for spiked analytes and from the surrogate recoveries.
Surrogate Recoveries — The EDB and DBCP, SVOC, and VOC surrogate recoveries were within
the laboratory-determined acceptance limits. Per AWAL for SVOCs full scan and SVOCs SIM
Mode, surrogates are introduced to determine extraction efficiency. Since both the SIM and full
scan come from the same extract the surrogates are only reported on the full scan report since the
concentration would be too high for the SIM analysis. Therefore, the full scan surrogates
determine the recovery for both analyses.
Field Duplicate Agreement — For field duplicate sample agreement where both results were
greater than five times the reporting limit (RL), it was considered to be acceptable if the RPD
between the results was 30%. For field duplicate samples where either result was less than five
times the RLs, agreement was considered to be acceptable if the absolute difference between the
results was less than two times the lower RL [<2xRL (with the RL being used for a non-detect
result].
The field duplicate pair reported in this data package was MW-5/MW-X. The agreement
between the field duplicate pair results were within the QAPP acceptance criteria of ±30% RPD
or difference <2xRL. Therefore, data qualification was not required.
Method Duplicate Agreement — For method duplicate samples where both results were greater
than five times the RL, agreement was considered to be acceptable if the RPD between the
results was _20%. For method duplicate samples where either result was less than five times the
RLs, agreement was considered to be acceptable if the absolute difference between the results
was less than one times the lower RL [<lxRL (with the RL being used for a non-detect result].
Sample MW-X was used to prepare the method duplicate for pH and sample MW-4 was used to
prepare the method duplicate for pH and TDS. The laboratory noted that the TDS RPD was
outside the laboratory limits of 5% with a RPD of 18.5%. However, as the agreement between
the sample and method duplicate results were within the QAPP acceptance criteria of ±20% RPD
and/or a difference <lxRL, qualification was not considered necessary.
AECOM
Payson City Landfill Data Validation Report Page 3-4
Reporting Limits — Several results were analyzed and reported by multiple methods. Results
were selected for reporting using the following criteria:
• If both results were non-detect, the non-detect result with the lower reporting limit was
selected.
• If both results were reported as detected, the higher detected result was selected for
reporting.
• If one result was reported as non-detect and the other result was reported as detected, the
detected result was selected for reporting.
Other — Acrolein and acrylonitrile have a sample preservation requirement of a pH range of 4-5
as these compounds are highly reactive. The samples were preserved to pH of <2; therefore, the
associated acrolein and acrylonitrile results for the samples associated with this data package
were qualified as estimated (UJ) based on professional judgement (PJ-I).
AECOM
Payson City Landfill Data Validation Report Page 4-1
4.0 OVERALL ASSESSMENT
The 2017 monitoring program fourth quarter Payson City Landfill data are considered acceptable
for use in meeting project objectives, as qualified. A general overall assessment of data quality
indicators is provided below.
4.1 SENSITIVITY
With the exceptions list below, the reporting limits satisfied the ground water protection
standards required in the Utah Solid Hazardous Waste Permitting and Management Rules R315-
308-4 and R315-308-5.
The dinoseb reporting limit for the samples associated with this data package exceeded the
groundwater protection standard of 7.00 lig/L required for Utah Solid Hazardous Waste
Permitting and Management Rules R315-308-5. As the dinoseb results were reported as non-
detect with reporting limits above the required concentration, these results will need to be
evaluated by the end-user with respect to project objectives.
Due to method blank contamination, the bis(2-ethylhexyl) phthalate reporting limit for sample
MW-5 exceeded the groundwater protection standard of 6.00 [ig/L required for Utah Solid
Hazardous Waste Permitting and Management Rules R315-308-5. As the bis(2-ethylhexyl)
phthalate result was reported as non-detect with a reporting limit above the required
concentration, this result will need to be evaluated by the end-user with respect to project
objectives.
4.2 ACCURACY
Accuracy is defined as the degree of agreement of a measurement to an accepted reference or
true value. Accuracy was measured as the percent recovery (%R) of an analyte in a reference
standard or spiked sample. The LCS spike recoveries and surrogate recoveries satisfied the
evaluation criteria.
With the exceptions listed in Section 3, the MS/MSD recoveries for parameters spiked at an
appropriate level (greater than or equal to 25% of the parent sample concentration) satisfied the
evaluation criteria. The overall level of accuracy demonstrated by the analyses is considered
acceptable.
4.3 PRECISION
Precision is defined as the agreement between a set of replicate measurements without
assumption or knowledge of the true value. Precision of laboratory measurements was evaluated
by the comparison of method duplicate results and MS/MSD results.
With the exception listed in Section 3, the MS/MSD results for parameters spiked at an
appropriate level (greater than or equal to 25% of the parent sample concentration) satisfied the
precision evaluation criteria. Method duplicate results satisfied the precision evaluation criteria
and the overall level of precision demonstrated by TDS and pH analyses are considered
acceptable. The field duplicate results satisfied the precision evaluation criteria. As such, the
overall level of precision with respect to the matrix is considered acceptable.
Payson City Landfill Data Validation Report Page 4-2
4.4 COMPLETENESS
Completeness is defined as the ratio of the number of valid analytical results (valid analytical
results include values qualified as estimated) to the total number of analytical results requested
on samples submitted for analysis. The results were considered usable for meeting project
objectives. As such, the overall analytical completeness was 1 00%.
4.5 REPRESENTATIVENESS
Representativeness is the degree to which data accurately and precisely represent a characteristic
of a population, parameter variations at a sampling point, or an environmental condition.
Representativeness was maintained during the sampling effort by completing the sampling using
similar sampling procedures.
4.6 COMPARABILITY
Comparability expresses the confidence with which one data set can be compared to another.
Comparability can be related to accuracy and precision because these quantities are measures of
data reliability. Data are comparable if collection techniques, measurement procedures, methods
and reporting are equivalent for the samples within a sample set. To maximize comparability, all
samples covered by this report were collected and analyzed in accordance with prescribed
quality assurance and quality control measures. Additionally, as acceptable levels of overall
accuracy and precision were attained, the data within this set are considered comparable to one
another.
AECOM
Analytical Laboratory Report
/
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INORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill 60544100.4
Lab Sample ID: 1803136-002
Client Sample ID: MW-X
Collection Date: 3'7;2018 800h
Received Date: 3 7 2018 1446h
Analytical Results TOTAL METALS
Date Date M ethod Reporting Analytical
3440 South 700 West Compound Units Prepared Analyzed Used Limit Result Qual

Salt Lake Ctty, UT 84119 Antimony mg/L 3 9 .1)18 11 lah 3/20 2018 1932h SW6020/3 0.00200 < 0.00200
Arsenic mg/L 3.9hOli 1114h 3120 2018 1932h SW6C2013 0.00200 0.00584
Barium mg& 3/9:2018 1114h 320(2018 1932b SW602013 0 00200 0.0708

Phone: [phone] Beryllium mg/L 3 9'2'18 1114h 3/20/2018 I932h SW60208 0.00200 < 0.00200
Cadmium mg& 3/9 2018 1114h 3/2012018 1932h SW602013 0.000500 < 0.000500
roll Free: [phone] Calcium met, 3 9/2018 1114h 1/16/2018 121Ih SW6C1OD 5.00 204

Fax: [phone] Chromium mg/L 39/2018 Illah 3/20108 1932h SW60208 0.00200 < 0.00200
e-mail: awal n a+r al -labs.com Cobalt rng/L 3 9 2018 1114h 320/2018 1932h SW602138 0.00400 < 0 00400
Copper mg/L 3'9/2018 1114h 320/2018 1932h SW60208 0.00200 0.00603
web: www.awal-labs.com Iron mg/L 3'9'2018 1114h 3/162018 12331i SW6010D 0.100 < 0.100
Lead mg/L 19/2018 1114h 3/202018 1932h SW60208 0.00200 -' 0 00200
Magnesium mg/L 3 9'2018 1114h 31162018 I147h SW60ICD 2.00 103
Kyle F. Gross Manganese mg/L 3 9/2018 II14h 3/20/2018 1932h SW60208 0.00200 0.0778
Laboratory Director Mercury mg2 3 152018 1743h 3/1612018 90Ih SW7470A 0.000150 < 0.000150
Nickel mg/L 3/92018 1114h 3/20/2018 1932h SW602013 0.00200 0.0274

Jose Rocha Potassium mg/L 3 92018 1114h 3/16/2018 I233h SW60108 1.00 43.7

QA Officer Selenium meL 3/9/2018 1114h 3/20 2018 I932h SW602013 0.00200 < 0.00200
Silver mg/L 3(9/2018 II14h 3/20 2018 1932h SW60208 0.00200 < 0.00200
Sodium mg/L 3/912018 1114h 3/16 2018 1211h SW6010D 5.00 209
Thallium mg/L 3;92018 II iah 3/20 2018 1932h SW60208 0.00200 < 0.00200
Tin mg/L 3/92018 1114h 3116/2018 1233h SW60 IOD 0.500 < 0.500
Vanadium mg/L 319/2018 1114h 3/16 2018 I 233h SW60108 0.00500 0.00851
mg/L 3/912018 II14h 3/20 2018 I932h SW60208 0.00500 Zinc 0.0134
Repor. Date 3/21 20125 Page 2 or 84
• )WS .;•, C • • KC " *eft • wl n ). ut • • 0' i • . • r,..1.1 %),- C. • • 1.v • • •• • • P • ' • Pe • • •t:11.. • •• t X ••••• en, t • •... uf. . • Pt 01 b ;cow • • trr n . En •• • "mot,' t • • Ay • (X , ton • ‘<.e. •U.t r• • • t'eport .r • • ••• (••,,, • 'ff f, 411:r% • ervfe, • , •t• • • r • • Iv w•• • - • r :•• • •e: • • hob gr • .1
3 12:-/u-
Contact: Lawrence Cannon AECOM
Payson City Landfill 60544100.4
Client:
Project:
• •• ,•• ••••'‘ am, cI )..
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3/24/i Report Dale 1 -1101 Page 3 of 84
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" S. • • ' • • • •)* s.dr • c.a..% • • leo • '•A ••*,•• • tar • r • - mu. • . • •k. • ns..• the t • ale • .
INORGANIC ANALYTICAL REPORT
Lab Sample ID: 1803136-003
Client Sample ID: MW-5
Collection Date: 3/7/2018 1000h
Received Date: 3/7/2018 I 446h
Analytical Results TOTAL METALS
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Antimony mg/L 3/912018 1114b 3/20/2018 1935h MOM 0.00200 < 0.00200
Arsenic mg/L 3/9/2018 11141t 3/20/2018 1935h SW60208 0.00200 0.00575
Bariurn mg/L 319/2018 1114b 3/20/2018 I935h SW6020B 0.00200 0.0717
Beryllium mg/L 31912018 1114h 3/20/2018 193% SW6020B 0.00200 0.00200
Cadrniurn mg/L 3/9/2018 1114h 3/20.7018 1933h SW60208 0.000500 < 0.000500
Calcium mg/L 3/9/2018 1114h 3,16/2C18 114911 SW6010D 5.00 209
Chromium mg/L 3/912018 I Ilsh 3/70 2018 1935h SW6020B 0.00200 < 0.00200
Cobalt mg/L 99/2018 II14h 3/20/2018 1935h SW6070B 0.00400 < 0.00400
Copper mg/L 99/2018 I 11413 3/20 2018 193511 SW6020B 0.00200 0.00511
Iron mg/L 3/9/2018 1114h 3 16 2018 1235h SW601CD 0.100 -• 0.100
Lead mg/1 3/9/2018 11 lah 3/20 2018 1935h SW602013 0.00200 - 0 00200
Magnesium mg/L 3/9/2018 1114h 3 16.7018 1149h SW601OD 5.00 107
Manganese mg/L 991201f 1114h 3/10 2018 1935h SW6020B 0.00200 0.0725
Mercury mg/L 3/192018 1745h 3%920111 903h 5W7470A 0.000150 < 0.000150
Nickel mg/I. 3/9/2018 I I I4h 3/20 2018 1935h SW6020B 0.00200 0.0256
Potassium mg/L 3/9/20111 I I lah 3 162018 I235h SW6010D 1.00 44.0
Selenium mg/L 3/9/2018 1114h 3/202018 19351t SW602CB 0.00200 < 0.00200
Silver mg/L 319/2018 1114h 9202018 1935h SW6020B 0.00200 < 0.00200
Sodium mg/L 319/2018 11 lah 3/16 2018 1149h SW60101) 5 00 212
Thallium mg/L 3/9/2018 1114h 3/20 2018 1935h SW6020B 0.00200 < 0.00200
Tin mg/L 3/9/2018 1114h 3/16 2018 1235h SW6010D 0.500 < 0.500
Vanadium mg/L 3/9/2018 1114h 3/192018 1235h SW6010D 0.00500 0.00857
Zinc mg/L 3/9/2018 11141 3/292018 1935h SW6020B 0.00500 0.0115
3440 South 700 West
Salt Lake City, UT 84119
Ams z.san s. 'iecb Att•A •T A , ,A3: 5^0Alfs,
Phone. [phone]
Toll Free. [phone]
Fax: [phone]
e-mail: awal d'awal-labs.coni
wcb: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose R.ocha
QA Officer
INORGANIC ANALYTICAL REPORT_
i'Pro 'tat : '3 t
Client: AECOM
Project: Payson City Landfill ' 60544100 4
Lab Sample ID: 1803136-004
Client Sample ID: MW-6
Contact: Lawrence Cannon
A A °T colt = =to Collection Date: 3/7/2018 1115h
Received Date: 3/7/2018 1446h
Analytical Results TOTAL METALS
Date Date Method Reporting Analytical
1440 South 700 West Compound Units Prepared Analyzed Used Limit Result Qual
Salt Lake City, UT 84119 Antimony mg/L 3/912018 1114h 3/20;2018 I938h SW60208 0.00200 < 0.00200
Arsenic mg/L 3/9(2018 1114h 3/20 2018 1938h SW60208 0.00200 < 0.00200
Barium mg/L 3/9/2018 1114h 3/20 2018 1938h SW60209 0.00200 0.0686
Phone: [phone] Beryllium mg/L. 3/9/2018 111411 120.2018 1938h SW6020B 0.00200 < 0.00200
Cadmium mg/L 3/9/2018 1114h 3/20.2018 1938h SW6020B 0.000500 < 0.000500 Toll Free: [phone] Calcium mg/L 3+9/2018 1114h 3.162018 1151h SW6010D 2.00 132
Fax: [phone] Chromium mg/L 3/9'2018 1114h 120'2018 193811 SW6020B 0.00200 0.0543
e-mail: [e-mail] Cobalt mg/L 3/9/2018 II14h 3/20 2018 1938h SW6020B 0.00400 < 0.00400
Copper mg/L 3/9/2018 II I4h 3r20:2018 1938h SW6020B 0.00200 0.00420
web: www.awal-labs.com iron mg/L 3/9/2018 II14h 3 16 2018 I237h SW6010D 0.100 0.826
Lead mgil 3/9/2018 1 1 leb 3r20 2018 1938h SW60208 0.00200 < 0.00200
Magnesium mg/L 3/94018 1114h 3 1622018 1237h SW6010D 1.00 49.5
Kyle F. Gross Manganese mg/L 3/9/2018 111411 3/20 2018 1938h SW6020B 0.00200 0.0419
Laboratory Director Mercury mg/L 3/112018 1745h 1 16,2018 9051t SW7470A 0.000150 < 0.000150
Nickel mg/L 1/9/2018 1114h 3n0 2018 1938h SW60208 0.00200 0.0584
Jose Rocha Potassium mg/L 3/9/2018 1114h 3 16/2018 1237h SW60101:I 1.00 13.4
QA Officer Selenium mg/L. 3/9/2018 I114h 3/20 2018 1938h SW6020B 0.00200 0.00252
Silver mg/L 3/9/2018 1114h 3/20'2018 193811 SW6020B 0.00200 - 0.00200
Sodium mg/L 3/9/2018 I 114h 116/2018 1151h SW6010D 2.00 105
Thallium mg/L 3r9.2018 1114h 3/20;2018 1938h SW602013 0.00200 < 0.00200
Tin mg/L 3/912018 1114h 316/2018 123Th SW6010D 0.500 ': 0 500
Vanadium mg/L 3/9/2018 1114h 116 2018 123Th SW6010D 0.00500 • 0.00500
Zinc mg/L 3/9/2018 1114h 3,20•2018 1938h SW60208 0.00500 0.0228
3 f 2 lc?
Report Date 3 21 201/ Page 4 of 84
nr, .1• • 1g ' ton,' ' '3. ....I •
:1•• . •tttlt ,x1c.

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INORGANIC ANALYTICAL REPORT
At mt.; EX, Aff
Client: AECOM
Project: Payson City Landfill 60544100.4
Lab Sample ID: 1803136-005
Client Sample ID: MW-4
Contact: Lawrence Cannon
Collection Date: 3/7/2018 1230h
Received Date: 3/7/2018 1446h
Analytical Results TOTAL METALS
Date Date Method Reporting Analytical
1440 South 700 West Compound Units Prepared Analyzed Used Limit Result Qual
Salt I.ake City, UT 84119 Antimony mg/L 3 9 2C18 11148 3/20 2318 1941h SW6020B 0.00200 < 0.00200
Arsenic mg/L 3 9 2018 1114h 3,20 2018 1941h SW602GB 0.00200 '‹ 0.00200
Barium mg/L 3,9 2018 1114h 3/20:2018 19418 SW6020B 0.00200 0.109
Beryllium mg/L 3 9 2018 I 114h 3/20 2018 1941h SW6020B 0.00200 < 0.00200 Phone: [phone] Cadmium meL 119:2018 11148 3/201018 19418 SW6020B 0.000500 < 0.000500 Toll Free. [phone] Calcium mg/L. 319,2018 111411 3/16 2018 1213h SW6010D 2.00 93.0
Fax: [phone] Chromium mg& 3/9/2018 11141. 300 2018 194111 5W6020B 0.00200 0.00277
e-mail: awal c a al -labs.com Cobalt mg/L 3/912018 1114h 3/20/2018 1941h SW6020B 0.00400 < 0.00400
Copper mg/L 349/2018 1114h 3/2C2018 1941h SW60208 0.00200 < 0.00200
web: www.awal-labs.com Iron mg& 3/9/2018 11141i 3 16 2018 1153b SW6010D 0.100 0.401
Lead mg/L 3/9/2018 I I 14h 3/20 2018 1941h SW602013 0.00200 •," 0 00200
Magnesium nil. 3/9/2018 1114h 3 16/2018 1153h SW6010 D 1.00 34.6
Kyle r. Gross Manganese mg& 39/2018 I 114h 3/202018 1941h 5W6020B 0.00200 0.0429
Laboratory Director Mercury mg/L 3/15/2018 I 745h 116 2318 8$2h SW7470A 0.000150 < 0.000150
Nickel mg/L 3/9/2018 I I 14h 3/20 2318 194111 SW6020B 0.00200 0.0580
Jose Rocha Potassium mg/L 319/2018 11148 3 16'2318 1153h SW6010D 1.00 10.3
QA Officer Selenium mg& 3/9/2018 1114b 3/20 2018 194Ib 5W602013 0.00200 < 0.00200
Silver mg/1. 319n018 1114h 3/20 2018 19416 SW602011 0 00200 < 0.00200
Sodium mg/L 3:9/2018 I 114h 3,16 2018 11$3h SW6010D 1.00 68.9
Thallium mg/L 3/9f2018 1114h 3/20,2018 1941h SW6020B 0.00200 < 0.00200
Tin mgfL 19/2018 1114h 3 16/2018 I153h SW6010D 0.500 < 0.500
Vanadium mg& 3/912018 1114h 3 16/2018 1153h SW6010D 0.00500 < 0.00500
Zinc mg& 3/9/2018 1114h 3/20.2018 1941h SW6020B 0.00500 < 0.00500
60_ 3 I 2g/it/
Bei= DaIe 3 21,201 Page 5 of 84
C X • 1: :
•
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INORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill • 60544100.4
Lab Sample ID: 1803136-002
Client Sample ID: MW-X
Collection Date: 3/7/2018 800h
Received Date: 3/7/2018 1446h
Analytical Results
Date Date Method Reporting Analytical
1440 South 700 West Compound Units Prepared Analyzed Used Limit Result Qual
114 2018 64011 Salt Lake City, Ul 84119
Phone- [phone]
Toll Free. [phone]
Fax: [phone]
e-ma:l: m‘alc mtal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Ammonia (as N),T 1-‘5- N mg/t.
Bicarbonate (as mg/L
CaCO3)
Carbonate (as CaCO3)
Chemical Oxygen meL
Demand
Chloride mg/L
Nitrate (as N).T t4 mg/L
pH @ 25° C pll Units
Sulfate mg/L
Total Dissolved Solids mg/L
Total Organic Carbon _ _ mg/L
3 14 2018 9058 E350.1 0.0500
I 8/2018 800h SM2320B 10.0
38/2018 800h SM232013 10.0
3/8/2018 6I7h HACH 8C00 10.0
3/14/2018 19021i E300.0 10.0
3nn018 19478 E353.2 0.100
3/7/2018 19358 SM4500-H+B 1.00
3/1412018 19028 E300.0 75.0
3/812018 I210h SM2540C 20.0
3/1612018 14498 SM5310B 1.00
' - Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
0.127
756
< 10.0
24.0
237
13.6
6.91
299
1,600
12.6
hf. 3
Rencrt Date. 3 21.2018 Page 6 of 84
c'" • ,.": • • I I .‘. 0,5r; • .J11:, •
• 4tx.q... • . rt. • / •
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INORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill 60544100.4
Lab Sample ID: 1803136-003
Client Sample ID: MW-5
Collection Date: 172018 1000h
Received Date: 3 7 2018 I446h
Analytical Results
3440 South 700 West
Salt Lake City. UT 84119
Kyle F. Gross
Laboratory Director
Date
Prepared
Date
Analyzed
M etliod
Used
Reporting
Limit
Analytical
Result Qual
3 14 2018 6406 3.142018
382018
38 2018
3 82018
3 14 2018
3 ' 2018
3 72018
3 14 2018
3 8r-018
3 16 2018
9066
800h
800h
617h
2009h
190411
935h
2009h
I21011
1504h
E350.1
SM2320B
SM2320B
HACH 8000
E300.0
E353.2
SM4500-188B
E300.0
SM2540C
SM5310B
0.0500
10.0
10.0
10.0
10.0
0.100
1.00
75.0
20.0
1.00
0.126
748
< 10.0
26.0
252
13.1
6.62
322
1,620
1 1.7
Phone: [phone]
Toll Free: [phone]
rax: [phone]
e-mail: awalevawal-labs.com
web: www.awal-labs.com
Compound Units
Ammonia (as N)3— f-‘9.14 met-
Bicarbonate (as mg/L
CaCO3)
Carbonate (as CaCO3) mg/L
Chemical Oxygen mg/L
Demand
Chloride mg/L
Nitrate (as N) 7 h5-14 mgt.
pH @ 25 C pH Units
Sulfate mg/L
Total Dissolved Solids mg/L.
Total Organic Carbon mg&
Jose Rocha
QA Officer
3/2/-14,
•:. •r• • tv, , • • • In RC% • 3.k nrwil .• . 33•••• at14.•:.— • .3 3 .0.1t .• •• now •0.• 4: or. • •Nee ..f te.• 3:: tx •••.e.ti•et. • ty :.•••:•••.••r. :• • - - • sump- . nettwo... •
Report Date. 3/21 2018 Page 7 of 84
. . • .14A, rovple- n 113 •• • Itisr• •.3 4:- • .•ea3

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• 41)%1 • e • ...1.,..adve 4•3eten.• •3•• lido's,. •
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(It it
INORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill/60544100.4
Lab Sample ID: 1803136-004
Client Sample ID: MW-6
Collection Date: 3/7:2018 1115h
Received Date: 3/7 '2018 1446h
Analytical Results
3440 South 700 West
Salt Lake City, UT 84119
Phone. [phone]
Toll Free. [phone]
Fax. [phone]
e-mail: awal amal-labs.com
web: www awal-labs.com
Kyle V. Gross
Laboratory Director
Compound Units
Ammonia (as MT ms- mg/L
Bicarbonate (as mg/L
CaCO3)
Carbonate (as CaCO3) mg/L
Chemical Oxygen ing/L
Demand
Chloride rng/L
Nitrate (as N) tAS - 1-1 mei-
pH @ 25° C pH Units
Sul fate mg/L
Total Dissolved Solids mg/L
Total Organic Carbon mg/L
Date Date Method
Prepared Analyzed Used
3 14.2018 640h 3 14.2018 9C7h E350 1
18 2018 8C0h sm2320B
3 8 2018 800h 58.1232013
3 8,2018 61 in HACH 8000
3 14,2018 1919h E300.0
3 7 2018 1909h E353.2
3 2018 I935h SM450C-H+B
3 14 2018 I919h E300.0
3 8 2018 121Gh SM254CC
3 16,2018 1517h SM5310B
Reporting
Limit
Analytical
Result Qual
0.0500 0.0960
10.0 436
10.0 10 0
10.0 10.0
2.00 178
0.0100 0.514
1.00 6.81
15.0 82.6
20.0 828
1.00 1.74
Jose Rocha
QA Officer
3/21/1411
Report Date 3 21 201' Page 8 of 8.1
• ,tA SI • • 104 •.• .0 • t• eNI ..t. om • — rt. • .1, %.1•T• • .•"•• • •tt ..xt .u•sz. • • 54. J1. 1,.!.• • • Se • 1 • W. • st• ••• s,. •,, • , • 0.*4t. I' 04. •,t, • x ••••• • "cc. • ;KM I 1.1.0•1• t u tit •. •• ), •
••• nimet 1:••••• , • • ase • vv.. • • • • tt .•• å .••• •;.š. 43 t , .ot ik • • t \ 3334 ...V.). •
Kyle F. Gross
Laboratory Director
INORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill / 60544100.4
Lab Sample ID: 1 803 136-005
Client Sample ID: MW-4
Collection Date: 3/7/2018 1230h
Received Date: 3/7/2018 1446h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Ammonia (as N) me. 3 14 2018 640h 3 14 2018 907t. E350 I 0.0500 < 0.0500
Bicarbonate (as mg/L 3 8 20)8 800h SM2320B 10.0 326
CaCO3)
Carbonate (as CaCO3) mg/1. 3 8 2018 8008 SM232CB 10.0 < 10.0
Chemical Oxygen mg/L 3:8/2018 61711 HACH 8000 10.0 < 10.0
Demand
Chloride mg/L 3 14 2018 20596 E300.0 2.00 91.2
Nitrate (as N) T ms - ti mg/1. 31;2019 19108 E353.2 0.0100 1.02
pH @ 25 C pH Units 31 2018 2105h SM4500-H+B 1.00 7.36
Sulfate mWL 3 14 2018 2059h F.300.0 15.0 58.0
Total Dissolved Solids mg/L 3.8/2018 1210h SM2540C 20.0 472 'a
Total Organic Carbon mg/L 3 161018 1531h SM5310B — 1.00 , 1.36
- High RPD due to suspected satnple non-homogeneity or matrix intedirence.
- Matrix spate recovery indicates matrix interference. The method is in control as indicated by the LCS
3440 South 700 West
Salt Lake City, UT 84119
Phone. (80 ) 263-8686
Toll Free: [phone]
Fax. [phone]
m‘al a‘%al labi com
www.awal-labs com
Jose Rocha
QA Officer
tv._ 3 /211,
Report Date 3 21/201, Page 9 of $4 . • .e . . 7 7 • " -.1%. %in.( • • .1,141... anal • atm. '• • .0cl•,..s •

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3440 South 700 Wes(
Salt Lake City, UT 84119 Compound
CAS Reporting Analytical
Number Limit Result Qual
Report Date. 3 21 2018 Page 10 of 84
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ORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill 60544100.4
Lab Sample ID: 1803136-002B
Client Sample ID: MW-X
Collection Date: 3 7 2018 800h
Received Date: 3 7 2018 1446h Test Code: 8011-W
Analytical Results EDB & DBCP by GC/ECD Method 8011
Analyzed: 3 8 2018 954h Extracted: 3 7.2018 1730h
Units: 1.1g/1. Dilution Factor: 1 Method: SW8011
Phone: [phone]
Toll Free: [phone]
Fax : (801 ) 263-8687
e-mail: awal anmal-Iabs.com
1,2-Dibromo-3-chloropropane
1,2-Dibromoethanc
Surrogate Units: pg/L
Surr 1,2-Dibromopropane
96-12-8 0.0102 < 0.0102
106-93-4 0.0102 < 0.0102

CAS Result Amount Spiked Y. REC Limits Qual

98-75-1 0.0978 0.09703 101 60-134
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Contact: Lawrence Cannon
Test Code: 8011-W
EDB & DBCP by GC/ECD Method 8011
Client: AECOM
Project: Payson City Landfill 60544100,4
Lab Sample ID: 1803136-003B
Client Sample ID: MW-5
Collection Date: 3/7/2018 100011
Received Date: 3'7/2018 1446h
Analytical Results
1,2-Dibromo-3-chloropropanc
1,2-Dibromoethane
96-12-8 0.0102 < 0.0102
106-93-4 0.0102 < 0.0102
1
Phone: [phone]
Toll Free: [phone] Surrogate Units: ug/L CAS Result Amount Spiked % REC Limits Qual
Fax: [phone]S7 Sun: 1,2-D:bromopropane 98-75-1 0.101 0.09725 104 60-134
e-mail: awal a aual-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Analyzed: 3 8 2018 1008h Extracted: 3 7 2018 1730h
Units: ug/L
3440 South 700 West
Salt Lake City, UT 84119 Compound
Dilution Factor: 1 Method: SW8011
CAS Reporting Analytical
Number Limit Result Qual
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Report Date 3 21.2018 Page 1 I of 84 .sLor c.f.+ • MUSS • .• vro• • • . fel 4.. • .4,,sse of c••• An• r .11,41.1" •1• IOU'', • ..,11the r. rOr uf tb ; •••41.1%%.• • . .11Id 0. •rykl.• • • '• yu, 4.f ,
A I ta,•••• . • • 10 • • • • aPe •••••
MOICISer ••• tuning: • ••••• • • . tt any po;•.< vo P... • rao " •
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Client Sample ID:
Collection Date:
Received Date:
Analytical Results
AECOM
Payson City Landfill / 60544100.4
1803136-004B
MW-6
31'2018 1115h
3'7,2018 1446h
Contact: Lawrence Cannon
Test Code: 8011-W
EDB & DBCP by GC/ECD Method 8011
3440 South 700 West
An alyzed: 3 '8•2018 1022h
Units: µWI_
Extracted: 3:7'2018 1730h
Dilution Factor: 1 Method: SW8011

Salt Lake City, UT 84119 Compound
CAS
Number
Reporting Analytical
Limit Result Qual
Phone. [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal a awal-labs.corn
1,2-Dibromo-3-chloropropane
1,2-Dibromoethane
Surrogate Units: Itg/L
Surr. 1,2-Dibromopropane
96-12-8 0.0104 < 0.0104
106-93-4 0.0104 < 0.0104
CAS Result Amount Spiked % REC Limits Qual
^
98-75-1 0.0847 0.09859 85.9 60-134
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
,c
ix 'cttMe,
- • rut,,Tt Pe' .13..Lanu, •-spowtol
60- 3 Report Date 3121 2018 Page 12 (11'84
tt rsTmil -
" , t T 5,11.^Clt. 00E,
r-t nerie `v west
ORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill 60544100.4
Lab Sample ID: 1803136-005B
Client Sample ID: MW-4
Collection Date: 31 2018 1230h
Received Date: 3.7'2018 1446h Test Code: 8011-W
Analytical Results EDB & DBCP by GC/ECD Method 8011
Analyzed: 3/82018 1036h Extracted: 317;2018 1730h
Units: µg/L
3440 South 700 West
Salt Lake City, UT 84119 Compound
Dilution Factor: 1 Method: SW8011
CAS Reporting Analytical
Number Limit Result Qual
1,2-Dibromo-3-chloropropane 96-12-8 0.0102 < 0.0102
1,2-Dibromoethane 106-93-4 0.0102 < 0.0102 Phone: [phone]
Toll Free: [phone] Surrogate Units: µg/L CAS Result Amount Spiked % REC Limits Qual
Fax: [phone] Surr. 1,2-Dtbromopropane 98-75-1 0 0787 0.09693 81.2 60-134
e-mail: awal a aual-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Roc!ia
QA Officer
6k- 3 s- Report Date 3 21 2018 Pagc 13 a 84
•• • • r • r .• a t crx I ••••• • • 4t, .;.'...:.a5:5•• t Z5 a • 1..1%.11 • ••••• n..11105*, .51 tr an,
Am rict Vv 1st A' ,
ORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill 60544100.4
Lab Sample ID: 1803136-0021
Client Sample ID: MW-X
Collection Date: 3'7 2018 800h
Received Date: 3/7'2018 1446h Test Code: 8270-W-S1M-3511
Analytical Results SVOA X2 SIM List by GC/MS Method 8270D/3511
Analyzed: 3.'19,2018 1616h Extracted: 3 8 2018 1233h
3440 South 700 West
Salt Lake City, UT 84119
Units: ug/L Dilution Factor: l Method: SW8270D
Compound
CAS Reporting Analytical
Number Limit Result Qual
Benzo(a)pyrene 50-32-8 0.0972 < 0.0972
Bis(2-ethylhexyl) phthalate let - 1 117-81-7 0:0402-2 Al 2.94 Phone: [phone] Hexachlorobenzene 118-74-1 0.972 < 0.972 Toll Free: [phone] Pentachlorophenol 87-86-5 0.972 < 0.972 Fax: [phone]
e-mail: awal a awal-labs.coni 8 - Elis(2-ethylhexy8phrhalate was present in the method blank at 1 51 pg L Levels of this compound at this concentration is a common contaminant and expected.
web: www.awal-lab,.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
3 tziki/P
Report Date 3/21 2018 Page 14 of 84

,s• • .1•4 • • ' • rate • • one. r • •nunt ..ata•••: " I ^ I'th : ""ar. •" •.••••14.4 •<• ts.. • • t••• a a eir.bv • • • •a•nx . • J.,' • WI. • .0 fr• e pt • ..e.y g, • Ac (It• • •p gar • ettr,...• • Tv :11 to,* ',4•1 • .1:Tre • CS: • '1 • • • • t•h• 8110 1' ;hi ." 11)•.0
in . A 'FICA ;,A'
Result Qual
3440 South 700 West
Salt Lake City, UT 84119 Compound
CAS Reporting Analytical
Number Limit
ORGANIC ANALYTICAL RE C :1T
Contact: Lawrence Cannon Client:
Project:
Lab Sample ID:
Client Sample ID:
Collection Date:
Received Date:
AECOM
Payson City Landfill 60544100.4
1803136-0031
MW-5
172018 1000h
3.72018 1446h Test Code: 8270-W-S1M-351 1
Analytical Results SVOA X2 SIM List by GC/MS Method 8270D/3511
Analyzed: 3/19/2018 1638h Extracted: 318,2018 1233h
Units: pg/L Dilution Factor: 1 Method: SW8270D
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal a awal-labs.com
Benzo(a)pyrene
Bis(2-ethylhexyl) phthalate CA Ft
Hexachlorobenzene
Pentachlorophenol
50-32-8
117-81-7
118-74-1
87-86-5
0.0969 < 0.0969
04)9697 • 32' 7.38
0.969 < 0.969
0.969 < 0.969
B - Bis12-ethy1heOpli1halate was present in the method blank at I 51 pg L Levels of this compound at this concentration is a common
contaminant and expected
web: www.awal-labs com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
1,1 hrœ.v?,
12C-l N1r) 2 • D:,ff,
Repoli Date 3'21 2018 Page 15 of 84
•rs erg" WA,
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
6,2
o
f<ir ( ,••
M :Ns ta...
Repon Date 3/21-2018 Page 16 of 84
. 3 • • t•r,.•s5sj5Ile : • ..3C lit • • x, A MI .t•• • prt • a. tlesc, • ...sit •
r • f • 3.1." tire"... '313
ORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill 60544100 4
Lab Sample ID: 1803136-0041
Client Sample ID: MW-6
Collection Date: 31'2018 1115h
Received Date: 3/7.2018 1446h Test Code: 8270-W-SIM-3511
Analytical Results SVOA X2 SIM List by GC/MS Method 8270D/3511
Analyzed: 319 2018 1701h Extracted: 3 8 2018 1233h
Units: 141.. Dilution Factor: 1 Method: SW8270D
3440 South 700 West
I Salt Lake City, Lif 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal a m%al-labs.com
CAS
Number
Reporting
Limit
Analytical
Result Qual
50-32-8 0.0975 < 0.0975
117-81-7 0.0975 < 0.0975
118-74-1 0.975 < 0.975
87-86-5 0.975 < 0.975
Compound
Benzo(a)pyrene
Bis(2-ethylhexyl) phthalate
llexachlorobenzene
Pentachlorophenol
1
ORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill 60544100.4
Lab Sample ID: 1803136-0051
Client Sample ID: MW-4
Collection Date: 3/7.2018 1230h
Received Date: 3 7 2018 1446h Test Code: 8270-W-SIM-3511
Analytical Results SVOA X2 SIM List by GC/MS Method 8270D/3511
Analyzed: 3 19/2018 1723h Extracted: 3'8 7018 1233h
Units: pg/L
3440 South 700 West
Salt Lake City, UT 84119 Compound
Dilution Factor: l Method: SW82700
CAS Reporting Analytical
Number Limit Result Qual
Benzo(a)pyrene 50-32-8 0.0969 < 0.0969
Bis(2-ethylhexyl) phthalate tat 6 -7 117-81-7 049,69 ( . k 2- 1.82 B
Hexachlorobenzene 118-74-1 0.969 < 0.969
Pentachlorophenol 87-86-5 0.969 < 0.969

• - Matrix spike recovery indicates matrix interference. The method is in control as tmlicated by the LCS
B - Bas(2-ethylhexyl)phthalate was present m the method blank at I 51 pg L Levels of this compound at this concentration is a common
contaminant and expected.
Phone: [phone]
Tol 1 Frce• [phone]
Fax: [phone]
e-inail: awal a an al-labs.com
web: www.awal-lab.:.corn
tbe 3/241e
Rcpott Chic 3 21,2018 Page 17 of 84
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
• • 1 .50 a; ) • • .t , • f.tngtl• • • pi 410. •.11 nce• d MO/ . • hed
, -clerk r.
ANA T• 4 , OR
Client:
Project:
Lab Sample ID:
Client Sample ID:
Collection Date:
Received Date:
Analytical Results
AECOM
Payson City Landfill 60544100.4
1803136-0021
MW-X
3 7 2018 800h
37'2018 1446h
ORGANIC ANALYTICAL REPORT
Contact: Lawrence Cannon
Test Code: 8270-W-3511
SVGA X2 List by GC/MS Method 8270D/3511
3440 South 700 West
Salt Lake City, UT 84119
None: 001) 263-8686
Toll Free: [phone]
Fax. [phone]
e-mail. awa: waal-labs.com
web: www.awal-lab.corn
Kyle F. Gross
1.aboratory Director
Jose Rocha
QA Officer
Analyzed: 3/9 2018 1511h Extracted: 3,8 2018 1233h
Units: µg/L Dilution Factor: 1 Method: SW8270D
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
1,2,4,5-Tetrachlorobenzene 95-94-3 9.72 < 9.72
1,3,5-Trinitrobenzene 99-35-4 9.72 < 9.72
1,3-Dinitrobenzene 99-65-0 9.72 < 9.72
1,4-Naphthoquinone 130-15-4 9.72 < 9.72
1,4-Phenylenediamine 106-50-3 9.72 < 9.72
1-Naphthylamine 134-32-7 9.72 < 9.72
2,3 4,6-Tetrachlorophenol 58-90-2 9.72 < 9.72
2,4,5-Trichlorophenol 95-95-4 9.72 < 9.72
2,4,6-Trichlorophenol 88-06-2 9.72 < 9.72
2,4-Dichlorophenol 120-83-2 9.72 < 9.72
2,4-Dimethylphenol 105-67-9 9.72 < 9.72
2,4-Dinitrophenol 51-28-5 9.72 < 9.72
2,4-Dinitrotoluene 121-14-2 9.72 < 9 72
2,6-Dichlorophenol 87-65-0 9.72 < 9.72
2,6-Dinitrotoluene 606-20-2 9.72 < 9.72
2-Acetylaminofluorene 53-96-3 9.72 < 9.72
2-Chloronaphthalene 91-58-7 9.72 < 9.72
2-Chlorophenol 95-57-8 9.72 < 9.72
2-Methylnaphthalene 91-57-6 9.72 < 9.72
2-Methylphenol 95-48-7 9.72 < 9.72
2-Naphthylamine 91-59-8 9.72 < 9.77
2-Nitroaniline 88-74-4 9.'72 < 9.72
2-N itrophenol 88-75-5 9 72 < 9.72
3&4-Methylphenol 9.72 < 9.72
3,3 '-Dichlorobenzidine 91-94-1 9.72 < 9.72
3,3 -Dimethylbenzidine 119-93-7 9.72 < 9.72
3-Methylcholanthrene 56-49-5 9.72 < 9.72
3-Nitroanihne 99-09-2 9.72 < 9.72
4,6-Dinitro-2-methylphenol (./fT P-AS J S 534-52-1 9.72 < 9.72
bit 31 28 fik
Repon Dale 3. : :018
M
Jr) th ; a 1 •
=, West A .4 ',TIC. %)1.,PATt
3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
awal awal-labs.com
web: www.awa1-labs.com
Kyle F. Gross
Laboratory Directoi
Jose Rocha
QA Officer
Lab Sample ID: 1803136-0021
Client Sample ID: MW-X
Analyzed: 3 9 2018 1511h Extracted: 3,8
Units: lig/L Dilution Factor:
2018 1233h
1 Method: SW8270D
Compound
CAS
Number
Reporting
Limit
Analytical
Result Quai
4-Aminobiphenyl 92-67-1 9.72 < 9.72
4-Bromophenyl phenyl ether 101-55-3 9.72 < 9.72
4-Chloro-3-methylphenol 59-50-7 9.72 < 9.72
4-Chloroaniline 106-47-8 9.72 < 9.72
4-Chlorophenyl phenyl ether 7005-72-3 9.72 < 9.72
4-Nitroaniline 100-01-6 9.72 < 9.72
4-Nitrophenol 100-02-7 9.72 < 9.72
5-Nitro-o-toluidine 99-55-8 9.72 < 9.72
7,12-Dimethylbenz(a)anthracene 57-97-6 9 72 < 9 72
a,a-Dimethylphenethylamine 122-09-8 48.6 < 48.6
Acenaphthene 83-32-9 9.72 < 9.72
Acenaphthylene 208-96-8 9.72 < 9.72
Acetophenone 98-86-2 9.72 < 9.72
Anthracene 120-12-7 9.72 < 9.72
Benz(a)anthracene 56-55-3 9.72 < 9.72
Betme4OPYfate- D 50 32 8 9.72 2 .
Benzo(b)fluoranthene 205-99-2 9.72 < 9.72
Benzo(g,h,i)perylene 191-24-2 9.72 < 9.72
Benzo(k)fluoranthene 207-08-9 9.72 < 9.72
Benzyl alcohol 100-51-6 9.72 < 9.72
Bis(2-chloroethoxy)methane 111-91-1 9.72 < 9.72
Bis(2-chloroethyl) ether I l 1-44-4 9.72 < 9 72
Bis(2-chloroisopropyl) ether 108-60-1 9.72 < 9.72
1349R-ethytheitpitt4alete--D F. 1.4 117-81-7 9.72 9.72
Butyl benzyl phthalate 85-68-7 9.72 < 9.72
Chlorobenzilate 510-15-6 9.72 < 9.72
Chrysene 218-01-9 9.72 < 9.72
Diallate (cis or trans) 2303-16-4 9.72 < 9 72
Dibenz(a,h)anthracene 53-70-3 9.72 < 9.72
Dibenzofuran 132-64-9 9.72 < 9.72
Diethyl phthalate 84-66-2 9.72 < 9.72
Dimethoate 60-51-5 9.72 < 9.72
Dimethyl phthalate 131-11-3 9.72 < 9.72
Dimethylaminoazobenzene 60-11-7 9.72 < 9.72
Di-n-butyl phthalate 84-74-2 9 72 < 9.72
Di-n-octyl phthalate 117-84-0 9.72 < 9.72
3 f2e-PF
Report Datc: 3/21/2018 Page 19 of 84

1,3%-1 • • ( Ottilde00.11 31111,114.11t1(00401,40 1111 rmflAlI, ',. •!.0 :3 Sc w • k tht , •-• • Jr. r” . Of 141/4 41011) Maki Of pram. or .11(1,411%01.0% IN! rcne. „ . • . sts 110411 b,,h afld according to te nites 01 the
Analyzed: 3 9 2018 1511h Extracted: 3 8 2018 1233h
Units: 1.Lg 'L Dilution Factor: 1 Method: SW8270D
Result Qua!
CAS Reporting Analytical
Number Limit
• ' • `. ' • ,
k. 3 f 2 e //1-'
of; Pt ‘It P • • x• ad.ero: • • •• nort, -
Rcpurt Date 3/21 2 .18 Puge 20 of 84 s ot thc • Vtmi • '
' t' • • ve . a • •• •...• e t. • '.rests• o .1 • am*, • `: • • ,`,...•PIPt cur Or ev J.§ 4 ez• •. • raripar., •
Lab Sample ID: 1803136-0021
Client Sample ID: MW-X
Dinoseb 88-85-7 9.72 < 9.72
Diphenylamine 122-39-4 9.72 < 9.72
Disulfoton 298-04-4 9.72 < 9.72
Ethyl methanesulfonate 62-50-0 9.72 < 9.72
Famphur 52-85-7 9 72 < 9.72
Fluoranthene 206-44-0 9.72 < 9.72
Fluorene 86-73-7 9.72 < 9.72
1-1414a41osobenzeue. 118-74-1 9.72 < 9.72
Hexachlorobutadiene 87-68-3 9.72 < 9.72
Hexachlorocyclopentadiene 77-47-4 9.72 < 9.72
Hexachloroethane 67-72-1 9.72 < 9.72
Hexachloropropene 1888-71-7 9.72 < 9.72
Indeno(1,2,3-cd)pyrene 193-39-5 9.72 < 9.72
Isodrin 465-73-6 9.72 < 9.72
lsophorone 78-59-1 9.72 < 9.72
lsosafrole 120-58-1 9.72 < 9.72
Kepone 143-50-0 9.72 < 9.72
Methapyrilene 91-80-5 9.72 < 9.72
Methyl methanesulfonate 66-27-3 9.72 < 9.72
Methyl parathion 298-00-0 9.72 < 9.72
Nitrobenzene 98-95-3 9.72 < 9.72
N-Nitrosodiethylamine 55-18-5 9.72 < 9.72
N-Nitrosodimethylamine 62-75-9 9.72 < 9.72
N-Nitrosodi-n-butylamine 924-16-3 9.72 < 9.72
N-Nitrosodi-n-propylamine 621-64-7 9.72 < 9.72
N-N itrosodiphenylarntne 86-30-6 9 72 < 9.72
N-Nitrosomethylethylamine 10595-95-6 9.72 < 9.72
N-Nitrosopiperidine 100-75-4 9.77 < 9.72
N-Nitrosopyrrolidine 930-55-2 9.72 < 9.72
0,0,0-Triethyl phosphorothioate 126-68-1 9.72 < 9.72
o-Toluidine 95-53-4 9.72 < 9.72
Parathion 56-38-2 9.72 < 9.72
Pentachlorohenzene 608-93-5 9 72 < 9.72
Pentachloronitrobenzene 82-68-8 9 72 < 9.72
Penteeklefophenel- .9.72 9.73
Phenaceun 62-44-2 9 72 -: 9.72
I 3440 South 700 West
Salt Lake City, UT 84119
Phor.e: [phone]
Tol I Free. [phone]
Fax: [phone]
awai e: a \ % al-labs.com
web: www.awal-labs com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
A <A1YT ,:A
3440 South 700 West
Salt Lake City, UT 84119
Lab Sample ID: 1 803 136-0021
Client Sample ID: MW-X
Analyzed: 3 9 2018 1511h
Units: p.g/L
Extracted: 3,8 2018 1233h
Dilution Factor: 1 Method: SW8270D
Compound
CAS Reporting
Number Limit
Analytical
Result Qual
Phenanthrene
Phenol
Phorate
Pronamide
Pyrene
Safrole
Thionazin
Surrogate (Jolts: ugL CAS
85-01-8
108-95-2
298-02-2
23950-58-5
129-00-0
94-59-7
297-97-2
Result Amount Spiked
9.72
9.72
9.72
9.72
9.72
9.72
9.72
% REC
< 9.72
< 9.72
< 9.72
< 9.72
< 9.72
< 9.72
< 9.72
Limits Qual
Sum 2,4,6-Tribromophenol 118-79-6 42 4 48.59 87.3 10-310
Sum: 2-Fluorobiphenyl 321-60-8 30.3 24.30 125 10-230
Sum 2-F1uorophenol 367-12-4 28.6 48 59 58.9 10-120
Sum Nnrobenzere-d5 4165-60-0 32 5 24.30 134 10-253
Sum Phenol-d6 13127-88-3 22.5 48 59 46.4 10-110
Surr. Terphenyl-d14 1718-51-0 31 3 24 30 129 10-255
Phone: [phone]
Toll Free: [phone]
Fa,t [phone]
e-mail: awal al-labs.com
web: www.awal-labs com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
3 12-&-)lt Report Da:e 3 21 2018 Pap 2 l 01'84
::)14.4,1:k•tUd, • ws u twouw „e • • XVII A•th • • • • I
Client:
Project:
Lab Sample ID: 1803136-0031
Client Sample ID: MW-5
AECOM Contact: Lawrence Cannon
Payson City Landfill 60544100.4

Rep ts Date: 3:2 •::
• " • • Inlott •t • e .• the
4 MVO t. 4.1 •,ht 'uric) AN
• , • • • 4 11 0,11, , •,
gnaw Cl‘• •-• 1/. V • •. C - ,.•. ept
3440 South 700 West
Salt Lake City, UT 84:19
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal tva‘%al-labs.com
web: www.awal-labs com
Kyle F. Gross
Laboiatory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Collection Date: 3 7 2018 1000h
Received Date: 3 7 2018 1446h
Analytical Results
Test Code: 8270-W-3511
SVOA X2 List by GC/MS Method 8270D/3511
Analyzed: 3'9 2018 1534h Extracted: 3'8 2018 I233h
Units: ig L Dilution Factor: 1 Method: SW8270D
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
1,2,4,5-Tetrachlorobenzene 95-94-3 9.69 < 9.69
1,3,5-Trinitrobenzene 99-35-4 9.69 < 9.69
I,3-Dinitrobenzene 99-65-0 9.69 < 9.69
1,4-Naphthoquinone 130-15-4 9.69 < 9.69
1,4-Phenylenediamine 106-50-3 9.69 < 9.69
1-Naphthylamine 134-32-7 9.69 < 9.69
2,3,4,6-Tetrachlorophenol 58-90-2 9.69 < 9.69
2,4,5-Trichlorophenol 95-95-4 9.69 < 9.69
2,4,6-Trichlorophenol 88-06-2 9.69 < 9.69
2,4-Dichlorophenol 120-83-2 9.69 < 9.69
2,4-Dimethylphenol 105-67-9 9.69 < 9.69
2,4-Dinitrophenol 51-28-5 9.69 < 9.69
2,4-Dinitrotoluene 121-14-2 9 69 < 9.69
2,6-Dichlorophenol 87-65-0 9 69 < 9.69
2,6-Dinitrotoluene 606-20-2 9.69 < 9.69
2-Acetylaminofluorene 53-96-3 9.69 < 9.69
2-Chloronaphthalene 91-58-7 9.69 < 9.69
2-Chlorophenol 9S-57-8 9.69 < 9.69
2-Methylnaphthalenc 91-57-6 9.69 < 9.69
2-Methylphenol 95-48-7 9.69 < 9.69
2-Naphthylamine 91-59-8 9.69 < 9.69
2-Nitroaniline 88-74-4 9.69 < 9.69
2-Nitrophenol 88-75-5 9.69 < 9.69
3&4-Methylphenol 9.69 < 9.69
3,3"-Dichlorobenzidine 91-94-1 9.69 9.69
3,3*-Dimethylbenzidine 119-93-7 9.69 < 9.69
3-Methylcholanthrene 56-49-5 9 69 < 9.69
3-Nitroaniline 99-09-2 9.69 < 9 69
4,6-Dinitro-2-methylphenol 14J frtS Is b 534-52-1 9.69 < 9.69
Amer, -an Wes A ,A tieDRA"
3440 South 700 West
Salt Lake City, LT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-tna I : awal e al-labs.corn
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Lab Sample ID: 1803136-0031
Client Sample ID: MW-5
Analyzed: 1'9;2018 1534h
Units: µWI.
Extracted: 3/8'2018 I 233h
Dilution Factor: 1 Method: SW8270D
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
4-Aminobiphenyl 92-67-1 9.69 < 9 69
4-Bromophenyl phenyl ether 101-55-3 9.69 < 9.69
4-Chloro-3-methylphenol 59-50-7 9.69 < 9.69
4-Chloroaniline 106-47-8 9.69 < 9.69
4-Chlorophenyl phenyl ether 7005-72-3 9.69 < 9.69
4-Nitroaniline 100-01-6 9.69 < 9 69
4-Nitrophenol 100-02-7 9.69 < 9.69
5-Nitro-o-toluidine 99-55-8 9.69 < 9.69
7,12-Dimethylbenz(a)anthracene 57-97-6 9.69 < 9.69
a,a-Dimethylphenethylarnine 122-09-8 48.5 < 48.5
Acenaphthene 83-32-9 9.69 < 9.69
Acenaphthylene 208-96-8 9.69 < 9.69
Acetophenonc 98-86-2 9.69 < 9.69
Anthracene 120-12-7 9.69 < 9.69
Benz(a)anthracene 56-55-3 9.69 < 9.69
IlenaefavyFene C) N - •---. 50 32 - 8
Benzo(b)fiuoranthene 205-99-2 9.69 < 9.69
Benzo(g,h,i)perylene 191-24-2 9.69 < 9.69
Benzo(k)fluoranthene 207-08-9 9.69 < 9.69
Benzyl alcohol 100-51-6 9.69 < 9.69
Bis(2-chloroethoxy)methane 111-91-1 9.69 < 9.69
Bis(2-chloroethyl) ether 111-44-4 9.69 < 9.69
Bis(2-chloroisopropyl) ether 108-60-1 9.69 < 9 69
gif42.alpiihe,y1) ri,th3tatp pp4 81 3 .117 449
Butyl benzyl phthalate 85-68-7 9.69 < 9.69
Chlorobenzilate 510-15-6 9.69 < 9.69
Chrysene 218-01-9 9.69 < 9.69
Diallate (cis or trans) 2303-16-4 9.69 < 9.69
Dibenz(a,h)anthracene 53-70-3 9.69 < 9.69
Dibenzofuran 132-64-9 9.69 < 9.69
Diethyl phthalate 84-66-2 9.69 < 9 69
Dimethoatc 60-51-5 9.69 < 9.69
Dirnethyl phthalate 131-11-3 9.69 < 9 69
Dimethylaminoazobenzene 60-11-7 9.69 < 9.69
Di-n-butyl phthalate 84-74-2 9.69 < 9 69
Di-n-octyl phthalate 117-84-0 9.69 < 9.69
be 312-1- Report Date 3/21/2u8' ;:.1- 23 Qi >s-
z - •• • • Cov.,:er • -st. • • tka tor, Ilittte4 08
't3 Tpr 48,8stillC ortn• • •• • OtX ' ' Sled 0^ .40:111oft nt :a 5. 7,
• • " • " j. • and as ,• 1,..• • •.• 1. tit traile.;-• - ••
Arrtt,':,-;can 'A • ,••414k. t An,,caTca-•
3440 South 700 West
Salt Lake City, UT 84119
Pnone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal i rmal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Lab Sample ID: 1803136-0031
Client Sample Ill: MW-5
Analyzed: 3,9,2018 1534h Extracted: 38
Units: ug/L Dilution Factor:
2018 1233h
l Method: SW8270D
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
Dinoseb 88-85-7 9.69 < 9.69
Diphenylamine 122-39-4 9.69 < 9.69
Disulfoton 298-04-4 9.69 < 9.69
Ethyl methanesulfonate 62-50-0 9.69 < 9.69
Famphur 52-85-7 9.69 < 9.69
Fluoranthene 206-44-0 9.69 < 9.69
Fluorene 86-73-7 9.69 < 9.69
Nexachlarabenzent D N 118 74 1 9.69
Hexachlorobutadiene 87-68-3 9.69 < 9.69
Hexachlorocyclopentadiene 77-47-4 9.69 < 9,69
Hexachloroethane 67-72-1 9.69 < 9.69
Hexachloropropene 1888-71-7 9.69 < 9.69
lndeno(1,2,3-cd)pyrene 193-39-5 9.69 < 9.69
lsodrin 465-73-6 9.69 < 9.69
lsophorone 78-59-1 9.69 < 9 69
lsosafrole 120-58-1 9.69 < 9.69
Kepone 143-50-0 9.69 < 9.69
Methapyrilene 91-80-5 9.69 < 9.69
Methyl mcthanesulfonate 66-27-3 9.69 < 9.69
Methyl parathion 298-00-0 9.69 < 9.69
Nitrobenzene 98-95-3 9.69 < 9.69
N-Nitrosodiethylamine 55-18-5 9.69 < 9.69
N-Nitrosodimethylamine 62-75-9 9.69 < 9.69
N-Nitrosodi-n-butylamine 924-16-3 9.69 < 9.69
N-Nitrosodi-n-propylamtne 621-64-7 9.69 < 9.69
N-Nitrosodiphenylamine 86-30-6 9.69 < 9.69
N-Nitrosornethylethylamine 10595-95-6 9.69 < 9.69
N-Nitrosopiperidine 100-75-4 9.69 < 9.69
N-Nitrosopyrrolidine 930-55-2 9.69 < 9.69
0,0,0-Triethyl phosphorothioate 126-68-1 9.69 < 9.69
o-Toluidine 95-53-4 9.69 < 9 69
Parathion 56-38-2 9.69 < 9.69
Pentachlorohenzene 608-93-5 9 69 < 9 69
Pentachloronitrobenzene 82-68-8 9.69 < 9 69
PemaebieFephenei- DN -
Phenacetin 62-44-2 9.69 9,69
N•414...to t . • • t t Kett ••••• .•••••
312fr I IS, Repon Date 3 . ;'-:•%
• tt•Ilem Win • • • <tthcosnsz • • . • •t •\• t `••• :-• :s•'POt•••,ther thrn . • • r•t e•A. e i(an) tr ••• •rf-12•1 e • • • • • •• ,tf
car West
3440 South 700 West
Salt Lake City. UT 84119
Lab Sample ID: 1803136-0031
Client Sample ID: MW-5
Analyzed: 3 92018 1534h Extracted: 3 8 2018 1233h
Units: pg/L Dilution Factor: 1 Method: SW8270D
CAS Reporting Analytical
Compound Number Limit Result Qual
Phenanthrene 85-01-8 9.69 < 9.69
Phenol 108-95-2 9.69 < 9.69
Phorate 298-02-2 9.69 < 9.69
Pronamide 23950-58-5 9.69 < 9.69
Pyrene 129-00-0 9.69 < 9.69
Safrole 94-59-7 9.69 < 9.69
Thionazin 297-97-2 9.69 < 9.69
Surrogate Units: pg/L CAS Result Amount Spiked % REC Limns Qual
Surr 2.4.6-Tribrornophenol 118-79-6 44 5 48.47 91 7 10-310
Sum 2-Fluorobipaenyl 32: -60-8 26.5 24.24 109 10-230
Surr: 2-Fluorophenol 367-12-4 31.2 48.47 64.3 10-120
Surr: Nitrobenzene-d5 4165-60-0 26 4 24.24 109 10-253
Surr Phenol-d6 13127-88-3 23.5 48.47 48 5 10-110
Surr: Terphcnyl-d14 1718-51-0 25.1 24.24 103 10-255
Phone- [phone]
Tol I Free: [phone]
Fax: [phone]'7
C-Mal I: awal a aal-labs.corn
web: www awal-labs.com
Kyle F. Gross
Laboratory D!rector
Jose Rocha
PA Officer
312-e-
Report Date 3/21,2018 Page 25 of 84 • • • si 4%.31c•I. ACV itsa " $u• • %.,1,1:43qa." • • f. • ./ Airl kr he C t • t .0a

4 • vl.sitnespent tr ••• 2 x• : • • t • •. rm•or A the ad•rr,*•••,4•-,

, cu•Xt h.a0,•ritr: tr..- • $.: • •• •• :het r • . • • (*Cr A.: 41. ve At Irrese, • • th `• .• to. ••••:, i.rt • 4,0 tc. eurr
,ftr' tic
3440 South 700 West
111 Salt Lake City, UT 84:19 Compound
CAS Reporting Analytical
Number Limit Result Qua(
ORGANIC ANALYTICAL REPORT
Client: AECOM
Project: Payson City Landfill 60544100.4
Lab Sample ID: 1803136-0041
Client Sample ID: M W-6
Collection Date: 3•7 2018 1115h
Received Date: 3 7 2018 1446h
Contact: Lawrence Cannon
Test Code: 8270-W-3511
Analytical Results SVOA X2 List by GC/MS Method 8270D/3511
Analyzed: 3 9 2018 1556h Extracted: 3 82018 1233h
Units: µO.. Dilution Factor: 1 Method: SW8270D
Phone. [phone]
Toll Free: [phone]
Fax: [phone]
e-mail. awal m%al-labs com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
1,2,4,5-Tetrachlorobenzene
1,3.5-Trinitrobenzene
1,3-Dinitrobenzene
1,4-Naphthoquinone
1,4-Phenylenediamine
1-Naphthylamine
2,3,4,6-Tetrachlorophenol
2,4,5-Trichlorophenol
2,4,6-Trichlorophenol
2,4-Dichlorophenol
2,4-Dimethylphenol
2,4-Dinitrophenol
2,4-Dinitrotoluene
2,6-Dichlorophenol
2,6-Dinitrotoluene
2-Acetylaminofluorene
2-Chloronaphthalene
2-Chlorophenol
2-Methylnaphthalene
2-Methylphenol
2-Naphthylamine
2-Nitroaniline
2-Nitrophenol
3&4-Methylphenol
3,3 '-Dichlorobenzidine
3,3 '-Dimethylbenzidine
3-Methylcholanthrene
3-Nitroanihne
4.6-Dmitro-2-methylphenol (5b-2"
95-94-3
99-35-4
99-65-0
130-15-4
106-50-3
134-32-7
58-90-2
95-95-4
88-06-2
120-83-2
105-67-9
51-28-5
121-14-2
87-65-0
606-20-2
53-96-3
91-58-7
95-57-8
91-57-6
95-48-7
91-59-8
88-74-4
88-75-5
91-94-1
119-93-7
56-49-5
99-09-2
534-52-1
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9 75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9 75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9 75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
9.75 < 9.75
6t 312f /IP Report Date' Paw. "34
-gy, • • . •••)••• :.•.k.% • . rer •r"... • . • -• • 4 ••55.4,. • 5 • I sy I. • • '.•••• e. :Or • I • nr. • in^ • 4 • • 110 • <•,••• • • • •
• • ,i)c. • • .• • Ask -5155 :s •••• .; • z.s• , 4 S. • s q, • • s', s's %s sm. the .•;• -ew zzxr,.• • a, • tna ; sl• • • M) • . , s • . is.
Rep n Date' . 8 ib Q. 3 / cf / I cP
Lab Sample ID: 1803136-0041
Client Sample ID: MW-6
Analyzed: 3 9,2018 1556h Extracted: 3 8
Units: pgIL Dilution Factor:
2018 1233h
1 Method: SW8270D
CAS Reporting Analytical
Compound Number Limit Result
4-Aminobiphenyl 92-67-1 9.75 < 9.75
4-Bromophenyl phenyl ether 101-55-3 9.75 < 9.75
4-Chloro-3-rnethylphenol 59-50-7 9.75 < 9.75
4-Chloroaniline 106-47-8 9.75 < 9.75
4-Chlorophenyl phenyl ether 7005-72-3 9.75 < 9.75
4-Nitroaniline 100-01-6 9. 75 < 9.75
4-Nitrophenol 100-02-7 9.75 < 9.75
5-Nitro-o-toluidine 99-55-8 9.75 < 9.75
7,12-Dimethylbenz(a)anthracene 57-97-6 9.75 < 9 75
a,a-Dimethylphenethylamine 122-09-8 48.7 < 48.7
Acenaphthene 83-32-9 9 75 < 9.75
Acenaphthylene 208-96-8 9.75 < 9.75
Acetophenone 98-86-2 9.75 12.8
Anthracene 120-12-7 9.75 < 9.75
Benz(a)anthracene 56-55-3 9.75 < 9.75
Beivrefu)pyrene- bt\1g. •
Benzo(b)fluoranthene 205-99-2 9 75 < 9.75
Benzo(g,h,i)perylene 191-24-2 9.75 < 9.75
Benzo(k)fluoranthene 207-08-9 9 75 < 9.75
Benzyl alcohol 100-51-6 9.75 < 9.75
Bis(2-chloroethoxy)mcthanc 111-91-1 9.75 < 9.75
Bis(2-chloroethyl) ether 111-44-4 9.75 < 9.75
Bis(2-chloroisopropyl) ether 108-60-1 9.75 < 9.75
gi i17 -9.75 .75 Dis4-2-€4140h4KY44-Ph444143- DN TZ-
Butyl benzyl phthalate 85-68-7 9.75 < 9.75
Chlorobenzilate 510-15-6 9.75 < 9.75
Chrysene 218-01-9 9.75 < 9.75
Diallate (cis or trans) 2303-16-4 9.75 < 9.75
Dibenz(a,h)anthracene 53-70-3 9.75 < 9.75
Dibenzofuran 132-64-9 9.75 < 9.75
Diethyl phthalate 84-66-2 9.75 < 9.75
Dimethoate 60-51-5 9.75 < 9.75
Dimethyl phthalate 131-11-3 9.75 < 9.75
Dimethylaininoazobenzene 60-11-7 9.75 < 9.75
Di-n-butyl phthalate 84-74-2 9.75 < 9.75
Dt-n-octyl phthalate 117-84-0 9.75 < 9.75
,t
- • t•tst-
Yri At CtR 141,
3440 South 700 West
Salt Lake City. t 1 84119
Phone: [phone]
Toll Free- [phone]
Fax: [phone]
e-mail: awal a a% al-labs corn
web: www.awal-labs.com
Kyle F. Gross
Laboratory Directoi
Jose Rocha
PA Officer
Qual
A A .1c I f.P
Lab Sample ID: 1803136-0041
Client Sample ID: MW-6
Analyzed: 3 9 2018 I556h Extracted: 3 8
Units: µg/L Dilution Factor:
2018 1233h
1 Method: SW8270D
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
Dinoseb 88-85-7 9.75 < 9.'75
Diphenylamine 122-39-4 9.75 < 9.75
Disulfoton 298-04-4 9.75 < 9.75
Ethyl rnethanesulfonate 62-50-0 9.75 < 9.75
Farnphur 52-85-7 9.75 < 9.75
Fluoranthene 206-44-0 9.75 < 9.75
Fluorene 86-73-7 9 75 < 9.75
FleafreMefebenzene 9.75 ----*-9775
Hexachlorobutadiene 87-68-3 9.75 < 9.75
Hexachlorocyclopentadiene 77-47-4 9.75 < 9.75
Hexachloroetharie 67-72-1 9.75 < 9.75
Hexachloropropene 1888-71-7 9 75 < 9.75
Indeno(1,2,3-ccl)pyrene 193-39-5 9.75 < 9.75
lsodrin 465-73-6 9 75 < 9.75
lsophorone 78-59-1 9.75 < 9.75
lsosafrole 120-58-1 9.75 < 9.75
Kepone 143-50-0 9.75 < 9.75
Methapyrilene 91-80-5 9 75 < 9.75
Methyl methanesulfonate 66-27-3 9 75 < 9.75
Methyl parathion 298-00-0 9.75 < 9.75
Nitrobenzene 98-95-3 9.75 < 9.75
N-Nitrosodiethylamine 55-18-5 9.75 < 9.75
N-Nitrosodimethylamine 62-75-9 9.75 < 9.75
N-Nitrosodi-n-butylamine 924-16-3 9.75 < 9.75
N-Nitrosodi-n-propylamine 621-64-7 9.75 < 9.75
N-Nitrosodiphenylarnine 86-30-6 9.75 < 9.75
N-Nitrosomethylethylamine 10595-95-6 9.75 < 9.75
N-Nitrosopiperidine 100-75-4 9.75 < 9.75
N-Nitrosopyrrolidine 930-55-2 9.75 < 9.75
0,0,0-Triethyl phosphorothioate 126-68-1 9.75 < 9.75
o-Toluidine 95-53-4 9.75 < 9.75
Parathion 56-38-2 9.75 < 9.75
Pentachlorobenzene 608-93-5 9.75 < 9.75
Pentachloronitrobenzene 82-68-8 9.75 < 9.75
Pentaohlecopheaol- D N - 87 S6 5 475 ---• 4:45
Phenacetin 62-44-2 9.75 < 9.75
3440 South 700 West
Salt 1.ake City, UT 841 19
Phone: [phone]
Toll Free- [phone]
FaX' [phone]
e-mail. awal A aual-labs.com
web. www.awal-lab.com
Kyle F. Gross
Laboratory D:rector
Jose Rocha
QA Officer
3/211-ia
Repc-, Date 32; Fav 2 t'. ?•1
Jf`f .f • any T.., • • ce.. re,a: rt) • ...lea • ist>>. q • • • •.>: • is ri• • n s . ••••• on • •• • • r> se • ' .e> • • >vs .'ssi...•• • .`..eee.e >>> •• ',">, } • • ;•• r t‘ • "es, •
0: • e.--,s'•• •• 9 * > e" : '10 • • ee•••• • ; •••:: • ^4.•••5; 0 it •• • ; • •. >•>cete `NS st f . s ; • .•••,'*:; •
Lab Sample ID: 1803136-0041
Client Sample ID: MW-6
Analyzed: 3,9 2018 1556h
Units: ug/L
Extracted: 38/2018 1233h
Dilution Factor: 1 Method: SW8270D
Compound
CAS Reporting
Number Limit
Analytical
Result Quad
Phenanthrene 85-01-8 9.75 < 9.75
Phenol 108-95-2 9.75 < 9.75
Phorate 298-02-2 9.75 < 9.75
Pronarnide 23950-58-5 9.75 < 9.75
Pyrene 129-00-0 9.75 < 9.75
Safrole 94-59-7 9.75 < 9.75
Thionazin 297-97-2 9.75 < 9.75
Surrogate Units: pg/L CAS Result Amount Spiked % REC 1.,imits Qual
Sum: 2,4,6-Tribromaphenol 118-79-6 45.2 48.74 92.6 10-3ID
Sum: 2-Fluoroblphenyl 321-60-8 29.8 24.37 122 10-230
Sum 2-Fluorophetiol 367-12-4 27.7 48 74 56.8 10-120
Surr Nitrobenzene-d5 4165-60-0 33.2 24.37 136 10-253
Sum Phenol-d6 1327-88-3 22 3 48.74 45.7 10-110
Surr: Terphenyl-d14 1718-51-0 30.9 24 37 127 10-255
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax- [phone]
e-mail: awal ay.al-laIss.corn
web: www.awal-labx.com
Kyle F. Gross
Laboratoly Director
Jose Rocha
QA Officer
Peport Date 321 2018 Page 29 of 84
4 "R >rxfs
A,Tteric2.. et
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Client Sample ID:
Collection Date:
Received Date:
Analytical Results
AECOM
Payson City Landfill 60544100.4
1803136-0051
MW-4
3/7'2018 1230h
3 7 2018 1446h
Contact: Lawrence Cannon
Test Code: 8270-W-3511
SVOA X2 List by GC/MS Method 8270D/3511
Analyzed: 3/9 2018 1618h
Units: µg/L
Extracted: 3/8 2018 1233h
Dilution Factor: 1 Method: SW8270D
CAS
Number
Reporting Analytical
Limit Result Qua!
95-94-3
99-35-4
99-65-0
130-15-4
9.69
9.69
9.69
9.69
< 9.69
< 9.69
< 9.69
< 9.69
106-50-3 9.69 < 9 69
134-32-7 9.69 < 9 69
58-90-2 9.69 < 9.69
95-95-4 9.69 < 9.69
88-06-2 9.69 < 9.69
120-83-2 9.69 < 9.69
105-67-9 9.69 < 9.69
51-28-5 9.69 < 9.69
121-14-2 9.69 < 9.69
87-65-0 9.69 < 9.69
606-20-2 9.69 < 9.69
53-96-3 9.69 < 9.69
91-58-7 9.69 < 9.69
95-57-8 9.69 < 9.69
91-57-6 9.69 < 9.69
95-48-7 9.69 < 9.69
91-59-8 9.69 < 9.69
88-74-4 9.69 < 9.69
88-75-5 9.69 < 9.69
9.69 9.69
91-94-1 9.69 < 9.69
119-93-7 9.69 <- 9.69
56-49-5 9.69 9 69
99-09-2 9 69 < 9.69
534-52-1 9.69 < 9.69 (a'
Report Date 111,20 I s Page 30 of 84
1440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal,a aual-labs.com
web. www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
OA Officer
Compound
1,2,4,5-Tetrachlorobenzene
1,3,5-Trtrutrobenzene
1,3-Dinitrohenzene
1,4-Naphthoquinone
1,4-Phenylenediamine
I -Naphthylamine
2,3,4,6-Tetrachlorophenol
2,4,5-Trichlorophenol
2,4,6-Trichlorophenol
2,4-Dtchlorophenol
2,4-Dimethylphenol
2,4-Dinitrophenol
2,4-Dinitrotoluene
2,6-Dichlorophenol
2,6-Dtnitrotoluene
2-Acetylaminofluorene
2-Chloronaphthalene
2-Chlorophenol
2-Methylnaphthalene
2-Methylphenol
2-Naphthylamine
2-Nitroaniline
2-N itrophenol
3&4-Methylphenol
3,3"-Dichlorobenzidine
3,3 •-Dimethylbenzidine
3-Methylcholanthrene
3-Nitroaniline
4,6-Dinitro-2-methylphenol i.115 13b-a-
bt
• "4 • • .1s, 01 01 •01: • • •"•0 r . •.r nembe. ,'n$ f, • • tet,,,110, 00, tha erpoq t. <ova ON h ft(' .• • • • • • •v• • .• .fi•fiht•fimoi<n•m<ftwl•-•.• • '1. • oiter.ec 55 'IN' fir, ed•dd, ^ • • .,••,•ru.• • rm. •etiv xe,41> e-t•e•st ' he tlx e•er. :r...rAt. vr • • • • • . • . • ot • , < s.
',Ie.SZ
Lab Sample Ill: 1803136-0051
Client Sample ID: MW-4
Analyzed: 3!9/2018 1618h
Units: µg/L
Extracted: 3/8'2018 1233h
Dihition Factor: 1 Method: SW8270D
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qua!
4-Aminobiphenyl 92-67-1 9.69 < 9.69
4-Bromophenyl phenyl ether 101-55-3 9.69 < 9.69
4-Chloro-3-methylphenol 59-50-7 9.69 < 9.69
4-Chloroaniline 106-47-8 9.69 < 9.69
4-Chlorophenyl phenyl ether 7005-72-3 9.69 < 9.69
4-Nitroaniline 100-01-6 9.69 < 9.69
4-Nitrophenol 100-02-7 9.69 < 9.69
5-Nitro-o-toluidine 99-55-8 9.69 < 9.69
7,12-Dimethylbenz(a)anthracene 57-97-6 9.69 < 9.69
a,a-Dimethylphenethylamine 122-09-8 48.4 < 48.4
Acenaphthene 83-32-9 9.69 < 9.69
Acenaphthylene 208-96-8 9.69 < 9.69
Acetophenone 98-86-2 9.69 < 9.69
Anthracene 120-12-7 9.69 < 9.69
Benz(a)anthracene 56-55-3 9 69 < 9.69
IleapaFa4pycerws- C) N.1 4.0 324 949 k 9.69
Benzo(b)fluoranthene 205-99-2 9.69 < 9.69
Benzo(g,h,i)perylene 191-24-2 9.69 < 9.69
Benzo(k)fluoranthene 207-08-9 9.69 < 9 69
Benzyl alcohol 100-51-6 9.69 < 9.69
Bis(2-chloroethoxy)methane 111-91-1 9.69 < 9.69
Bis(2-chloroethyl) ether 111-44-4 9.69 < 9.69
Bis(2-chloroisopropyl) ether 108-60-1 9.69 < 9.69
B464141411,444074Y44-0"3144- b W. 117 81 7 9.69 .69
Butyl benzyl phthalate 85-68-7 9.69 < 9.69
Chlorobenzilate 510-15-6 9.69 < 9.69
Chrysene 218-01-9 9.69 <9.69
Diallate (cis or trans) 2303-16-4 9.69 < 9.69
Dibenz(a,h)anthracene 53-70-3 9.69 < 9.69
Dihenzofuran 132-64-9 9.69 < 9.69
Diethyl phthalate 84-66-2 9 69 < 9.69
Dimethoate 60-51-5 9.69 <9 69
Dimethyl phthalate 131-11-3 9.69 < 9.69
Dirnethylaminoazobenzene 60-11-7 9.69 < 9 69
Di-n-butyl phthalate 84-74-2 9.69 < 9 69
Di-n-octyl phthalate 117-84-0 9.69 < 9.69
3440 South 700 Wes:
Salt Lake City, UT 84119
Phone: (SOI) 263-8686
Toll Free- [phone]
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awal al-labs.coni
web: www.awal-labs.com
Kyle F. Gross
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Jose Rocha
QA Officer
bri, 3 I 2<f- It Rep irt Date. 3/2 11201 P.T.! : 4
A ar: '‘'•A tr: prf,m ed .v.r.• ***mut. *••• I • ..; • • • . • .••1 * or** rum lacy or *.t) . • • .• • v• z•I•tret,r +.• ran** •••••) * • •••*.••••• • • :.
• ' • -1 • Y' • .31hX. t. NJ," " • • .` • ": ..S t •••.-%• •4C 01 r-t • • • •.• • " ••• • ..•• » etWINVI gl .1/4 1-2 laNr • .•.• ih* ••• pore • • • • • • • ••• • :Ind t re" OP. *A* u• vitt
Reim.% Date 3!....` '2U• Pace 32 of 84
• -• • st tt. •t 44. e 'Ott I V. t
6f- 3 12k At
• r • r, • kt.. 1.0. 3110. t". t. • Ç. r
acs - I c ..4:1
.^,lose ti,• t ' rt , t . • :t1
Lab Sample ID: 1803136-0051
Client Sample ID: MW-4
Analyzed: 3'9 2018 1618h Extracted: 3(8
Units: gg/L Dilution Factor:
2018 I233h
l Method: SW8270E)
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qua!
Dinoseb 88-85-7 9.69 < 9.69
Diphenylamine 122-39-4 9.69 < 9.69
Disulfoton 298-04-4 9.69 < 9.69
Ethyl methanesulfonate 62-50-0 9.69 < 9.69
Famphur 52-85-7 9.69 < 9.69
Fluoranthene 206-44-0 9.69 < 9.69
Fluorene 86-73-7 9.69 < 9.69
licxachlorobenaene D 118-74-1 9.69 -4.-9769
Hexachlorobutadiene 87-68-3 9.69 < 9.69
Ilexachlorocyclopentadiene '77-47-4 9.69 < 9.69
Hexachloroethane 67-72-1 9.69 < 9.69
Hexachloropropene 1888-71-7 9.69 < 9.69
Indeno(1,2,3-cd)pyrene 193-39-5 9.69 < 9.69
lsodrin 465-73-6 9.69 < 9.69
Isophorone '78-59-1 9.69 < 9.69
lsosafrole 120-58-1 9.69 < 9.69
Kepone 143-50-0 9.69 < 9.69
Methapyrilene 91-80-5 9.69 < 9.69
Methyl methanesulfonate 66-27-3 9.69 < 9.69
Methyl parathion 298-00-0 9.69 < 9.69
Nitrobenzene 98-95-3 9.69 < 9.69
N-Nitrosodiethylamine 55-18-5 9.69 < 9.69
N-Nitrosodimethylamine 62-75-9 9.69 < 9.69
N-Nitrosodi-n-butylamine 924-16-3 9.69 < 9.69
N-Nitrosodi-n-propylamine 621-64-7 9 69 < 9.69
N-Nitrosodiphenylamine 86-30-6 9.69 < 9.69
N-Nitrosomethylethylamine 10595-95-6 9.69 < 9.69
N-Nitrosopiperidine 100-75-4 9.69 < 9.69
N-Nitrosopyrrolidine 930-55-2 9.69 < 9.69
0,0,0-Triethyl phosphorothioate 126-68-1 9.69 < 9.69
o-Toluidine 95-53-4 9 69 < 9.69
Parathion 56-38-2 9.69 < 9.69
Pentachlorobenzene 608-93-5 9.69 < 9.69
Pentachloronitrobenzene 82-68-8 9.69 < 9.69
Ftenisehieropiteftei-D - 47464-
Phenacet in 62-44-2 9.69 9 69
yv.trit.'1n
3440 South 700 West
Salt Lake City, UT 84:19
Phone: [phone]
Toll Free: [phone]
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Kyle F. Gross
Laboratory Director
Jose R.ocha
OA Officer
3440 South 700 West
Salt Lake City, UT 84119
Lab Sample ID: 1803136-0051
Client Sample ID: MW-4
Analyzed: 3r912018 1618h Extracted: 3
Units: ug/L Dilution Factor:
8/2018 1233h
1 Method: SW82701J
CAS Reporting Analytical
Compound Number Limit Result
Phenanthrene 85-01-8 9.69 < 9.69
Phenol 108-95-2 9.69 < 9.69
Phorate 298-02-2 9.69 < 9.69
Pronamide 23950-58-5 9.69 < 9.69
Pyrene 129-00-0 9.69 < 9.69
Safrole 94-59-7 9.69 < 9.69
Thionazin 297-97-2 9,69 < 9.69
Surrogate Units: ug/L CAS Result Amount Spiked % REC Limits Qual
Sum 2,4.6-Tribromophenol 118-79-6 39 6 48 43 81 8 10-310
Surr 2-Fluoroblphenyl 321-60-8 23.7 24.21 98.0 10-230
Sum 2-Fluoropheno1 367-12-4 28 2 48 43 58 3 10-120
Surr Nitrobenzene-d5 4165-60-0 25.9 2411 107 10-253
Surr: Plienol-d6 13127-88-3 20.5 48.43 42 3 10-110
Sum Terphenyl-d14 1718-51-0 25 9 24 21 107 10-255
ree - High RPD due to suspected sample non-homogeneity or matrix interference.
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Kyle F Gross
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Jo%e Rocha
QA Officer
3 21t2018 Page 33 (.4'84 •“, t:
Analyzed: 3 82018 900h
Units: µWt. Method: SW8260C
1440 South 700 West
II Salt Lake City, UT 84119 Compound
Dilution Factor: 1
Reporting Analytical
Limit Result Qual
CAS
Number
Ar.ri NIL'S I, At. :Y
Client:
Project:
Lab Sample ID:
Client Sample ID:
Collection Date:
Received Date:
AECOM
Payson City Landfill 60544100.4
1803136-001A
TB-030718
3.7'2018
372018 1446h
ORGANIC ANALYTICAL REPORT
Contact: Lawrence Cannon
Test Code: 8260-W
Analytical Results VOAs Appendix II List by GC/MS Method 8260C/5030C
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QA Officer
1,1,1,2-Tetrachloroetharte
1,1,1-Trichloroethane
1,1,2,2-Tetrachloroethane
1,1,2-Trichloroethane
1,1-Dichloroethane
1,1-Dichloroethene
1,1-Dichloropropene
1,2,3-Trichloropropane
1,2,4-Trichlorobenzene
1,2-Dibromo-3-chloropropanc
1.2-Dibromoethane
1,2-Dichlorobenzene
1,2-Dichloroethane
1,2-Dichloropropane
1,3-Dichlorobenzene
1,3-Dichloropropane
1,4-Dichlorobenzene
2,2-Dichloropropane
2-Butanone
2-Hexanone
4-Methy1-2-pentanone
Acetone
Acetonitrile
Acrolein
Acrylonitrile IÁ T.* Pr-
Allyl chloride
Benzene
Bromochloromethane
Bromodichloromethane
630-20-6
71-55-6
'79-34-5
79-00-5
75-34-3
75-35-4
563-58-6
96-18-4
120-82-1
96-12-8
106-93-4
95-50-1
107-06-2
78-87-5
541-73-1
142-28-9
106-46-7
594-20-7
78-93-3
591-78-6
108-10-1
67-64-1
75-05-8
107-02-8
107-13-1
107-05-1
71-43-2
74-97-5
75-27-4
2.00 < 2.00
2.00 < 2.00
2 00 < 2.00
2.00 < 2.00
2.00 < 2.00
2.00 < 2.00
2.00 < 2.00
2.00 < 2.00
2 00 < 2.00
5.00 < 5.00
2.00 < 2.00
2.01.) < 2.00
2.00 < 2.00
2.00 < 2.00
2.00 < 2.00
2.00 < 2.00
2.00 < 2.00
2.00 < 2.00
10.0 < 10.0
5.00 < 5.00
5.00 < 5.00
10.0 < 10.0
5.00 < 5.00
5.00 < 5.00
10.0 ‹. 10.0
5.00 ‹. 5.00
2 00 < 2.00
2.00 < 2.00
2.00 < 2.00
3)2 a- I Rep rt Date 3 2," I • Page 34 of 97
• ;., I rz; • •a• •
A tr.( :7, 1 I, st ATJA T •
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toli Free: [phone]
Fax: [phone]
awai a au al-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Lab Sample ID: 1803136-001A
Client Sample ID: TB-030718
Analyzed: 3/8 2018 900h
Units: µg/L Dilution Factor: 1 Method: SW8260C
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
Bromoform 75-25-2 2.00 < 2.00
Bromomethane 74-83-9 5.00 < 5.00
Carbon disulfide 75-15-0 2.00 < 2.00
Carbon tetrachloride 56-23-5 2.00 < 2.00
Chlorobenzene 108-90-7 2.00 < 2.00
Chloroethane 75-00-3 2.00 < 2.00
Chloroform 67-66-3 2.00 < 2.00
Chloromethane 74-87-3 3.00 < 3.00
Chloroprene 126-99-8 2.00 < 2.00
c is-1,2-D ic hloroethene 156-59-2 2.00 < 2.00
cis-1.3-Dichloropropene 10061-01-5 2.00 < 2.00
Dibromochloromethane 124-48-1 2.00 < 2.00
Dibromomethane 74-95-3 2.00 < '7.00
Dichlorodifluoromethane 75-71-8 2.00 < 2.00
Ethyl methacrylate 97-63-2 2.00 < 2.00
Ethylbenzene 100-41-4 2.00 < 2.00
lodomethane 74-88-4 5.00 < 5.00
lsobutyl alcohol 78-83-1 100 < 100
Methacrylonitrile 126-98-7 5.00 < 5.00
Methyl methacrylate 80-62-6 5.00 < 5.00
Methylene chloride 75-09-2 2.00 < 2.00
Naphthalene 91-20-3 2.00 < 2.00
Propionitri le 107-12-0 25.0 < 25.0
Styrene 100-42-5 2.00 < 2.00
Tetrachloroethene 127-18-4 2.00 < 2.00
Toluene 108-88-3 2.00 < 2.00
trans-1,2-Dichloroethene 156-60-5 2.00 < 2.00
trans-1,3-Dichloropropene 10061-02-6 2.00 < 2.00
trans-1,4-Dich I oro-2-butene 110-57-6 2.00 < 2.00
Trichloroethene 79-01-6 2.00 < 2.00
Trichlorofluoromethane 75-69-4 2.00 --• 2 00
Vinyl acetate 108-05-4 10.0 < 10 0
Vinyl chloride 75-01-4 1.00 < 1 00
Xylem. Total 1330-20-7 2.00 < 2 00
A sea., ,•• I r " 41, to t . ;‘,/
PA 3129 be Rep„rt Date 2 20 P4 ,tf" •c.. • ••• •vp ,tr .44 4,,e. • . • •••• t ' • ,t • , t. • • t, • •ts *4 4 'X .3,4, e • c• •;•• ••e -r•" • • •4v r war. ,r `vv. ••x• , tr7 tr, • MA", )31‘ • 4 /al : • p••• •1. • ••,‘ ,i'•••••e JO • hr AV • t 4. • 1.;%1 t • .: 1...") ). • VA. • ' • . • Art • • III e ft• St C J. f t • •
Lab Sample ID: 1803136-001A
Client Sample ID: TB-030718
Analyzed: 1832018 900h
Units: p.g/L Dilution Factor: 1 Method: SW8260C
Surrogate Units: µIA CAS Result Amount Spiked % REC Limits Qual _ ...... _ _ . C' itl Surr. 1,2-Dichloroethane-d4 17060-07-0 50.6 50.00 101 72-151
Surr: 4-Brornofluorobenzene 460-00-4 51.7 50.00 103 80-152
Surr: Dibrclainfluoromethane 1868-53-7 57.1 50.00 114 72-135
Surr: Toluene-d8 2037-26-5 50.8 50.00 102 80-124
3440 Soath 700 West
Salt Lake etty, UT 84119
Phone. [phone]
Toll Free: (88S) 263-8(86
Fax: [phone]
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weir www.awai-lab,..com
Kyle F. Gross
1.akratory Director
Jose R.ocha
QA Officer
6 3 eS'• Report Date: 3'2" 2018 Page 36 of 8 ,
net. :at 3, t rt flr tr. V.)t " tt ' ^t • ,
^Ot p.., tr %SS t ' ott t,etr'' 13,- ck -
.4 It It' .r.t
Test Code: 8260-W
VOAs Appendix II List by GC/MS Method 8260C/5030C Analytical Results
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill ' 60544100.4
Lab Sample ID: 1803136-002A
Client Sample ID: MW-X
Collection Date: 3 7 2018 800h
Received Date: 3 712018 1446h
Dilution Factor: I Method: SW8260C
Analyzed: 3.8 2018 920h
Units: itg/L
ORGANIC ANALYTICAL REPORT
1.1,1,2-Tetrachloroethane 630-20-6 2.00 < 2.00
1,1,1-Trichloroethane 71-55-6 2.00 < 2.00
1,1,2,2-Tetrachloroethane 79-34-5 2.00 < 2.00
1,1,2-Trichloroethane 79-00-5 2.00 < 2.00
1,1-Dichloroethane 75-34-3 2.00 < 2.00
1,1-Dichloroethene 75-35-4 2.00 < 2.00
1,1-Dichloropropene 563-58-6 2.00 < 2.00
1,2,3-Trichloropropane 96-18-4 2.00 < 2.00
1,2,4-Trichlorobenzene 120-82-1 2.00 < 2.00
172-14ibtemo-3-ebloreproponc 9128 --S-RO
1 g r2-Dibremeethooe- 106 93 4 2.00 < :MO
1.2-Dichlorobenzene 95-50-1 2.00 < 2.00
1,2-Dichloroethane 107-06-2 2 00 < 2.00
1,2-Dichloropropane 78-87-5 2 00 < 7.00
1,3-Dichlorobenzene 54 1-73- 1 2.00 < 2.00
1,3-Dichloropropane 142-28-9 2.00 < 2.00
1,4-Dichlorobenzene 106-46-7 2.00 < 2 00
2,2-Dichloropropane 594-20-7 2.00 < 2.00
2-Butanone 78-93-3 10.0 < 10.0
2-Hexanone 591-78-6 5.00 < 5.00
4-Methy1-2-pentanone 108-10-1 5.00 < 5.00
Acetone 67-64-1 10.0 < 10.0
Acetonitrile 75-05-8 5.00 < 5.00
Acrolein J` - 107-02-8 5.00 < 5.00
Acrylonitrile - 107-13-1 10.0 10 0
Ally! chloride 107-05-1 5.00 5.00
Benzene 71-43-2 2.00 < 2 00
Bromochloromethane 74-97-5 2.00 < 2 00
Bromodichloromethane 75-27-4 2 00 < 2 00
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e rnail: awal a aN. al-labs.com
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Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
3/ 21•11S'
Report Date 3.'2 71' S 7a 3 of
; K 1;
• • : e C . fol • !II ;;; n . . , ' • • .1 • `, ; 4 I .1. IV t• .1 '•
Result Qual
3440 South 700 West
Salt Lake City, UT 84119 Compound
CAS Reporting Analytical
Number Limit
#.; ir k n; s.
1,440 South 700 West
Salt Lake City. t T 84119
Lab Sample ID: 1803136-002A
Client Sample ID: MW-X
Analyzed: 3'82018 920h
Units: pg., L Dilution Factor: 1 Method: SW8260C
Compound
CAS
Number
Repor(ing
Limit
Analytical
Result Qual
Bromoform 75-25-2 2.00 < 2.00
Bromomethane 74-83-9 5.00 < 5.00
Carbon disulfide 75-15-0 2.00 < 2 00
Carbon tetrachloride 56-23-5 2.00 < 2.00
Chlorobenzene 108-90-7 2.00 < 2.00
Chloroethane 75-00-3 2.00 < 2.00
Chloroform 67-66-3 2.00 < 2.00
Chloromethane 74-87-3 3.00 < 3.00
Chloroprene 126-99-8 2.00 < 2.00
cis-1,2-Dichloroethene 156-59-2 2.00 5.24
cis-1,3-Dtchloropropene 10061-01-5 2.00 < 2 00
Dibromochlorornethane 124-48-1 2.00 < 2.00
Dibromomethane 74-95-3 2.00 < 2.00
Dichlorodifluoromethane 75-71-8 2.00 < 2.00
Ethyl methacrylate 97-63-2 2.00 < 2.00
Ethylbenzene 100-41-4 2.00 < 2.00
lodomethane 74-88-4 5.00 < 5.00
Isobutyl alcohol 78-83-1 100 < 100
Methacrylonitrile 126-98-7 5.00 < 5.00
Methyl methacrylate 80-62-6 5.00 < 5.00
Methylene chloride 75-09-2 2.00 2.71
Naphthalene 91-20-3 2.00 < 2.00
Propionitrile 107-12-0 25.0 < 25.0
Styrene 100-42-5 2.00 < 2.00
Tetrachloroethene 127-18-4 2.00 < 2.00
Toluene 108-88-3 2.00 < 2.00
trans-1,2-Dichloroetherte 156-60-5 2.00 < 2.00
trans-1,3-Dichloropropene 10061-02-6 2.00 < 2.00
trans-1,4-Dichloro-2-butene 110-57-6 2.00 < 2.00
Trichloroethene 79-01-6 2.00 < 2.00
Trichlorofluoromethane 75-69-4 2.00 < 2.00
Vinyl acetate 108-05-4 10 0 < 10.0
Vinyl chloride 75-01-4 1.00 < 1 00
Xylenes, Total 1330-20-7 2 00 < 2 00
3)221),- Repat Da : .:3
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Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
A •%, •.• 'A. • A R 4A •4•4, ".4"• ' • • t,Z• • +1 .0.4 .` • .;1. • CI t• 21) >,1", •,r • • o rq. • A ; {ft- •,,• •on •tt• • •se • st • ••••,Z • al SO. r • 1 Ut • K • . • C ••• tt?..

.• . r 't. , •‘• •sc,.., .4 x • t • '(1•' :t • • ,u 1•••• •Nr; . • 4.rtc x44 . 4s. tscr . '.• • ," a .•xt •• • . • i:•.)• . 4:1•;*., to, 4t• • .•O. • erw
Lab Sample ID: 1803136-002A
Client Sample ID: MW-X
Analyzed: 3/8'2018 920h
Units: pg/1.- Dilution Factor: 1 Method: SW8260C
. ..... ..,...._ ..... _ _
Surrogate Units: pg/L CAS Result Amount Spiked % REC Limits Qual ... _ ..... .......
Surr: 1,2-Dichloroethane-d4 17060-07-0 50 4 50 00 101 72-151
Surr: 4-Bromolluorobenzene 460-00-4 51.2 50.00 103 80-152
Surr: Dibromolluoromethane 1868-53-7 61 7 50.00 123 72-135
Surr Toluene-d8 2037-26-5 50.0 50.00 100 80-124
3440 South 700 West
Salt Lake City, UT 8 119
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Kyle F. Gross
Laboratos y Director
Jose Rocha
QA Officer

)akjit Repon Date 321,2013 Page 36 of 84

' Ai- 1" r W $a'" r‘e
' el. A

1

504, • tt,

I 3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal'et a‘k al-labs.com
web• www.awal-labs coin
ORGANIC ANALYTICAL REPORT
Client: AECOM Contact: Lawrence Cannon
Project: Payson City Landfill i 60544100.4
Lab Sample ID: 1803136-003A
Client Sample ID: MW-5
Collection Date: 3/7 2018 1000h
Received Date: 3 7 2018 1446h Test Code: 8260-W
Analytical Results VOAs Appendix Il List by GC/MS Method 8260C/5030C
Analyzed: 3,8 2018 940h
Units: pg/L Dilution Factor: 1 Method: SW8260C
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
1,1,1,2-Tetrachloroethane 630-20-6 2.00 < 2.00
1,1,1-Trichloroethane 71-55-6 2.00 < 2.00
1,1,2,2-Tetrachloroethane 79-34-5 2 00 < 2.00
1,1,2-Trichloroethane 79-00-5 2.00 < 2.00
1,1-Dichloroethane 75-34-3 2.00 < 2.00
1,1-Dichloroethene 75-354 2.00 < 2.00
1,1-Dichloropropene 563-58-6 2.00 < 2.00
1,2,3-Trichloropropane 96-18-4 2 00 < 2.00
1,2,4-Trichlorobenzene 120-82-1 2.00 < 2.00
ON 5.00 1.72-Dibrefno.-3-ehleceprepane 12. 96 12
112-Dibremeethane- 1?- 106 9.4 4 2.00- 4 2.00
1,2-Dichlorobenzene 95-50-1 2.00 < 2.00
1,2-Dichloroethane 107-06-2 2.00 < 2.00
1,2-Dichloropropane 78-87-5 2.00 < 2.00
1,3-Dichlorobenzenc 541-73-1 2.00 < 2.00
1,3-Dichloropropane 142-28-9 2.00 < 2.00
1,4-Dichlorobenzene 106-46-7 2.00 < 2.00
2,2-Dichloropropane 594-20-7 2.00 < 2.00
2-Butanone 78-93-3 10.0 < 10.0
2-Hexanone 591-78-6 5.00 < 5.00
4-Methyl-2-pentanone 108-10-1 5.00 < 5.00
Acetone 67-64-1 10.0 < 10.0
Acetonitrile 75-05-8 5.00 < 5.00
Acrolein Ut .T r 107-02-8 5.00 < 5.00
Acrylonitrile 1./t 1"3- -- 107-13-1 10.0 ' 10.0
Allyl chloride 107-05-1 5.00 , 5,00
Benzene 71-43-2 2.00 2.00
Bromochloromethane 74-97-5 2.00 < 2.00
Bromodichloromethane 75-27-4 2.00 < 2.00
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
bri 3/241,
Report Date .2: 20 •i :14 • 37 )1
• ti ,• „nal •31 • JIC W? '41 k Pt • • ; t• ; .se •A oi.• •• • ••• •stv
- • tit. • t. urn • •
'•• . t' • .1, t". .•Al • TrZ • -it tat , %L. ' • •( CC' • :P. • • . • • It • :11, .1 • • C1.• p••• ;10. •55.t• yr/ 11 • ••I • 2,
• .1, • '..1C• •.11: es .nt .er . .11 'Mt ....• . s a .rti •$/••••It. •-•••• • . •
Dilution Factor: 1 Method: SW8260C
Result Qual
CAS Reporting Analytical
Number Limit
kie 3124-AP Report Date• 3,21 '2C 18 c, 4
• :e
• Y.) 0,03• 'Mee ea •" •se d • •• • v.% r • Vf • t• 0.44 • • I • ••• • • •Ar•:•), r4 c• • ; - z0 ••• -cc
Bromoform
Bromomethane
Carbon disulfide
Carbon tetrachloride
75-25-2
74-83-9
75-15-0
56-23-5
2 00
5.00
2.00
2.00
< 2.00
< 5.00
< 2.00
< 2.00
3440 South 700 West Chlorobenzene 108-90-7 2.00 < 2.00
Salt Lake City, UT 84119 Chloroethane 75-00-3 2.00 < 2.00
Chloroform 67-66-3 2.00 < 2.00
Chloromethane 74-87-3 3.00 < 3.00
Phone: [phone] Chloroprene 126-99-8 2.00 < 2.00
Toll Free [phone] cis-1,2-Dichloroethene 156-59-2 2.00 5.18
Fax: [phone] cis-1,3-Dichloropropene 10061-01-5 2.00 < 2.00
e-mail: awal tt am.al-labs.com Dibromochloromethane 124-48-1 2.00 < 2.00
Dibromomethane 74-95-3 2.00 < 2.00
web. www.awal-labi.com Dichlorodifluoromethane 75-71-8 2.00 < 2.00
Ethyl methacrylate 97-63-2 2.00 < 7.00
Ethylbenzene 100-41-4 2.00 < 1.00
Kyle F. Ciross lodomethane 74-88-4 5.00 < 5.00
Laboratory Drector lsobutyl alcohol 78-83-1 100 < 100
Methacrylonitrile 126-98-7 5.00 < 5.00 Jose Rocha Methyl methacrylate 80-62-6 5.00 < 5.00 QA Officer Methylene chloride 75-09-2 2.00 2.56
Naphthalene 91-20-3 2.00 < 2 00
Propionitrile 107-12-0 25.0 < 25.0
Styrene 100-42-5 2.00 < 2.00
Tetrachloroethene 127-18-4 2.00 < 2.00
Toluene 108-88-3 2.00 < 2.00
trans-1,2-Dichloroethene 156-60-5 2.00 < 2.00
trans-1,3-Dichloropropene 10061-02-6 2.00 < 2.00
trans-1,4-Dichloro-2-butene 110-57-6 2.00 < 2.00
Trichloroethene 79-01-6 2.00 < 2.00
Trichlorofluoromethane 75-69-4 2.00 < 2.00
Vinyl acetate 108-05-4 10.0 < 10.0
Vinyl chloride 75-01-4 1.00 --- 1.00
Xylenes, Total 1330-20-'7 2.00 ' 2.00
Lab Sample ID: 1803136-003A
Client Sample ID: MW-5
Analyzed: 3'8 2018 940h
Units: ug/L
Lab Sample ID: I 803136-003A
Client Sample ID: MW-5
Analyzed: 3,82018 940h
Units: pg/L Dilution Factor: 1 Method: SW8260C
Surrogate Units: ug/L CAS Result Amount Spiked % REC Limits Qual
Surr 1,2-Dichloroethane-d4 17060-07-0 50.1 50.00 100 72-151
Surr: 4-Brorrsolluorobenzene 460-00-4 50 7 50.00 101 83-152
Sum Dibromofluoromethane 1868-33-7 60.0 50.00 120 72-135
Sun: Toluene-d8 2037-26-5 49.7 50.00 99,4 80-124
3440 South 700 West
Salt Lake City. UT 84119
Phone. (8(>1) 263-8686
To11 Free. (888) 263-868(
Fax' [phone]
c-mail: awal o al-I abs.com
web: www awal-labs.com
Kyle F. Gross
Laboratory Directoi
Jose Rocha
QA Officer
Repcn Date: 3 21,2018 Page 39 of 84

g- ,r3t „ 5r • '

, 41. r33t 333 .5cct tlt ttt 5;

.I. tat, „ ,
0,7
t,t < "t ‘1. 'A< • .51
Analyzed: 3'8 2018 1000h
Units: pg/L Method: SW8260C Dilution Factor: 1
Result Qual
Reporting Analytical
Limit
• ,n41:: C4 ••• het. A. , , •••1.1 • Cy , f.
Report Date 3 _1,1.18 Page 40 of 84 e :v. .0 .4.0

cs• nt., • •.• sNi ,w< • ne4.. C .h, uf • • •
ex. 3/24 /11'
• q s 1 ••to . .. • .4 , • • .0 •c •

.1•To • ht. • •: • •• a ot.s. WI. • • •r. : •• • • • A., s •C tst) • Wu • ). .4. • .3., P ev s • • VC. .4 no . le • .rer r4 r yr :On: • pr..a: • 4. At. . and
Air 3t
Client:
Project:
Lab Sample ID:
Client Sarnple ID:
Collection Date:
Received Date:
Analytical Results
3440 South 700 West
1,1,1,2-Tetrachloroethane 630-20-6 2.00 < 2.00
1,1,1-Trichloroethane 71-55-6 2.00 < 2.00
I , I ,2,2-Tetrachloroethane 79-34-5 2.00 < 2.00
1,1,2-Trichloroethane 79-00-5 2.00 < 2.00
1,1-Dichloroethane 75-34-3 2 00 < 2.00
1,1-Dichloroethene 75-35-4 2.00 < 2 00
1,1-Dichloropropene 563-58-6 2.00 < 2.00
1,2,3-Trichloropropane 96-18-4 2.00 < 2.00
1,2,4-Trichlorobenzene 120-82-1 2.00 < 7.00
14-14449mo-3-chlopappapane 0)41Z 96 12 8 -5.430-- ------,xee
172-i4brornoothaao-t>tE 106 97 4 _
1,2-Dichlorobenzene 95-50-1 2.00 < 2 00
1,2-Dichloroethane 107-06-2 2.00 < 2.00
1,2-Dichloropropane 78-87-5 2.00 < 7.00
1,3-Dichlorobenzene 541-73-1 2.00 < 2.00
1.3-Dichloropropane 142-28-9 2 00 < 2.00
1,4-Dichlorobenzene 106-46-7 2.00 < 2 00
2,2-Dichloropropane 594-20-7 2.00 < 2.00
2-Butanone 78-93-3 10.0 < 10.0
2-Hexanone 591-78-6 5.00 < 5.00
4-Methy1-2-pentanone 108-10-1 5 00 < 5.00
Acetone 67-64-1 10.0 < 10.0
Acetonitrile 75-05-8 5.00 < 5.00
Acrolein S 107-02-8 5.00 < 5.00
Acrylonitrile t1iT P,T- 107-13-1 10.0 < 10.0
Anyl chloride 107-05-1 5 00 < 5.00
Benzene 71-43-2 2 00 < 2.00
Bromochloromethane 74-97-5 2 00 < 2.00
Bromodichloromethane 75-27-4 2 00 < 2.00
Phone. [phone]
Totl Free: [phone]
Fax. [phone]
e-mail awal et w% al-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Salt Lake City, UT 84119 Compound
CAS
Number
AECOM
Payson City Landfill / 60544100 4
1803136-004A
MW-6
3'7/2018 1115h
3 7 2018 I446h Test Code: 8260-W
VOAs Appendix 11 List by GC/MS Method 8260C/5030C
Contact: Lawrence Cannon
A.i St
3440 South 700 West
Salt Lake City. UT 84)19
Pnone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal ti al-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Lab Sample ID: I803136-004A
Client Sample ID: MW-6
Analyzed: 3,8'2018 1000h
Units: pg`L Dilution Factor: 1 Method: SW8260C
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
Brornoforrn 75-25-2 2 00 < 2.00
Bromomethane 74-83-9 5.00 < 5.00
Carbon disulfide 75-15-0 2.00 < 2.00
Carbon tetrachloride 56-23-5 2.00 < 2.00
Chlorobenzene 108-90-7 2.00 < 2.00
Chloroethane 75-00-3 2.00 < 2.00
Chloroform 67-66-3 2.00 < 2 00
Chloromethane 74-87-3 3.00 < 3.00
Chloroprene 126-99-8 2.00 < 2.00
cis-1,2-Dichloroethene 156-59-2 2.00 < 2.00
cis-1,3 -Dichloropropene 10061-0: -5 2.00 < 2.00
Dibromochloromethane 124-48-1 2.00 < 2.00
Dibromomethane 74-95-3 2.00 < 2.00
Dichlorodifluoromethane 75-71-8 2.00 < 2.00
Ethyl rnethacrylate 97-63-2 2.00 < 2.00
Ethylbenzene 100-41-4 2.00 < 2.00
lodomethane 74-88-4 5.00 < 5.00
lsobutyl alcohol 78-83-1 100 < 100
Methacrylonitrile 126-98-7 5.00 < 5.00
Methyl methacrylate 80-62-6 5.00 < 5.00
Methylene chloride 75-09-2 2.00 < 2.00
Naphthalene 91-20-3 2.00 < 2.00
Propionitrile 107-12-0 25.0 < 25.0
Styrene 100-42-5 2.00 < 2 00
Tetrachloroethene 127-18-4 2.00 < 2.00
Toluene 108-88-3 2.00 < /.00
trans-1,2-Dichloroethene 156-60-5 2.00 < 2.00
trans-1,3-Dichloropropene 10061-02-6 2.00 < 2.00
trans-1,4-Dichloro-2-butene 110-57-6 2.00 < 2.00
Trichloroethene 79-01-6 2.00 < 2.00
Trichlorofluoromethane 75-69-4 2.00 < 2 00
Vinyl acetate 108-05-4 10.0 < 10.0
Vinyl chloride 75-01-4 1 00 < 1 00
Xylenes, Total 1330-20-7 2 00 , 2 00
P09._ 3i2s,/u)
Revrt Date 3/21 ?0: - ;e4
• .3•_ tett _ tlt, • t `t;)`. ;titter,. t,,ett -t • e %Ito • tt' . Ls% tt It
Lab Sample ID: 1803136-004A
Client Sample ID: MW-6
Analyzed; 3'8.'2018 1000h
Units: ug/L Dilution Factor: 1 Method: SW8260C
y
Surrogate Units: pg/1. CAS Result Amount Spiked ..... ....._ % REC _ .. ... Limits Quid _ ..._ ... .....
Surr. 1,2-Dichloroeihane-d4 17060-07-0 50 7 50 00 101 72-151
Surr 4-Bronm1luoro1enzene 460-00-4 51 0 50.00 101 80-152
Surr: Dibromofluoromethane 1868-53-7 60.1 50.00 120 72-135
Suir Toluene-d8 2037-26-5 50 1 50.00 100 80-124
3440 South 700 West
Salt Lake City, UT 84119
Phone. [phone]S6
Toll Free. [phone]
Fax [phone]
e-mail: awal awal-labs.corn
web: www.awal-labs.com
Kyle F. Grol.g
Laboratory Director
Jose Rocha
OA Officer
P Repoo Date 3.2: '2018 Page 42 of 84
AC' di<
, ' ' t.,4`UtÇ
VOAs Appendix II List by GC/MS Method 8260C/5030C Analytical Results
Report Date • ): 8 Page 43 of a4
it me ice'
At ,TiC LAC
Client:
Project:
Lab Sample ID:
Client Sample ID:
Collection Date:
Received Date:
AECOM
Payson City Landfill / 60544100.4
1803136-005A
MW-4
3 7 2018 1230h
3 7 2018 1446h Test Code: 8260-W
ORGANIC ANALYTICAL REPORT
Contact: Lawrence Cannon
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
oll Free: [phone]
Fax: [phone]
e-mail. awal aual-labs.com
web ww w.a wa
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Analyzed: 3 8 2018 1020h
Units: µg/L Dilution Factor: I Method: SW8260C
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
1,1,1,2-Tetrachloroethane 630-20-6 2.00 < 2.00
1,1,1-Trichloroethane 71-55-6 2.00 < 2.00
1,1,2,2-Tetrachloroethane 79-34-5 2.00 < 2.00
1,1,2-Trichloroethane 79-00-5 2.00 < 2.00
1,1 -Dich1oroethane 75-34-3 2.00 < 2.00
1,1-Dichloroethene 75-35-4 2.00 < 2.00
1,1-Di chloropropene 563-58-6 2.00 < 2.00
1,2,3-Trichloropropane 96-18-4 2.00 < 2.00
1,2,4-Trichlorobenzene 120-82-1 2.00 < 2.00
1-,49161,erettr-3-ellierepfepane ts.1 96 8 12 5-.00 4 5:00
1.2-Diluomoolhano-t) t‘j R_ 106 93-4 2.00 < 7.00
1,2-Dichlorobenzene 95-50-1 2 00 < 2.00
1,2-Dichloroethane 107-06-2 2.00 < 2.00
1,2-Dichloropropane 78-87-5 2.00 < 2.00
1,3-Dichlorobenzene 541-73-1 2.00 < 2.00
1,3-Dichloropropane 142-28-9 2.00 < 2.00
1,4-Dichlorobenzene 106-46-7 2 00 < 2.00
2,2-Dichloropropane 594-20-7 2.00 < 2.00
2-Butanone 78-93-3 10.0 < 10.0
2-Hexanone 591-78-6 5.00 < 5.00
4-Methy1-2-pentanone 108-10-1 5.00 < 5.00
Acetone 67-64-1 10.0 < 10.0
Acetonitrile 75-05-8 5 00 < 5.00
Acrolein (AT PT - 107-02-8 5 00 5.00
Acrylonitrile j"Pr - 107-13-1 10.0 < 10 0
Allyl chloride 107-05-1 5.00 < 5 00
Benzene 71-43-2 2.00 -- 2 00
Bromochloromethane 74-97-5 2 00 •,' 2 00
Bromodichloromethane 75-27-4 2 00 < 2.00
. in k ies? ANA T ..
3440 South 700 West
Salt Lake City. UT 84119
Phone. [phone]
Toll Free [phone]
Fax: [phone]
e-mail awal awal-labs.com
web: www.awal-labs com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Lab Sample ID: 1803136-005A
Client Sample ID: M W-4
Analyzed: 3.8'2018 1020h
Units: 1.1g/L Dilution Factor: I Method: SW8260C
Compound
CAS
Number
Reporting
Limit
Analytical
Result Qual
Bromoform 75-25-2 2.00 < 7.00
Bromomethane 74-83-9 5.00 < 5.00
Carbon disulfide 75-15-0 2.00 < 2.00
Carbon tetrachloride 56-23-5 2.00 < 2.00
Chlorobenzene 108-90-7 2.00 < 2.00
Chloroethane 75-00-3 2.00 < 2.00
Chloroform 67-66-3 2.00 < 2.00
Chloromethane 74-87-3 3.00 < 3.00
Chloroprene 126-99-8 2.00 < 2.00
cis-1,2-Dichloroethene 156-59-2 2.00 < 2.00
cis-1,3-Dichloropropene 10061-01-5 2 00 < 2.00
Dibromochloromethane 124-48-1 2 00 < 2.00
Dibromomethane 74-95-3 2.00 < 2.00
Dichlorodifluorornethane 75-71-8 2.00 < 2.00
Ethyl methacrylate 97-63-2 2.00 < 2.00
Ethylbenzene 100-41-4 2.00 < 2.00
lodomethane 74-88-4 5.00 < 5.00
lsobutyl alcohol 78-83-1 100 < 100
Methacrylonitriie 126-98-7 5.00 < 5.00
Methyl methacrylate 80-62-6 5.00 < 5.00
Methylene chloride 75-09-2 2.00 < 2.00
Naphthalene 91-20-3 2.00 < 2.00
Propionitrile 107-12-0 25.0 < 25.0
Styrene 100-42-5 2.00 < 2.00
Tetrachloroethene 127-18-4 2.00 < 2.00
Toluene 108-88-3 2.00 < 2.00
trans-1,2-Dichloroethene 156-60-5 2 00 < 2.00
trans-1,3-Dichloropropene 10061-02-6 2.00 < 2.00
trans-1,4-Dichloro-2-butene 110-57-6 2.00 < 2.00
Trichloroethene 79-01-6 2.00 < 2.00
Trichlorofluoromethane 75-69-4 2.00 < 2.00
Vinyl acetate 108-05-4 10.0 -', 10 0
Vinyl chloride 75-01-4 1.00 < 1.00
Xylenes, Total 1330-20-7 2 00 < 2 00
I ,a`sser. -rc Pr.
3124-0
•„.., • • pro • 1 a 34.:, • "`. . tt .1, r-q••••, • • - a VZitt, •• • • ..• . •,,P1••• ,e :It., • • .: •• • t , • , • • -r7 • • rr„-,:a.ry. • ••4 TWX.V

Rep-rt D. ic -• 21/2: •r84 ed CC A .•• , ". 0.1.1 ^ • •Orsrv. • ,..113, • .1. the ot. •zne• ••- tut,"<^ 10•'... • • +` •• • ; toss ,•• • •••t- •• gl• • .8. W. PIS lt t st`f . • *le .. 7 to • 1,1 ••• fe,,t< ••1
Lab Sample ID: 1803136-005A
Client Sarnple ID: MW4
Analyzed: 3,8,2018 1020h
Units: µg/L Dilution Factor: 1 Method: SW8260C
Surrogate Units: pg/L CAS Result Amount Spiked % REC Limits Qual ... ... . ............ ......... ......... ...... .......
Surr 1,2-Dtchloroethane-d4 17060-07-0 5I4 50.00 103 72-151
Surr 4-Bromo11uorobenzene 460-00-4 52 2 50 00 104 80-152
Surr: Dibromoiluoromethane 1868-53-7 57 9 50.00 116 72-135
Surr Toluene-d8 2037-26-5 51.1 50.00 102 80-124
3440 South 700 West
Salt Lake City, UT 84119
Phone. (80:)263-8686
Toll Free. [phone]
Fax [phone]
e-mail: awal m%al-labs.com
web: www.awal-labs.com
K.yle F. Gross
L.aboratory Director
Jose Rocha
OA Officer
Repon Date 3 21 2018 Page 45 of 84

z ^,X • ,
',F1 ,
111V• • 11,1: 1O13. •
' 1! •st vr•
AECOM
Payson City Landfill 60544100.4
Contact: Lawrence Cannon
Dilution Factor: I Method: SW8260C
Analyzed: 3 8'2018 1121h
Units: L
Client:
Project:
Lab Sample ID: 1803136-006A
Client Sample ID: FB-030718
Collection Date: 3 7 2018 1045h
Received Date: 3 7 2018 I 446h
Analytical Results
Test Code: 8260-W
VOAs Appendix II List by GC/MS Method 8260C/5030C
1,1,1,2-Tetrachloroethane 630-20-6 2.00 < 2.00
1,1,1-Trichloroethane 71-55-6 2.00 < 2.00
1,1,2,2-Tetrachloroethane 79-34-5 2.00 < 2.00
1,1,2-Trichloroethane 79-00-5 2.00 < 2.00
1 ,I-Dichloroethane 75-34-3 2.00 < 2.00
1,I-Dichloroethene 75-35-4 2.00 < 2.00
1,I-Dichloropropene 563-58-6 2.00 < 2.00
1,2,3-Trichloropropane 96-18-4 2.00 < 2.00
1,2,4-Trichlorobenzene 120-82-1 2.00 < 2.00
96444 5.00 5.00 1-72-Dibioome-3-ehlerepfepaae DNZ-
12 Dibromoethano j 106-93-4 -2-40- g_
1,2-Dichlorobenzene 95-50-1 2.00 < 2.00
1,2-Dichloroethane 107-06-2 2.00 < 2.00
1,2-Dichloropropane 78-87-5 2.00 < 2.00
1,3-Dichlorobenzene 541-73-1 2.00 < 2.00
1,3-Dichloropropane 142-28-9 2.00 < 2.00
1,4-Dichlorobenzerie 106-46-7 2.00 < 2.00
2,2-Dichloropropane 594-20-7 2.00 < 2.00
2-Butanone 78-93-3 10.0 < 10.0
2-Hexanone 591-78-6 5.00 < 5.00
4-Methy1-2-pentanone 108-10-1 5.00 < 5.00
Acetone 67-64-1 10.0 < 10.0
Acetonitrile 75-05-8 5.00 < 5.00
Acrolein 1,1 T Fr_ 107-02-8 5.00 < 5.00
Acrylonitrile 1,13- Pr- 107-13-1 10.0 < 10.0
Ally! chloride 107-05-1 5.00 < 5.00
Benzene 71-43-2 2.00 < 2.00
Bromochloromethane 74-97-5 2.00 < 2 00
Bromodichloromethane 75-27-4 2.00 < 2 00
(2klig
;..acs. $ tn :r k 5: N I: 'de • tiln• • .1, -` • N.: A X,' .• AM' A.g.. an ;rt.\
r pot •!...; • 1. 41c Ars • oad• ••• an. et • , • eptt ••cs • no r•-• c men • 1
ReVrt Dale Pag.: '
a I:. ••,,, • • t 'IR • 1.
';r1' e•O Vie -AC A fr '
ORGANIC ANALYTICAL REPORT
Phone [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal a awal-labs.corn
web. www.awal-labs com
Kyle F. Gross
1 aboratory Director
Jose Rocha
QA Officer
Result Qual
3440 South 700 West
Salt Lake City, UT 84119 Compound
CAS Reporting Analytical
Number Limit
Dilution Factor: 1
Limit Result Qual Compound
Lab Sample ID: 1803136-006A
Client Sample ID: FB-030718
Analyzed: 318'2018 112Ih
Units: pgt Method: SW8260C
CAS Reporting Analytical
Number A AA Ar P.
3440 South 700 West
Salt Lake City, UT 84119
Pnone: [phone]
Toll Free: (S$S) 263-8686
Fax: [phone]
e-rnail. awal al-tabs.com
web. www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Bromoform
Brornomethane
Carbon dtsulfide
Carbon tetrachloride
Chlorobenzene
Chloroethane
Chloroform
Chloromethane
Chloroprene
cis-1,2-Dichloroethene
cis-1,3-Dichloropropene
Dibromochloromethane
Dibromomethane
Dichlorodifluoromethane
Ethyl rnethacrylate
Ethylbenzene
lodomethane
lsobutyl alcohol
Methacrylonitrile
Methyl methacrylate
Methylene chloride
Naphthalene
Propionitrile
Styrene
Tetrachloroethene
Toluene
trans-1,2-Dichloroethene
trans-1,3-Dichloropropene
trans-1,4-Dichloro-2-butene
Trichloroethene
Trichlorofluoromethane
Vinyl acetate
Vinyl chloride
Xylenes, Total
75-25-2 2 00
74-83-9 5.00
75-15-0 2.00
56-23-5 2.00
108-90-7 2.00
75-00-3 2.00
67-66-3 2.00
74-87-3 3.00
126-99-8 2.00
156-59-2 2.00
10061-01-5 2.00
124-48-1 2.00
74-95-3 2.00
75-71-8 2.00
97-63-2 2 00
100-41-4 2.00
74-88-4 5.00
78-83-1 100
126-98-7 5.00
80-62-6 5.00
75-09-2 2.00
91-20-3 2.00
107-12-0 25.0
100-42-5 2.00
127-18-4 2.00
108-88-3 2.00
156-60-5 2.00
10061-02-6 2.00
110-57-6 2.00
79-01-6 2.00
75-69-4 2.00
108-05-4 10.0
75-01-4 1 00
1330-20-7 2 00
< 2.00
< 5.00
< 2.00
< 2.00
< 2.00
< 2.00
< 1.00
< 3.00
< 2.00
< 2.00
< 2 00
< 2.00
< 2.00
< 2.00
< 2.00
< 2.00
< 5.00
< 100
< 5.00
< 5.00
< 2 00
< 2.00
< 25.0
< 2.00
< 2.00
<100
< 2 00
< 2 00
< 2.00
< 2.00
< 100
< 10.0
< 1 00
< 2 00
60- 3 f u fit
Report Date 3' .`12." 4 Page 41 of 84
. <la; : sc• • OA 4 A. • • :tr , • 4,1 ••1 At" •, • . 4 A JO, • dte h. • "(-• 1
" A •• • 041 • *I • ,••••• • • , „ , ,:ta pot • •• • t:n 2‘' " ". • '41/4 wl) too . t. .,< a; east e •••• • , zact• • JCt Ne • ••••r• • tt •• .x.1 • , t •ost PI • • ' • y: A A •c•Pf ',‘ • • A• stA •• , Kt
Dilution Factor: 1 Method: SW8260C
Lab Sample ID: I803136-006A
Client Sample ID: FB-030718
Analyzed: 31.2018 1121h
Units: og/1.,
Surrogate Units: µWt.
Surr: 1.2-Dichloroethanc-d4
Surr 4-Bromafluarobenzene
Surr Dibronsofluoromelhane
Sum: Toluene-d8
CAS Result Amount Spiked
17060-07-0 51.4 50 00
460-00-4 50.8 %Co
I 868-53-7 58 2 50.00
2037-26-5 50.6 50.00
% REC Limits Qua
103 72-151
102 80-157.
116 72-135
101 80-124
3440 South 700 West
Salt Lake City, UT 84119
Phone. (80 i) 263-8686
Toll Free. [phone]
Fax, [phone]
e-mail: awal a au al-labs.corn
web: www awal-labs.eorn
Kyle F. Gross
1.aboratory Director
Jose R.00hta
QA Off.cer
t
Repot Date- 121 2018 Page 48 of 84 •oa .1, 4 1.• , ,vier , Yu' LOC 4%1.
MI MB in On 11.11 11111 lin OM AM an 3440 South 700 West *t*,
Salt Lake City. UT 84119
Phone: [phone], Toll Free: [phone], Fro,: [phone]
e-mail: [e-mail], web: www.awal-labs corn
Jose Rocha
QA Officer
)__C SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: ME
Project: Payson City Landfill / 60544100.4 QC Type: LCS
Analyte
Lab Sample ID:
Test Code
LCS-54532
6010D-W
Result
Date Analyzed
Date Prepared
Units
03/16/2018
03/09/2018
Method
1145h
1114h
MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC RPD Ref. RPD
Limits Amt % RPD Limit Qual
Calcium 9 80 mg/L SW6010D 0 0119 1 00 10 00 0 98 0 80 - 120
Iron 1 00 mg/L SW6010D 0 0180 0 100 1 000 0 100 80 - 120
Magnesium 9 98 mg/L SW6010D 0 0568 1 00 10 00 0 99 8 80 - 120
Potassium 10 2 mg/L sw6010D 0 106 1 00 10 00 0 102 80 - 120
Sodium 10 2 mg/L 5w6010D 0 0375 1 00 10 00 0 102 80 - 120
Tin 0 944 rng/L SW6010D 0 00543 0 500 1 000 0 94 4 80 - 120
Vanadium 0 187 mg/L SW60 IOD 0 00105 0 00500 0 2000 0 93 3 80 - 120
Lab Sample ID: LCS-54532 Date Analyzed 03/20/2018 1929h
Test Code 6020B-W Date Prepared 03/09/2018 1114h
Antimony 0 212 mg/L 5W6020B 0 000123 0 00200 0 2000 0 106 85 - 115
Arsenic 0 204 rng/L SW6020B 0 000576 0 00200 0 2000 0 102 85 - 115
Barium 0 201 mg/L 5W6020B 0 000173 0 00200 0 2000 0 101 85 - 115
Beryllium 0 198 rng/L SW6020B 0 0000516 0 00200 0 2000 0 99 0 85 - 115
Cadmium 0 201 mg/L SW6020B 0 000100 0 000500 0 2000 0 101 85 - 115
Chromium 0 203 mg/L SW6020B 0 000354 0 00200 0 2000 0 101 85 - 115
Cobalt 0 205 rng/L SW6020B 0 000151 0 00400 0 2000 0 102 85 - 115
Copper 0 203 mg/L SW6020B 0 00107 0 00200 0 2000 0 102 85 - 115
Lead 0 204 mg/L SW6020B 0 000444 0 00200 0 2000 0 102 85 - 115
Manganese 0 208 mg/L SW6020B 0 000270 0 00200 0 2000 0 104 85 - 115
Nickel 0 204 rng/L SW6020B 0 000177 0 00200 0 2000 0 102 85 - 115
Selenium 0 203 mg/L SW6020B 0 000278 0 00200 0 2000 0 101 85 - 115
Silver 0 186 rng/L SW6020B 0 0000404 0 00200 0 2000 0 92 8 85 - 115
Thallium 0 198 mg/L SW6020B 0 000174 0 00200 0 2000 0 99 0 85 - 115
Zinc l 01 rng/L SW6020B 0 00159 0 00500 1 000 0 101 85 - 115
Report Date 3/27/2018 Page 52 of 87
'MI analyses apphsable to the CVl A q)WA, and It.( 12A are per formed in sccordance to NI IA( protocols Pei limn samplina informal on is located on the attached ( (JC Confidenttal Iles ncas Infix inaPon Ilrri ittport ls povided for the exclusive use ol ths addressee Privileges of subsequtrit we of the
name ot this ,onipany or any member arts staff, or reproduction of this repo] t in oonnection with the advertisement, promotion or sale ot any oduet or ptocess., or in connection .s.th the re-publication of this report tor any purpose othei than for the addressee will be granted only on contact This
co nrx...iv accepts no responsibility eseent tor the dae per manec of irsacction and,or analvais in good faith and acc tin ..ulas the trade and ot reit IN-
Kyle F. Gross
Laboratory Director
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax [phone]
e-rnail: awalgawal-labs.eom, web: www.awal-lahs.eom
OC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: ME
Project: Payson City Landfill / 60544100.4 QC Type: LCS
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: LCS-54656 Date Analyzed 03/16/2018 846h
Test Code 11G-W-7470A Date Prepared 03/15/2018 1745h
Mercury 0 00342 mg/L Svv7470A 0 0000307 0 000150 0 003330 0 103 80 - 120
Report Date 3/27/2018 Page 53 of 87
All analyacs applicable to the CW 'zIP,VA, and FU RA are pei formed m accordance to NLIA( piotoeola Pin tment sampling informaton is located on the alached C Oc Confidential Rus.ness Infitinanon epoil IS pi ov nded [or the exclusive use ol the addiessee Pmileges of subsequent uae atlas mune of this company or and in rriber of as stafh or repro,insa » on of this report in yinnection with thd ady or:ism-lent, promotion or sale of any pr oduct ci r» ocess õr in connection yyith trie d-pubinfation of this report for any purposo othei than for the addresiice ykill be drained onb on contain Ilus riiiiiisacceptsionsdniatiour manse tlort Ara, 31, lr rtce jjijr anti ails the :rade aillinct
an MI ale 411.111111111111/1111.
11.111 1111111 11.1 MB SIM an 1101 allit 1111111
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone]. Fax: [phone] Laboratory Director
e-mail. [e-mail], eb: www.awal-lahs.cont
Jose Rocha
QA Officer _Qc SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: ME
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID:
Test Code
MB-54532
6010D-W
Date Analyzed
Date Prepared
03/16/2018
03/09/2018
1143h
1114h
Calcium < 1 00 mg/L SW6010D 0 0119 1 00
Iron < 0 100 mg/L SW6010D 0 0180 0 100
Magnesium < 1 00 mg/L SW6010D 0 0568 1 00
Potassium < 1 00 mg/L 5W6010D 0 106 1 00
Sodium < 1 00 rng/L SW60101) 0 0375 1 00
Tin < 0 500 mg/L SW60 I OD 0 00543 0 500
Vanadium < 0 00500 mg/L SW6010D 0 00105 0 00500
Lab Sample ID: MB-54532 Date Analyzed 03/20/2018 1926h
Test Code 6020B-W Date Prepared 03/09/2018 1114h
Antimony < 0 00200 mg/L SW6020B 0 000123 0 00200
Arsenic < 0 00200 mg/L 5W6020B 0 000576 0 00200
Barium < 0 00200 mg/L SW6020B 0 000173 0 00200
Beryllium < 0 00200 mg/L SW6020B 0 0000516 0 00200
Cadmium < 0 000500 mg/L SW6020B 0 000100 0 000500
Chromium < 0 00200 rng/L SW6020B 0 000354 0 00200
Cobalt < 0 00400 mg/L SW6020B 0 000151 0 00400
Copper < 0 00200 mg/L SW6020B 0 00107 0 00200
Lead < 0 00200 rng/L SW6020B 0 000444 0 00200
Manganese < 0 00200 mg/L 5W6020B 0 000270 0 00200
Nickel < 0 00200 rng/L SW6020B 0 000177 0 00200
Selenium < 0 00200 mg/L SW6020B 0 000278 0 00200
Silver < 0 00200 ing/L SW6020B 0 0000404 0 00200
Thallium < 0 00200 mg/L 5W6020B 0 000174 0 00200
Zinc < 0 00500 mgd. SW6020B 0 00159 0 00500
Report Date 3/27/2018 Page 54 of 87
All analyses applicable to the CW A, SDW A, and RCR A are pet formed in t.c.cordance to Nl A( pi otocols Pcitment sampling info, locan.d on the alached CDC ( 'ord triennial lliismess Infig motion I he, ieport is niosoded for the exclusive use of the add, esice Pr nileges of subscquent use of ihe
name atlas company or a ay member of its staff or rcp,:xhiction of this report in connection with the ads criisement, promotion or gale of any tnoduct ot ocess, or in connection v. th thc ic-pabocation of this teport for ans purpose •_Yhet than for thc addressee will be granted only on contact This
COMIKI iv accents no responsibility e‘cept t dae ne-IniTIVrICE .): invection flJ,y anttlygis in vood 4%1th ind eliinit t cg o trade aril ge e
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], vveb: www.awal-lahs.com
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: ME
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: MB-54656 Date Analyzed 03/16/2018 844h
Test Code FIG-W-7470A Date Prepared 03/15/2018 I 745h
Mercury < 0 000150 mg/L SW7470A 0 0000307 0 000150
Report Date 3/27/2018 Page 55 of 87 Alt analeses applicable to the CWA, SOW A, and RA RA are per formed in accordance to NIA A( protheols Pertinent samplyG nPumatiori is located on the atOched COC odidential Business Information Ibis ieport is piosiihat for Are estall 41 ve use of the addressee Privileges of subsequent rige of the nainc of this cc ropant, or any rnetrincr of its staff, or reprott action of this repon in connection \kith tific advertsement proinotim side of airs itiroduct of pi ocess. or in cimnectio AMA thc ie-pubheat en of this report tor an}. purpose mho than tor the adJiestee tic eranted onb on contact This ciinapitecepts resoonsibiiity e \ cent fOr thc due nertoi mance oimition and:or analysis Jr coed faith and oe.cio rotes e'the !fade and of smite,
1111111111.11111111110-411101111.
Client: AECOM
Lab Set ID: 1803136
Project: Payson City Landfill / 60544100.4
ale OM IIIIIII On 111111 11111 1111. 4111111 111111 111111
3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone], Toll Frzz: [phone]. Nix: [phone]
e-mail: awalgawal-labs.eom, web: www.awal-lahs.com Jose Rocha
QA Officer
QC SUMMARY REPORT
Contact: Lawrence Cannon
Dept: ME
QC Type: MS
Analyte
Reporting Amount Spike Ref. RPD Ref. RPD
Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID:
Test Code
1803136-00511MS
6010D-W
Date Analyzed
Date Prepared
03/16/2018 1157h
03/09/2018 11I4h
Iron 1 39 mg/L SW6010D 0 0180 0 100 1 000 0 401 98 6 75 - 125
Magnesium 44 4 mg/L SW6010D 0 0568 1 00 10 00 34 6 97 7 75 - 125
Potassium 20 6 mg/L SW6010D 0 106 1 00 10 00 10 3 103 75 - 125
Sodium 78 4 mg/L SW6010D 0 0375 1 00 10 00 68 9 94 7 75 - 125
Tin 0 965 mg/L SW6010D 0 00543 0 500 1 000 0 96 5 75 - 125
Vanadium 0 191 mg/L SW6010D 0 00105 0 00500 0 2000 0 95 4 75 - 125
Lab Sample ID: 1803136-005HMS Date Analyzed 03/16/2018 12I9h
Test Code 6010D-W Date Prepared 03/09/2018 1114h
Calcium 101 mg/L SW6010D 0 0238 2 00 10 00 93 78 8 75 - 125
Lab Sample ID: 1803136-005HMS Date Analyzed 03/20/2018 1950h
Test Code 6020B-W Date Prepared 03/09/2018 1114h
Antimony 0 215 rng/L SW6020B 0 000123 0 00200 0 2000 0 107 75 - 125
Arsenic 0 212 mg/L SW6020B 0 000576 0 00200 0 2000 0 00137 105 75 - 125
Barium 0 308 rng/L SW6020B 0 000173 0 00200 0 2000 0 109 99 4 75 - 125
Beryllium 0 196 mg/L SW6020B 0 0000516 0 00200 0 2000 0 98 2 75 - 125
Cadmium 0 200 mg/L SW6020B 0 000100 0 000500 0 2000 0 100 75 - 125
Chromium 0 207 mg/L SW6020B 0 000354 0 00200 0 2000 0 00277 102 75 - 125
Cobalt 0 203 mg/L SW6020B 0 000151 0 00400 0 2000 0 00131 101 75 - 125
Copper 0 199 mg/L SW6020B 0 00107 0 00200 0 2000 0 00108 98 8 75 - 125
Lead 0 200 mg/L SW6020B 0 000444 0 00200 0 2000 0 99 8 75 - 125
Manganese 0 252 mg/L SW6020B 0 000270 0 00200 0 2000 0 0429 105 75 - 125
Nickel 0 260 mg/L SW6020B 0 000177 0 00200 0 2000 0 058 101 75 - 125
Selenium 0 205 mg/L SW6020B 0 000278 0 00200 0 2000 0 00159 102 75 - 125
Silver 0 186 mg/L SW6020B 0 0000404 0 00200 0 2000 0 93 0 75 - 125
Thallium 0 196 mg/L SW6020B 0 000174 0 00200 0 2000 0 98 1 75 - 125
Zinc 1 02 mg/L SW6020B 0 00159 0 00500 1 000 0 00286 101 75 - 125
Report Date 3/27/2018 Page 56 of 87
All analyecs appheable to the CW A SIM A and II( RA are per formed in accordance to NIA,A( protocols Pet linent sampling in rol matron re located on Cle attache(' ( OC Confidential !kermess lnformoon I hi, report Is ITIOvIdud for the exclusive use ol the addressee Privileges of subsequent Lica of the
lame of this company OT any inembcr o" Its staff, or reproduction of thi, report in connection with the cid verliserreni, pro.net 01 or Note of any product or process or or connection with the re-publreatioa of this report tor anv purpose Jther than tor the addressee wt.l be granted on.y on contact Tins
compnv accept.. no responsibility meet thc ch,c nertoi ma 1,c of inspectrim mid/or arilvsiv in 'coed faith and accJrclrma tr. tla rules o' the trade ird cnce
Kyle F. Gross
Laboratory Director
3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
[e-mail], web: www.awal-lahs.corn
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: ME
Project: Payson City Landfill / 60544100.4 QC Type: MS
Reporting Amount Spike Ref. RPD Ref. RPD Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: 1803136-005HMS Date Analyzed 03/16/2018 853h
Test Code HG-W-7470A Date Prepared 03/15/2018 1745h
Mercury 0 00348 mg/L SW7470A 0 0000307 0 000150 0 003330 0 104 80 - 120
Report Date 3/27/2018 Page 57 of 87
All analyses appkable lo the CWA, .1DirVA, and R(._ RA arc per loaned ur accaodunce NI..1 AC. notocols Pertment csinpling ink matron rs loeated un ihe attached ( OC Cunt identre I llusmer.s lnformairon flub report is prostdral for the OULISIVe use ol the addressee Prryileges oesuIrseclutra use .he name of this company any nern her of Its staff or reptojactson of th, report In corncou on wsth the ady et tryernent, nreatattroo or sale ot any ploduct plot:ow or In conrootion uath the etpublreatron of this report tor any purpose othen than tor the addressee voll ptantcd only on contact Thrs Ciairceptsoaritarnior the due perfoonance Mir on antFor analysis yooa foal and accordraa to the rulas of the trade and of sere rot
Man MI
111111 11111. MN 111111 11.1 1111. 3440 South 700 West
Salt Lake City. UT 84119 Kyle F. Gross
l'hone: (8011263-8686, Toll Free: [phone], Fax: 1,8011 263-8687 Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: ME
Project: Payson City Landfill / 60544100.4 QC Type: MSD
Analyte
Lab Sample ID:
Test Code
1803136-005HMSD
6010D-W
Result
Date Analyzed
Date Prepared
Units Method
03/16/2018 1159h
03/09/2018 11I4h
MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC Limits
RPD Ref.
Amt % RPD
RPD
Limit Qual
Iron
Magnesium
Potassium
Sodium
Tin
Vanadium
Lab Sample ID:
Test Code
1803136-005HMSD
60I0D-W
1 40
44 5
20 7
79 7
0 958
0 189
Date Analyzed
Date Prepared
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
03/16/2018
03/09/2018
SW6010D
SW6010D
SW6010D
SW6010D
SW6010D
SW6OIOD
1222h
1114h
0 0180
0 0568
0 106
0 0375
0 00543
0 00105
0 100
1 00
1 00
1 00
0 500
0 00500
1 000
10 00
10 00
10 00
1 000
0 2000
0 401
34 6
10 3
68 9
0
0
100
98 5
105
108
95 8
94 4
75 - 125
75 - 125
75 - 125
75 - 125
'75 - 125
75 - 125
I 39
44 4
20 6
78 4
0 965
0 191
1 22
0 185
0 559
1 70
0 694
1 02
20
20
20
20
20
20
Calcium
Lab Sample ID:
Test Code
1803136-005IIMSD
6020B-W
101
Date Analyzed
Date Prepared
mg/4
03/20/2018
03/09/2018
SW6010I)
1953h
1114h
0 0238 2 00 10 00 93 77 1 75 - 125 101 0 163 20
Antimony
Arsenic
Barium
Beryllium
Cadmium
Chromium
Cobalt
Copper
Lead
Manganese
Nickel
Selenium
Silver
Thallium
Zinc
0 217
0 204
0 315
0 200
0 202
0 203
0 199
0 197
0 207
0 251
0 255
0 208
0 187
0 201
I 03
mg/L
mg/L
raWL
rng/L
rng/L
mg/L
rng/L
mg/1_,
mg/L
mg/L
ing/L
mg/L
rng/L
mg/L
rrig/L
SW6020B
SW6020B
SW602013
SW602013
SW6020B
SW6020B
SW6020B
SW6020B
SW6020B
5W6020B
SW6020B
SW6020B
5W6020B
5W6020B
SW6020B
0 000123
0 000576
0 000173
0 0000516
0 000100
0 000354
0 000151
0 00107
0 000444
0 000270
0 000177
0 000278
0 0000404
0 000174
0 00159
0 00200
0 00200
0 00200
0 00200
0 000500
0 00200
0 00400
0 00200
0 00200
0 00200
0 00200
0 00200
0 00200
0 00200
0 00500
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
0 2000
1 000
0
0 00137
0 109
0
0
0 00277
0 00131
0 00108
0
0 0429
0 058
0 00159
0
0
0 00286
108
101
103
99 8
101
100
98 8
97 8
103
104
98 3
103
93 4
101
103
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
75 - 125
0 215
0
0 2
30128
0 196
0 2
0 207
0 203
0 199
0 2
0 252
0 26
0 205
0 11986
0

6
1 02
1 04
4 25
2 22
I 64
0 589
1 98
1 87
0 958
3 59
0 557
2 05
1 35
0 443
2 47
1 22
20
20
20
20
20
20
20
20
20
20
20
20
20
20
20
Report Date 3/27/2018 Page 58 of 87
All analyses appludble to the CWA 'iDWA, and R( RA are per funned in accordance to N1.1.A( protocols Per talent sampling nlormabon is located on the lowlier! ( OC ( orifideritial liminess Information 711,, lepori peosidexl for .he orclusore /Ise of the addressee Pr sileges of subsequent use of the
name of tlus compary or any member arts stall or repro.hietron of thrs report in c,nneetior with the a.lscrt sement, pro notion or sale of ;my odLet or is oeess, or in connectiod s,ti, tne le-public:it on of tuts report for any purpose othei than for the addressee will be ',ranted only on Contact This
com is iv accents no responsibrlity e,,cent for d lc cLie nerio tn., of irs.nct ion ..tni tor an sis lr 2oocl kir 1 c111d .11:1 'din" '11 ti,. rules n't1 e -rale dr j nt
3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone], Toll Free: [phone]. Fax. [phone]
e-mail: awal:i.414al-labs.com, %Net): www.awal-lahs.com
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: ME
Project: Payson City Landfill / 60544100.4 QC Type: MSD
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: 1803136-005IIMSD Date Analyzed 03/16/2018 855h
Test Code 1IG-W-7470A Date Prepared 03/15/2018 1745h
Mercury 0 00345 pag/L SW7470A 0 0000307 0 000150 0 003330 O 104 80 - 120 0 00348 0 770 20
Report Date 3/27/2018 Page 59 of 87
All analv,es applicable to the CW A 'zDWA and fiX RA are pei funned in accordance to NI otocols Pea tment sampling mini illation is located on the attached CM` Confidential liminess Intormation This ieport is pi os klud for the exclusive use ul the add, essee Privileges of subsi..quent use of the
'rem: ot this Ponspany or tidy inernbcr of its staft, or reproduction of this report tn connection voth the akerz,svmmt, prionotton or stile of any product oi pi ocess or in connection vdth the ic-publisrttion of this report for any purposc odic, than for the add, esser Will Fe granted onis.on contoct This
citiiiarcepesmitsihtlavirnor th,. ctimarno Ice11jt5i».tnsnlair In stali acd dccordina to thy retcs of the trade mid
MI 1111111/ 111111/ MO MO MIN IIIII
1111. an 1111111 11111 1.1. alle OM MI MI 3440 South 700 West
Salt Lake City. UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone]. Fax. [phone] Laboratory Director
[e-mail], web: www.awal-labs.com Jose Rocha
QA Officer
QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: WC
Project: Payson City Landfill / 60544100.4 QC Type: DUP
Analyte Result Units
Lab Sample ID: 1803136-002CDUP Date Analyzed 03/07/2018
rest Code PEI-4500E1+B
pH g 25° C 6 85 pH Units
Lab Sample ID: 1803136-005CDUP Date Analyzed 03/07/2018
Test Code PH-4500H+B
7 4 I pH Units
Lab Sample ID: 1803136-005DDUP Date Analyzed 03/08/2018
Test Code IDS-W-2540C
Total Dissolved Solids 568 g/L
- Thgh RPD due to suspected sample non-homogeneity or matrtx interference
Method
1935h
MDL
Reporting Amount Spike Ref.
Limit Spiked Amount %REC Limits
RPD Ref.
Amt % RPD
RPD
Limit Qual
SM4500-H+B 1 00 1 00 6 91 0 872 5
2105h
SM4500-H+B 1 00 1 00 7 36 0 677 5
1210h
SM2540C 15 7 20 0 472 18 5 5 g
pH g 25° C
Report Date 3/27/2018 Page 60 of 87
All analyses appla,able to the CWA '41)W A, and R( RA aro ',dimmed m zaaaticlance to NI,I AC pi ()toads Pei talent -tempting lamination iii located on the attached ( OC Confidential I fusiness Information flub ieport IS i ovid.l for the anclusive use of the addiessee Pr vilegos of sulisequcn. use of tl'e
'lame of tins eompany or any member of Its sof I. or reproiuction of this report in ronnoceon with the aiit erhszmeni, prointaioil or sale of um/ ,troducit or pi ecess, or ir conneetioii vani the ie-pub'leation of this report for any purpose other 'hen for the add, estate will '.:4! emoted only on contact rhis
iieeep-s no iespersibilire eent for thi, due ne-fo 111,1n, e irspecnon and/or anali •ns ir frood iiti ard acaord.ne - u es of the, tr tee Ind it view
3440 South 700 West
Salt Lake City, (JT 84119
Phone: [phone], Toll Free: [phone], Fax. [phone]
[e-mail], web: INV% w.awal-labs.corn
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: WC
Project: Payson City Landfill / 60544100.4 QC Type: LCS
Analyte Result Units Method MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC
RPD Ref. RPD
Limits Amt % RPD Limit Qual
Lab Sample ID: LCS-R111240 Date Analyzed 03/14/2018 1241h
Test Code 300 O-W
Chlonde 5 18 mg/L E300 0 0 0581 0 100 5 000 0 104 90 - 110
Sulfate 5 46 mg/L E300 0 0 102 0 750 5 000 0 109 90 - 110
Lab Sample ID: LCS-R110999 Date Analyzed 03/08/2018 800h
Test Code ALK-W-2320B
Alkalinity (as CaCO3) 250 mg/L SM2320B 2 14 10 0 250 0 0 100 90 - 110
Lab Sample ID: LCSI -R110998 Date Analyzed 03/08/2018 617h
Test Code COD-HACH8000
Chemical Oxygen Demand 307 mg/L nACI-I8000 2 83 10 0 300 0 0 102 85 - 115
Lab Sample ID: LCS2-R110998 Date Analyzed 03/08/2018 617h
Test Code COD-HACH8000
Chemical Oxygen Demand 93 0 mg/L HACH 8000 2 83 10 0 100 0 0 93 0 85 - 115
Lab Sample ID: LCS3-R110998 Date Analyzed 03/08/2018 617h
Test Code COD-HACH8000
Chemical Oxygen Demand 9 00 mg/L HACH 8000 2 83 10 0 10 00 0 90 0 85 - 115
Lab Sample ID: LCS-R110998 Date Analyzed 03/08/2018 617h
Test Code COD-HACH8000
Chemical Oxygen Demand 900 mg/L HACH 8000 28 3 100 1,000 0 90 0 85 - 115
Lab Sample ID: LCS-54599 Date Analyzed 03/14/2018 9031i
Test Code NH3-W-350 1 Date Prepared 03/14/2018 640h
Ammonia (as N) 10 6 mg/L E350 I 0 0330 0 0500 10 00 0 106 90 - 110
Report Date 3/27/2018 Page 61 of 87
A II analyses applmable to the CWA SOI,V A, end R( RA arc pei formed in accordalee to NI.I.A( piotoeols Pei linent sainphng information is located on the altiehed Ihismess Information his ieport is pi osided for the exilisive use ol addi iCe Privileges ot subsequent use of the mune of dus compant, or any ruembs r of us Math or reprolattIon of that report In conneonon with the ad, cr hsernent, proototron or stde ot ant,: prodam or pi OCel,s, or nt connection watlr the te-pub leatutat of the, report tor try purpose other than for the addlassac v,t I orantcd onh oantaat This emiacceptsairschhotraor the drama Ice iiiiron lop ,IS 1 Il ale and a, ..aordana to tha lila trade
1111111 ala an
Analyte
Lab Sample ID: LCS-R110985
Test Code NO3-W-353 2
Nitrate (as N)
Lab Sample ID: LCS-R110987
Test Code PH-4500H+B
Result Units
Date Analyzed 03/07/2018
1 03 mg/L
Date Analyzed 03/07/2018
8 90 pH Units
Date Analyzed 03/07/2018
9 09
Date Analyzed
pH Units
03/08/2018
200 mg/L
Date Analyzed 03/16/2018
9 71 mg/L
g 25° C
Lab Sample ID: LCS-RI10988
Test Code PH-4500H+B
pH g 25° C
Lab Sample ID: LCS-R1I1055
Test Code TDS-W-2540C
Total Dissolved Solids
Lab Sample ID: LCS-R111291
Test Code TOC-W-5310B
Total Organic Carbon
MB MI MO 11110 MB MI
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: aml@avk al- labs.com, v‘eh: www.awal-lahs.com
Client: AECOM
Lab Set ID: 1803136
Project: Payson City Landfill / 60544100.4
MI MI Mill MI MI In
Kyle F. Gross
Laboratory Director
J ose Rocha
QA Officer QC SUMMARY REPORT
Contact: Lawrence Cannon
Dept: WC
QC Type: LCS
Reporting Amount Spike Ref. RPD Ref. RPD
Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qua)
1856h
E353 2
1935h
0 00799 0 0100 1 000 0 103 90 - 110
SM4500-H+13
2105h
1 00 1 00 9 000 0 98 9 98 - 102
SM4500-H FB
1210h
1 00 1 00 9 000 0 101 98 - 102
SM2540C
1306h
7 87 10 0 205 0 0 97 6 80 - 120
SM5310B 0 715 1 00 10 00 0 97 1 90 - 110
Report Date 3/27/2018 Page 62 of 87
Nil dna lyses appin,a ble to the MA. NIAVA, arid IICRA ere per formed to taxordance tn N otocols Pea intent sainpl log nfoonation IN located on tha attached ( 0C ( onlidernial ikasint.,as hVormation ilt.s leport 'no, tiled for the excluorve use untie addiosser Pris ;lege,. of S)...quoin use of the
name ot tins company nr ten; membcr of ns staff_ ur reproducoon ,1 the, repon m connection with the advertisement_ promotion or sale of any pi oduct or lioness_ or in connection troth the repubncetion of this repot t tor any purpose other than for the addreswe yell be reamed only on contact I his
corn accepts no responsi Hoe e cept t., ttc dee oar,b limns e of nyectron emi/or toe hist, in eood Piet and act-a-din. to en ru c‘ of the trade or., sctek
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
3440 South 700 West
Salt Lake City. VT 84119
Phone: [phone]. Toll Free: [phone], Fax. [phone]'7
e-mail: awalgawal-labs.emn, web: www.awal-lahs.com
Qc SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: WC
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Result
Date Analyzed
Units
03/14/2018
Method
1225h
MDL
Reporting Amount Spike Ref. RPD Ref. RPD
Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
< 0 100 mg/L E300 0 0 0581 0 100
< 0 750 rng/L E300 0 0 102 0 750
Date Analyzed 03/08/2018 800h
< 10 0 mg/L SM2320B 2 14 10 0
< 10 0 mg/L 8M2320B 2 14 10 0
Date Analyzed 03/08/2018 617h
< 10 0 mg/L HACH 8000 2 83 10 0
Date Analyzed 03/14/2018 902h
Date Prepared 03/14/2018 640h
< 0 0500 mg/L E350 I 0 0330 0 0500
Date Analyzed 03/07/2018 1853h
<00100 mg/L E353 2 0 00799 0 0100
Date Analyzed 03/08/2018 1210h
< 10 0 mg/L SM2540C 7 87 10 0
Date Analyzed 03/16/2018 1251h
< 1 00 rng/L SM5310B 0 715 1 00
Report Date 3/27/2018 Page 63 of 87
All analyses applicable to the CW A, SDWA end RI RA are per formed in accordance to NIA Ax protocol, Pertinent sampling infnrmation 1,, located on the attached C'OC onlidentral lheaness Information Th, leport s proshkd for the exclusive use of Mt, addiessee Pr nfieges of subst-quent tem atilt Panto ot tl,,sCowan!, or any nce,le r of Its stat ft or reproduce on of the, report at t.onncepon wth the ac , et t,sctrent, prornottpo or attic at any yttoduct or pi ocetss, or In copeection Nclttl tho le-publ teat on of tho, report tor any purpose ot11,1 than for at, add, s sses ',4111 N. granted onb, on ,ont,tst Ihtu cairoceptssionsatalliiiiiio- the diiiiiiatanceilitronanjjjj and aka-110 the nal traae
NS NM MS an MB MS MI IMO UN
Analyte
Lab Sample ID: MB-R111240
Test Code 300 O-W
Chloride
Sulfate
Lab Sample ID:
Test Code
Bicarbonate (as CaCO3)
Carbonate (as CaCO3)
Lab Sample ID: MB-R110998
Test Code COD-HACH8000
Chemical Oxygen Demand
Lab Sample ID: NIB-54599
Test Code NH3-W-350 1
Ammonia (as N)
Lab Sample ID: MB-R110985
Test Code NO3-W-353 2
Nitrate (as N)
Lab Sample ID: MB-R111055
Test Code TDS-W-2540C
Total Dissolved Solids
Lab Sample ID: MB-R111291
Test Code TOC-W-5310B
Total Organic Carbon
MB-R110999
ALK-W-2320B
MI an 1111111 111111 an 11.0 11110 111. 3440 South 700 West
Salt Lake City. UT 84 1 19 Kyle F. Gross
Phone: [phone], Toll Free: (888, 263-8686, Fax: [phone] Laboratory Director
e-mail: [e-mail], ‘4eb: wv+w awal-lahs.com
Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: WC
Project: Payson City Landfill / 60544100.4 QC Type: MS
Analyte
Lab Sample ID: 1803136-003CMS
Test Code 300 O-W
Result
Date Analyzed
Units
03/14/2018
Method
2026h
MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC
RPD Ref. RPD
Limits Amt % RPD Limit Qual
Chlonde 1,230 mg/L E300 0 11 6 20 0 1,000 252 98 0 90 - 110
Sulfate 1,310 mg/L E300 0 20 4 150 1,000 322 99 1 90 - 110
Lab Sample ID: 1803136-005CMS Date Analyzed 03/08/2018 800h
Test Code ALK-W-2320B
Alkalinity (as CaCO3) 422 mg/L SM2320B 2 14 10 0 100 0 326 96 0 80 - 120
Lab Sample ID: I803136-005GMS Date Analyzed 03/08/2018 617h
Test Code COD-HACH8000
Chemical Oxygen Demand 46 0 mg/L HACH 8000 2 83 10 0 50 00 0 92 0 85 - 115
Lab Sample ID: 1803136-00.5FMS Date Analyzed 03/14/2018 908h
Test Code NI13-W-350 1 Date Prepared 03/14/2018 640h
Arnmorna (as N) 11 1 rng/L E350 0 0330 0 0500 10 00 0 111 90 - 110
Lab Sample ID: 1803136-005CMS Date Analyzed 03/07/2018 1949h
Test Code NO3-W-353 2
Nitrate (as N) 6 30 mg/L E353 2 0 0400 0 0500 5 000 1 02 105 90 - 110
Lab Sample ID: I803136-005EMS Date Analyzed 03/16/2018 1545h
Test Code TOC-W-5310B
Total Organic Carbon 26 9 mg/L SM5310B 3 58 5 00 25 00 1 36 102 80 - 120
- Matrix spike recovery indicates matrix interference The method is in control as indicated by the LCS
Report Date 3/27/2018 Page 64 of 87
All analyses applit,able to the ("WA, Sl)Vv A, and RC R A are pei funned tn accordance to MLA( mocols Raiment s'unplins information is located on the attach& ( OC ( ide•dial Ilusiness Inflame/ton I his iepoit is :no, ided tor tbe exclustve use ul thx. addiecsee Prisileges at subsequent wse of the
name of dus company or any member of its sta:i or reproduction ot ths report in connzetion with the adsornscrnent, prorny bon rir sale of s.ty oduct or process. or in connection ssith the re-publication of this report tor any put pose oaks than tor the addressee Kill be granted on[y on contact This
company accers no responsibeitv except tor the due perfoim...ke of inspection ard/o, anal,/ ars ir e.iod tk,t't and act., sd nil, tl Iv e'lle trade and if sc leiwe
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax. [phone]
e-rnail: [e-mail], web: www.awal-labs.corn
_QC SUMMARY REPORT
Result Analyte
426 Alkalinity (as CaCO3)
49 0
Date Analyzed
Date Prepared
Chemical Oxygen Demand
Lab Sample ID: 1803136-005FMSD
Test Code NH3-W-350 1
11 4 Ammonia (as N)
6 63 N ttrate (as N)
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: WC
Project: Payson City Landfill / 60544100.4 QC Type: MSD
Units Method
03/14/2018 2043h
MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC Limits
RPD Ref.
Ann % RPD
RPD
Limit Qual
mg/L E300 0 11 6 20 0 1,000 252 98 9 90 - 110 1230 0 749 20
mg/L E300 0 20 4 150 1,000 322 101 90 - 110 1310 1 77 20
03/08/2018 800h
mg/L SN42320B 2 14 10 0 100 0 326 100 80 - 120 422 0 943 10
03/08/2018 617h
mg/L HACH 8000 2 83 10 0 50 00 0 98 0 85 - 115 46 6 32 10
03/14/2018 909h
03/14/2018 640h
mg/L E350 I 0 0330 0 0500 10 00 0 114 90 - 110 11 1 2 13 10
03/07/2018 1950h
mg/L E353 2 0 0400 0 0500 5 000 1 02 112 90 - 110 6 3 5 17 10
03/16/2018 I 559h
mg/L SN45310B 3 58 5 00 25 00 l 36 91 1 80 - 120 26 9 10 8 20
- Matrix spike recovery indicates matrix Interference The method is in control as indicated by the LCS
Report Date 3/27/2018 Page 65 of 87
All analyses appluarble to the CW A, SIM A and RI. R A are per formed in accordance to NI IA( momeols Pertmert sampling information rs loeaud on the attached ( (IC Confidential Business information This report is provided for the exelusr re use ol the addressee Preilleges of subsequent use of the mane of this collipan!, or ally mernbc- Os staff or reproduenon 5,1 rh,s report In connection with •he advetzasement, oro.00tlon 0, sr,le ot U ly oduct or plocess, or In conreCtion wth the e-ptiblicatlon thas repolt or ary purposd other than tor the addiesvee Vvl bc orrolted only on contact rhrs Company accepts roiralltriar the dianlan,e andalsis in 0ood rad!, and accordlns :,, the rule., of the bade and ot science jjjj
alla MN MO Si MN MI
Lab Sample ID: 1803136-003CMSD Date Analyzed
Test Code 300 0-W
Chloride 1,240
Sulfate 1,340
Lab Sample ID: 1803136-005CMSD Date Analyzed
Test Code ALK-W-232013
Lab Sample ID: 1803136-005GMSD Date Analyzed
Test Code COD-HACH8000
Lab Sample ID: 1803136-005CMSD Date Analyzed
Test Code NO3-W-353 2
Lab Sample ID: 1803136-005EMSD Date Analyzed
Test Code TOC-W-5310B
Total Organic Carbon 24 1
Units Method MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC
RPD Ref. RPD
Limits Amt % RPD Limit Qual
03/08/2018 926h
03/07/2018 1730h
p.g/L SW8011 0 00316 0 0105 0 1000 0 111 60 - 130
110- SW8011 () 00334 0 0105 0 1000 o 98 3 48 8 - 146
ttg/L 5W8011 0 1000 91 2 65 - 157
Result
Date Analyzed
Date Prepared
Analyte
Lab Sample ID: LCS-54490
Test Code 8011-W
1,2-D ibromo-3-ch loropropane 0 111
1,2-Di bromoethane 0 0983
Surr 1,2-Dibromopropane 0 0912
1111. 1111. MI
3440 South 700 West
Salt Lake City. tJT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: awahiOwal-labs.eoln, web: www.awal-lahs.com
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
110111 MI UM IPS MI MN OM
Client: AECOM
Lab Set ID: 1803136
Project: Payson City Landfill / 60544100.4
Contact:
Dept:
QC Type:
Lawrence Cannon
GC
LCS

Report Date 3/27/2018 Page 66 of 87
A II analrres apphcable to the ('WA, `rzt)Wri,, and RA RA aro per formed in ac.r..ordance 10 Nl LA( protocols Penmen, samplIng information Is located on the attache(' ( OC Confidential Business 111114 inctron 'fins report provided tor the exclusive use of the addressee Pnvsleges of suf.sem.ent me of the
name ot this company or r. iv munber of its stat t or rcproductroo of this report m connection wrth the adscrtisament, promoted or sale ot any PtOucl or pi ocess, sr ir eonnectio i oath the I e-pubheation of this report tor ary purpose other than tor thc addi essee sciil cre reranted only on contact Tills
eo rr, rar iv m :opts no res,ronsilmistV es cent for- t re due per4or n c non andkr- deal, sr, ir rood and “0,,,sd fv, tilt !Islas o Ira* dr,1
3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-rnail: [e-mail], web: www.awal-lahs.com
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: GC
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: NIB-54490 Date Analyzed 03/08/2018 912h
Test Code 8011-W Date Prepared 03/07/2018 1730h
1,2-Dtbromo-3-chloropropane <00105 ttg/L SW8011 0 00316 0 0105
1,2-Drbromoethane < 0 0105 ng/L SW8011 0 00334 0 0105
Surr 1,2-Dibromopropane 0 0955 ug/L SW8011 0 1000 95 5 65 - 157
Report Date 3/27/2018 Page 67 of 87
All analyses apphLable to the CWA, OW& and R( RA dre per formed in accordance to N1.1.M protwols Per lawn, samphng .nformation located urr the attached ( OC i onfidentra liusrneos tntorrnat.on his report is pros.ded for the exclusive use a tht. addressee Prix ileges of subsequent LINe of the
name of t'us romparn, lr any membc r of its staff_ Or reprod OMNI of thts repot t 12,,Pnc011on wIth the aal set nsernert, prothot on ot sale ot ally rloduct or pt ocess, or in connection ss.th the I e-publicatien thrs report for any purpose mho than for the add] essre be aranted only on Contdst
chirh,a At accepts no reshot-rat-Arty escept fa- th,.. doe perorrss,, Ire salon seldfol aralvs.,s, sr coed thah ancl aceard al.2 TO tt le rules of the trade ond A shis sae
111111 MI MI 1111111 MO OM MO 1111111 11111 111111 Ma SIM
MI MI MI MB MI IIIIII 11111 UM al NM OM 11.11 ON NM
3440 South 700 West
Salt Lake City. Ur 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone], Fax: [phone]
Laboratory Director
e-mail: awal@av,al-labs.eom, web: www.awal-lahs.com
Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: GC
Project: Payson City Landfill / 60544100.4 QC Type: MS
Analyte Result Units Method MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC
RPD Ref. RPD
Limits Amt % RPD Limit Qual
Lab Sample ID: 1803136-005BMS Date Analyzed 03/08/2018 1050h
Test Code 8011-W Date Prepared 03/07/2018 1730h
1,2-Dtbromo-3-chloropropane 0 119 ug/L SW8011 0 00307 0 0102 0 09717 0 122 58 - 148
1,2-D ibromoethane 0 0736 µg/L SW8011 0 00325 0 0102 0 09717 0 75 7 34 - 161
Surr 1,2-Di broniopropane 0 0914 !_tg/L SW8011 0 09717 94 0 60 - 134
Report Date 3/27/2018 Page 68 of 87
analyees appl cable to the CWA, SIM A and 11(11A are pcifurrned m accordance to N1.1 A.( imotecole Pellinei,L sampling infoimation i located on Mc andellea Cardidential /Liminess Intininntion Ilme I epost is ni muted for The exclusive use ut thc addieseee Pris lege. a...subsequent Use of the
name ut tins company ot anv metnbc- of its stall. or rcproducuon of this report in connecuon with the atheinsemerc promotion or sale ot i ooduct 01 process, or in connection vt.th the ie-pablicatioit fthi.. report for any purpcsa other than for the addlessee oall ye eranted only en contact I lus
Conno, iv accepts no responeilmhtv event for tit, ode neat>, rnt•we of onnection and,o- n,ilvs" emid /Tut') and .1 ne •,) the reIcs o= the irsdc -f sex Tut',
3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: awal(Oawal-labs.eom, \Net): www.awal-labs.com
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: GC
Project: Payson City Landfill / 60544100.4 QC Type: MSD
Analyte
Lab Sample ID: 1803136-005BMSD
Result
Date Analyzed
Units Method
03/08/2018 11I8h
MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC Limits
RPD Ref.
Aint % RPD
RPD
Limit Quai
Test Code 8011-W Date Prepared 03/07/2018 1730h
1,2-Dibromo-3-ehloropropane 0 112 ug/L SW80 l l 0 00308 0 0102 0 09749 0 115 58 - 148 0 119 5 98 25
1,2-Dthromoethane 0 0709 ug/L SW801 1 0 00326 0 0102 0 09749 0 72 8 34 - 161 0 0736 3 62 25
Surr 1,2-Dibrornopropane 0 0857 ug/L SW8011 0 09749 87 9 60 - 134
Report Date 3/27/2018 Page 69 of 87 Al: analyses apphsable to the CWA, SOW A and R( RA are per formed in secordance to NI .A( :notocols Pei tment sampling Information is located on the attached ( OC ( out ;denim! l3usiness Informal-ton ïhs report is pi osadsd for the cxultruve use of the addressee Prrsi leges of subsequent use of the narnoof thts company or anat ititrinber of its staff, or roprodcetton of thrs repot t connection \Ninth the advertisement, proirinhor or sale or oduct or process, or In connection ooth thete-pubheat on or thrs report tor any taurpose other than for tho addressee will et, pranted onls on co ntaet ins
C acceptsumnsibititviaor the cideuiforrnaoreatition andtor dpaiVsr, "pod &nth and accordine to the rules of the trade and ot scrence
111111 IMP 1111.-1111.- 1111111 MEM
•b ra
In NM =I 11.2 1.11 11.1 3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone]. Toll Free: [phone]. Fax. [phone]
Laboratory Director
e-mail: [e-mail], web: www.awal-lahs.com
Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: LCS
Analyte
Lab Sample ID: LCS-54502
Test Code 8270-W-3511
Result
Date Analyzed
Date Prepared
Units
03/09/2018
03/08/2018
Method
1449h
1233h
NIDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC
RPD Ref. RPD
Limits Amt % RPD Limit Qual
2,4,6-Trichlorophenol 82 9 pg/L SW8270D 2 85 10 0 100 0 0 82 9 10 - 179
2,4-amethylphenol 90 2 ug/L SW8270D 4 62 10 0 100 0 0 90 2 25 - 123
2,4-Dmitrotoluene 101 ug/L SW8270D 2 30 10 0 100 0 0 101 35 - 161
2-Chloronaphthalene 99 7 pg/L 5W8270D 1 63 10 0 100 0 0 99 7 22 - 172
2-Chlorophenol 72 3 pg/L 5W8270D 6 84 10 0 100 0 0 72 3 14 - 117
4,6-Dinitro-2-methylphenol 71 0 ug/L 5W8270D 7 70 10 0 100 0 0 71 0 10 - 156
4-Chloro-3-methylphenol 69 4 ligil-, 5W82700 4 62 10 0 100 0 0 69 4 16 - 127
4-Nurophenol 12 0 PO- SW8270D 1 38 10 0 100 0 0 12 0 10 - 80
Acenaphthene 92 6 ug/L SW8270D 2 42 10 0 100 0 0 92 6 45 - 132
Benzo(a)pyrene 92 0 ug/L 5W8270D 3 33 10 0 100 0 0 92 0 29 - 195
N-Nitrosodi-n-propylamme 71 8 ttg/L SW8270D 6 44 10 0 100 0 0 71 8 10 - 180
Pentachlorophenol 49 6 ug/L SW8270D 3 02 10 0 100 0 0 49 6 10 - 158
Phenol 42 0 pg/L SW8270D 1 22 10 0 100 0 0 42 0 10 - 100
Pyrene 92 6 ttg/L SW8270D 2 97 10 0 100 0 0 92 6 41 - 159
Surr 2,4,6-Tribrornophenol 41 2 ug/L SW8270D 50 00 82 3 10 - 227
Surr 2-Fluoroblphenyl 24 1 ttg/L SW8270D 25 00 96 4 23 - 145
Surr 2-Fluorophenol 27 6 µg/L SW8270D 50 00 55 3 10 - 110
Surr Nitrobenzene-d5 25 4 Mil- 5W8270D 25 00 102 39 - 174
Surr Phenol-d6 23 3 ttg/L SW8270D 50 00 46 6 10 - 100
Surr Terphenyl-d14 24 3 ug/L 5W8270D 25 00 97 1 30 - 199
Report Date 3/27/2018 Page 70 of 87
All analyses appludble to the CWA SDW arid R A dre performed m accordance to NU A( protocols Pertinent sampling m Nriation is located on the attached COC Confidential liiismess leormation 1 lus report is provided for the CseAuslye use ul tho addressee Privileges of subsequent use or the
name of this company or any member of its staff. or reproduction cif ths repot t in connection with the advertisement, promot Lin or ic.le of any product or IN ocess. oi in cOnneCncin csit'd tne te-publicat on of this report for any purpose othei than tor the addressee will he oranted onlv or. contact flus
c0mp7.iv neer no responsibility esecut for the doe eerily man. e mspec tion ard/ir amlysis in di)Cri 1411th ard a:cord .11, 'a Vie 0..es o' the rrale ard ot nee
3440 South 700 West
Salt I.ake City. UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-rnail: [e-mail], web: wv,w.awal-lahs.com
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: MB-54502
Test Code 8270-W-3511
Date Analyzed
Date Prepared
03/09/2018 I 427h
03/08/2018 1233h
1,2,4,5-Tetrachlorobenzene < 10 0 ng/L SW8270D 2 38 10 0
1,3,5-Trinitrobenzene < 10 0 Rg/L SW8270D 1 41 10 0
1,3-Dmitrobenzene < 10 0 Rg/L SW8270D 2 23 10 0
1,4-Naphthoquinone < 10 0 µg/L SW8270D 4 18 10 0
I ,4-Pheny1ened tamme < 10 0 ligit. SW8270D 1 42 10 0
1-Naphthylamme < 10 0 ng/L SW8270D 7 71 10 0
2,3,4,6-Tetrachlorophenol < 10 0 Rg/L SW8270D 2 82 10 0
2,4,5-Triehlorophenol < 10 0 ge/L 5W8270D 2 92 10 0
2,4,6-Trtchlorophenol < 10 0 ng/L 5W8270D 2 85 10 0
2,4-Diehlorophenol < 10 0 Rg/L SW8270D 6 31 10 0
2,4-Dimethylphenol < 10 0 Rg/L SW8270D 4 62 10 0
2,4-Dmitrophenol < 10 0 [TX SW8270D 8 99 10 0
2,4-Dinitrotoluene < 10 0 ng/L 5W8270D 2 30 10 0
2,6-Dichlorophenol < 10 0 Rg/L SW8270D 5 53 10 0
2,6-Dmitrotoluene < 10 0 gg/L 5W8270D 3 42 10 0
2-Acetylammofl uorene < 10 0 ng/L SW8270D 3 76 10 0
2-Chloronaphthalene < 10 0 Rg/L SW8270D 1 63 10 0
2-Chlorophenol < 10 0 Rg/L SW8270D 6 84 10 0
2-Methylnaphthalene < 10 0 gg/L SW8270D 3 75 10 0
2-Methylphenol < 10 0 WI- SW8270D 2 43 10 0
2-Naphthylamme < 10 0 ng/L SW8270D 6 71 10 0
2-Nitroamline < 10 0 Rg/L SW8270D 4 25 10 0
2-Nitrophenol < 10 0 µg/L 5W8270D 5 81 10 0
3&4-Methylphenol < 10 0 nWL SW8270D 5 49 10 0
3,3"-Dichlorobenzidme < 10 0 Rg/L SW8270D 3 52 10 0
3,3"-Dimethylbenzidme < 10 0 PO- SW8270D 1 44 10 0
3-Methylcholanthrene < 10 0 ng/L 5W8270D 2 87 10 0
Report Date 3/27/2018 Page 71 of 87
All analyses apphcable to the CW A SDWA, and RC RA arc performed m accordance to NIA AC protocols Per tweet sampling Information ii loeated un the attteltee COC ( onlidential Business Intinmanon ihia eport is In osidt.t1 for the exclusive use 01 tin. addressee Privileges of saIrsetruent rere of the
name ot this compact, or any inernkr of-its staff or reproduction of tfus repo] i Ie Connection with the ach,of nsement, promotion or ,ala of any Imoduct or IN 0CeSS or io connection mill the ie-pubhcation of thrs report for any purposc alio that, for the acka essee \kill be granted onp on eenteet Tits
eimacceptimobilitimins the 11.01)fl animists ir and aaro the fair trade alleci
11.11 IMS 1111111
1111111 MI 1.1111 MO 3440 South 700 West
Salt Lake City, (JT 84119
Phone: [phone], Toll Free: [phone], Fax. [phone]
awaRawal-labs.com, web: www.awal-lahs.com
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: MBLK

Analyte

Reporting Amount Spike Ref. RPD Ref. RPD
Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: MB-54502
Test Code 8270-W-3511
Date Analyzed
Date Prepared
03/09/2018
03/08/2018
1427h
1233h
3-Nitroanilme < 10 0 PO- SW8270D 3 23 10 0
4,6-Dmitro-2-methylphenol < 10 0 ug/L SW82700 7 70 10 0
4-Ammobiphenyl < 10 0 ug/IL SW8270D 3 73 10 0
4-Bromophenyl phenyl ether < 10 0 ug/L SW8270D 2 69 10 0
4-Chloro-3-methylphenol < 10 0 ttg/L SW8270D 4 62 10 0
4-Chloroandine < 10 0 ug/L SW82700 7 49 10 0
4-Chlorophenyl phenyl ether < 10 0 µg/L 5W8270D 2 74 10 0
4-N itroanihne < 10 0 ug/L SW8270D 2 93 10 0
4-Nitrophenol < 10 0 pg/L SW8270D 1 38 10 0
5-Nitro-o-toltudine < 10 0 ug/L 5W8270D 3 94 10 0
7,12-Dimethylbenz(a)anthracene < 10 0 ttg/L SW8270D 6 01 10 0
a,a-Dimethylphenethylamine < 50 0 u.g/L SW8270D 26 1 50 0
Acenaphthene < 10 0 ug/L S W8270D 2 42 10 0
Acenaphthylene < 10 0 ug/L SW8270D 1 92 10 0
Acetophenone < 10 0 1-tgli- SW8270D 6 42 10 0
Anthracene < 10 0 ug/L SW82700 2 90 10 0
Benz(a)anthracene < 10 0 ug/L 5W82700 4 24 10 0
Benzo(a)pyrene < 10 0 ug/L SW8270D 3 33 10 0
Benzo(b)fluoranthene < 10 0 ug/L SW8270D 3 71 10 0
Benzo(g)m)perylene < 10 0 ug/L 5W8270D 3 57 10 0
Benzo(k)fluoranthene < 10 0 Pg/I- SW8270D 3 07 10 0
Benzyl alcohol < 10 0 ug/L SW8270D 1 79 10 0
Bis(2-chloroethoxy)methane < 10 0 pg/L 5W8270D 5 18 10 0
Bis(2-chloroethyl) ether < 10 0 tig/L SW8270D 4 78 10 0
Bis(2-chloroisopropyl) ether < 10 0 ug/L 5W8270D 3 43 10 0
Bis(2-ethylhexyl) phthalate < 10 0 uWL SW8270D 3 97 10 0
Butyl benzyl phthalate < 10 0 ug/L 5W8270D 5 20 10 0
Report Date 3/27/2018 Page 72 of 87
All analyses apphcable to the CWA, OW A, and Rt. RA ore per formco rn t.ccordance to NI A AC piotocolx Per intent ,ampl .n fix matron ix Ia.:nod on the attached COC Conhdennal liuson.rs Information l'h.s report is provedcd for the exchr,oe use of tho fakir exser Povileges of subsoquent use the
rume of elis company or LW incmhcr of its staff or reprodueuon of thrs report in connceum with thc aclv t.sement, promutron or sale of anv ;moduct or process, or in corn-or-Dm wrth tnc re-publreshon of tho report lor any purpose othel thon tor the midi essee wrIl be rya ncci on y on eontact This
cornrow. accept, no rexoor.s txliry except For the clue performance of rnspet non ard,o, analvsrx 1r g000 tan and ac, .rd.nu 1.r OH ides 0=flie trade and of
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax. (80 ) 263-8687
awal(Omt al-labs.com, web: www.awal-lahs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1 80313 6 Dept: MSSV
Project: Payson City Landfill / 605441 00.4 QC Type: MBLK
Analyte
Lab Sample ID: MB-54502
Test Code 8270-W-3511
Result
Date Analyzed
Date Prepared
Units
03/09/2018
03/08/2018
Method
1427h
1233h
MDL Reporting Amount Spike Ref. RPD Ref. RPD
Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Chlorobenzilate < 10 0 µg/L SW8270D 2 93 10 0
Chrysene < 10 0 µWI- SW8270D 2 87 10 0
Diallate (cis or trans) < 10 0 1-10-- SW8270D 3 18 10 0
Dibenz(a,h)anthracene < 10 0 ttg/L SW8270D 3 38 10 0
Dibenzofuran < 10 0 ug/L SW8270D 2 44 10 0
Diethyl phthalate < 10 0 ug/L 5W8270D 5 89 10 0
Dimethoate < 10 0 gg/L SW8270D 1 28 10 0
Dimethyl phthalate < 10 0 ug/L SW8270D 5 40 10 0
Dimethylaminoazobenzene < 10 0 ug/L SW8270D 2 45 10 0
Di-n-butyl phthalate < 10 0 ug/L SW8270D 3 99 10 0
Di-n-octyl phthalate < 10 0 ug/L SW8270D 4 16 10 0
Dinoseb < 10 0 µg/L SW8270D 6 71 10 0
Diphenylamine < 10 0 ug/L 5W8270D 2 42 10 0
Disulfoton < 10 0 PLO- 5W8270D 3 89 10 0
Ethyl methanesulfonate < 10 0 ttg/L 5W8270D 6 00 10 0
Famphur < 10 0 tig/L SW8270D 9 58 10 0
Fluoranthene < 10 0 ug/L 5W8270D 3 18 10 0
Fluorene < 10 0 ttg/L SW8270D 2 19 10 0
Hexachlorobenzene < 10 0 µg/L 5W8270D 2 91 10 0
Hexachlorobutadiene < 10 0 µWL 5W8270D 3 23 10 0
Hexachlorocyclopentadiene < 10 0 (tg/L 5W8270D 2 60 10 0
Hexachloroethane < 10 0 ug/L 5W8270D 2 65 10 0
l lexachloropropene < 10 0 PTA- SW8270D 4 44 10 0
Indeno(1,2,3-cd)pyrene < 10 0 ttg/L SW8270D 3 20 10 0
Isodrin < 10 0 µg/L SW8270D 3 43 10 0
Isophorone < 10 0 141- SW8270D 3 39 10 0
Isosafrole < 10 0 ligil, SW8270D 9 09 10 0
Report Date 3/27/2018 Page 73 of 87
All analyses apphsable to the CWA, SOW& and R( RA are perturrned 'A:cord:ewe to NIA A( protocols Penmen'. sarnpl nig Inforrnatrun ts I oeartd on the ('OC ( onlidelral usineis Infornuaron hp, report Is prosrdsx1 or the exclusive use or the addressee Privrleges of subsequent use of the ntlfne ot tins vorthant, or any mem hc r us stif f or reprodoetton of this report m connectlon with the adr orttsoment, promo-non or rale of any rroduct procatss, or tn conneetto vtett the le-put-the:1ton of thp. report tor -my purposs orlfu Ow for ths ad lusrkt ttrantcd only on sontast This einbaccoptsiiiirsaultti,T .61,1,nr eiiiitr on Ili., SIS in Poi, and accord .ne to tlie rule, of the trade tar MN MIN Mill 11111 MI F -1
Client: AECOM
Lab Set ID: 1 803 13 6
Project: Payson City Landfill / 60544100.4
11.1 1111. 111111 MN 1.11 41111. MN 3440 South 700 AN est
Salt Lake City. UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone]. FaN : (80n 263-8687 Laboratory Director
e-mail. awal'eOwal-labs.eorn, v‘eb: www.awal-lahs.com
Jose Rocha
QA Officer
QC SUMMARY REPORT
Contact: Lawrence Cannon
Dept: MSSV
QC Type: MBLK
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: MB-54502
Test Code 8270-W-3511
Date Analyzed
Date Prepared
03/0912018
03/08/2018
1427h
1233h
Kepone < 10 0 pg/L SW8270D 6 60 10 0
Methapyrilene < 10 0 ag/L SW8270D 9 81 10 0
Methyl methanesulfonate < 10 0 µg/L SW8270D 1 66 10 0
Methyl parathion < 10 0 Pgr/I- SW8270D 2 72 10 0
N itrobenzene < 10 0 itg/L SW8270D 2 37 10 0
N-Nitrosodiethy lam ine < 10 0 µg/L SW8270D 4 98 10 0
N-Nitrosodirnethylamine < 10 0 µg/L SW8270D 1 17 10 0
N-Nitrosodi-n-butylarnine < 10 0 µWL SW8270D 6 48 10 0
N-Nitrosodi-n-propylarn I ne < 10 0 µg/L SW8270D 6 44 10 0
N-Nitrosodiphenylamine < 10 0 pg/L SW8270D 2 66 10 0
N-Nitrosomethylethylamme < 10 0 µg/L SW8270D 6 38 10 0
N-Nitrosopiperidine < 10 0 ag/T SW8270D 4 72 10 0
N-Nitrosopyrrolidine < 10 0 pg/L SW8270D 4 31 10 0
0,0,0-Triethyl phosphorothioate < 10 0 µg/L SW8270D 2 91 10 0
o-Toluidine < 10 0 µg/L SW8270D 8 38 10 0
Parathion < 10 0 p.g/L 5W8270D 2 19 10 0
Pentachlorobenzene < 10 0 p.g/L SW8270D 2 26 10 0
Pentachloromtrobenzene < 10 0 µg/L 5W8270D 4 92 10 0
Pentachlorophenol < 10 0 ligil- SW8270D 3 02 10 0
Phenacetin < 10 0 pg/L 5W8270D 2 39 10 0
Phenanthrene < 10 0 ug/L SW8270D 2 82 10 0
Phenol < 10 0 pg/L SW8270D 1 22 10 0
Phorate < 10 0 µg/L SW8270D 2 99 10 0
Pronamide < 10 0 IAA' SW8270D 3 40 10 0
Pyrene < 10 0 tig/L 5W8270D 2 97 10 0
Safrole < 10 0 ug/L 5W8270D 1 74 10 0
Thionazin < 10 0 Pgil- SW8270D 5 38 10 0
Report Date 3/27/2018 Page 74 of 87
All analyses applutoble to the (IVA, SDW A, and ft,Cli A dre pei formed in accordance to protoeols Pet intent samplms liminattort Is located on the anoc bed COC Confidential linsmess lnformanon '1 hrs ieport is niosultAl for the exclusive use attar addressee Prryileges of subs...went use of tbe
name dors company or any member of rts stall. or reprodualon oftfirs report in eonnecut n waft the adyeruserrent, promotion ur sale of any product or IN ocess, or ut connectron ss.th fru: le-pubratatron of this report tor any purpose other than tor the addressee. *Ili be vranted only on contact This
roan,- ry accepts no t'esoontobrlitv escept tor to, due perfot rot ke automaton .sndior analysis ir ard tin ru cs of the ir ade and a se, 'It

3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone], Toll Free: (888)2634686, Fax. [phone]
[e-mail], weh: www.awal-lahs.coni
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Analyte
Lab Sample ID: MB-54502
Test Code 8270-W-3511
Result
Date Analyzed
Date Prepared
Units
03/09/2018
03/08/2018
Reporting
Method MDL Limit
1427h
1233h
Amount Spike Ref. Spiked Amount %REC RPD Ref. RPD Limits Amt % RPD Limit Qual
Surr 2,4,6-Tribromophenol 53 0 ug/L SW8270D 50 00 106 10 - 227
Surr 2-Fluorob iphenyl 30 5 ug/L SW8270D 25 00 122 23 - 145
Surr 2-Fluorophenol 31 1 PLO- SW8270D 50 00 62 2 10 - 110
Surr Nitrobenzene-d5 32 5 ug/L SW8270D 25 00 130 39 - 174
Surr Phenol-d6 24 1 ug/L SW8270D 50 00 48 2 10 - 100
Surr Terphenyl-d14 32 0 ug/L SW8270D 25 00 128 30 - 199
Report Date 3/27/2018 Page 75 of 87 All analyses applmable to die CWA, SDW A, and R.0 RA sre per formai. in ,.,ccard.rice o Nl.l.A( protocols Pertinent saiwling animation Pi located on the attached COC Cardidentird Business lamination this report rs provided fix the uxclusive use ul tin- addressee Privileges of suhsogracnt Ilse of the Mine 01 tiUs rorripany Or aAv mem hE of Its stlff.c,r reprontoetton of th.,, report In cOnncorl on wall the ads et trs011M, promOtIN1 Or sale- rvi a,1)! vr od uer procCss. or In cOnneetion with tile I e-pubhettucte atilt, report Frvr an'y purpose ether fhar for the addl rsves i1i br ',anted Orli, Orr ,ontaut fliis comurany accertaiiinsibilitago- the AM, arliiirsts rrr lir and jilt, the rol- 0' the trade timeht -t NM OM NM NM MI UM MI 1111111
1111111 111111 61111 1111. 111.1 101111 IN 1111111 1121111 OM ON Ma OM UM 3440 South 700 Vi est
Salt Lake City. UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone], Fax: [phone] Laboratory Director
[e-mail], web: www.awal-labs.com Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: MS
Analyte
Lab Sample ID: 1803136-005IMS
Test Code 8270-W-3511
Result
Date Analyzed
Date Prepared
Units
03/09/2018
03/08/2018
Method
1640h
1233h
MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC
RPD Ref. RPD
Limits Amt % RPD Limit Qual
2,4,6-Triehlorophenol 78 1 pg/L SW82700 2 78 9 76 97 58 0 80 1 14 - 191
2,4-Dimethylphenol 90 6 ug/L SW8270D 4 51 9 76 97 58 0 92 8 50 - 1 32
2,4-Dinitrotoluene 107 ug/L SW82700 2 24 9 76 97 58 0 109 95 - 190
2-Chloronaphthalene 99 2 ug/L SW8270D 1 59 9 76 97 58 0 102 70 - 175
2-Chlorophenol 76 3 110- SW8270D 6 67 9 76 97 58 0 78 2 27 - 136
4,6-Dinitro-2-methylphenol 48 7 ug/L SW8270D 7 51 9 76 97 58 0 49 9 10 - 156
4-Chloro-3-methylphenol 78 9 ug/L 8W8270D 4 51 9 76 97 58 0 80 8 50 - 144
4-Nnrophenol 13 5 pg/L SW8270D 1 35 9 76 97 58 0 13 9 10 - SO
Acenaphthene 95 7 ug/L SW8270D 2 36 9 76 97 58 0 98 1 80 - 172
Benzo(a)pyrene 94 1 ug/L SW8270D 3 25 9 76 97 58 0 96 4 80 - 195
N-1Sitrosodi-n-propylamme 79 2 ug/L 8W8270D 6 28 9 76 97 58 0 81 2 20 - 180
Pentac hlorophenol 26 4 ug/L SW8270D 2 95 9 76 97 58 0 27 0 20 - 172
Phenol 45 1 pg/L SW8270D 1 19 9 76 97 58 0 46 3 10 - 80
Pyrene 95 7 ug/L SW8270D 2 90 9 76 97 58 0 98 1 81 - 179
Sum 2,4,6-Tribromophenol 43 2 ug/L SW8270D 48 79 88 6 10 - 310
Sun 2-Fluorobiphenyl 25 4 Mil- SW8270D 24 40 104 10 - 230
Surr 2-1- luorophenol 33 5 ug/L SW8270D 48 79 68 6 10 - 120
Surr Nitrobenzene-d5 28 4 ug/L 5W8270D 24 40 117 10 - 253
Surr Phenol-d6 25 6 ug/L SW8270D 48 79 52 5 10 - 110
Surr Terphenyl-d14 26 6 1-TriL SW8270D 24 40 109 10 - 255
Report Date 3/27/2018 Page 76 of 87
na I ”es applickle to the CWA, ,fl)NV A and RCR A are per formed in accordance to NI I.A( protocols Pertinent sampling information vs located on the atuehed OC ( ondidential liminess Information I his !cowl Is ovidod for the ocuusiye use of the addrecsee Priv tlegec of subsequent use of the
oady at tars company or any Incrnbcr arts staf I. or reproductron th.s report in ronnectron vadi the a..fsurtisornent promotton or rale of a ry product or proorss. or in connection "nth rrrc re-pablicatron of thus report tor am purpose .3ther than for the addressee will he aranted only on contret I his
o MI, 1" accepts no respersasihtv except fey- tn,. due rerfoirmut.c irspeelion andire nral ors tr. stoocl fear' i turd ACI tn, the rides of the uncle and ‘t svence
3440 South 700 West
Salt Lake City, U f 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
awalwal-labs.eom, web: www.aml-lahs.com
QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: MSD
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Analyte
Lab Sample ID: 1803136-005IMSD
Test Code 8270-W-3511
Result
Date Analyzed
Date Prepared
Units
03/09/2018
03/08/2018
Method
1703h
1233h
2,4,6-Triehlorophenol 79 9 ug/L SW8270D
2,4-Dimethylphenol 94 3 141- SW8270D
2,4-Dmitrotoluene 114 µWI_ SW8270D
2-Chloronaphthalene 103 ug/L SW8270D
2-Chlorophenol 75 4 ug/L SW8270D
4,6-Dautro-2-methylphenol 76 9 ug/L SW8270D
4-Chloro-3-methylphenol 82 5 pg/L SW8270D
4-Nhtrophenol 14 2 µg/L SW8270D
Acenaphthene 101 ug& SW8270D
Benzo(a)pyrene 99 8 µg/L SW8270D
N-Nlitrosodt-n-propylamine 96 0 tig/L SW8270D
Pentachlorophenol 34 1 µg/L SW8270D
Phenol 48 2 ug/L SW8270D
Pyrene 104 ttg/L SW8270D
Surr 2,4,6-Tribrornophenol 4 l 4 ttg/L 5W8270D
Surr 2-Fluorobiphenyl 25 1 ug/L 5W8270D
Surr 2-Fluorophenol 30 7 ug/L SW8270D
Surr Nitrobenzene-d5 27 3 ug/L SW8270D
Surr Phenol-d6 25 9 ttg/L SW8270D
Surr Terphenyl-d14 27 5 ug/L SW 8270D
@ - High RPD due to suspected sample non-homogeneity or matrix interference
Reporting Amount Spike Ref. RPD Ref. RPD
MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qua!
9 71 97 11 0 2 77 82 3 14 - 191 78 1 2 19 25
4 49 9 71 97 11 0 97 1 50 - 132 90 6 3 99 25
2 23 9 71 97 11 0 118 95 - 190 107 6 85 25
1 58 9 71 97 11 0 106 70 - 175 99 2 3 43 25
6 64 9 71 97 11 0 77 6 27 - 136 76 3 1 29 25
7 48 9 71 97 11 0 79 2 10-156 48 7 44 9 25
4 49 9 71 97 11 0 85 0 50 - 144 78 9 4 50 25
1 34 9 71 97 11 0 14 6 10 - 80 13 5 4 50 25
2 35 9 71 97 11 0 104 80 - 172 95 7 4 90 25
3 23 9 71 97 11 0 103 80 - 195 94 1 5 90 25
6 25 9 71 97 1 l 0 98 9 20 - 180 79 2 19 2 25
2 93 9 71 97 11 0 35 1 20 - 172 26 4 25 6 25
1 18 9 71 97 11 0 49 6 10 - 80 45 1 6 46 25
2 88 9 71 97 11 0 107 81 - 179 95 7 7 94 25
48 56 85 3 10 -310
24 28 103 10 - 230
48 56 63 1 10 - 120
24 28 112 10 - 253
48 56 53 4 10 - 110
24 28 113 10 - 255
Report Date 3/27/2018 Page 77 of 87
A II analyscs appbcable to the CWA, SDWA, and 8( Itik are 1)u:1%i-riled in at-um-dance to motocols Po[nnent gunpfing man mahon IN loCalCd on the amiched OC or.lidelha I BUS IlezIS Information Fins epon 1.1()V OW (of ihe CKCALlilye oi ir.i. sddleSsee PTIYIlegc, NIIIISIAILIETIt LINE. of Ihe male of Ons comp% or am: int mticr of as staff or reproduction of this report in col-if-locum with *he a/sort:sumer& preinctioo or sole, of sm otoduct or process, or in connection with the ie-pubiaintrini antis report for iny purposo othdr than ton the itclri,s.t.e will hc urantEd Di& or sontas T cajacceptaiinsibIkv eve for the. due nor':um:1,e irt'insneetion gnarl ins in 000d faith and iii,crdine tile rules ihd trade ind velem,.
1.1.11111.111101111111.11. ale IMO 111111111.11MIMIlif
1111111 11111111 Iffin 111.1 MI MO MI IIIIII 3440 South 700 W est
Salt Lake City. IJT 84119 Kyle F. Gross
Phone: [phone], Toll Free: (888t 263-8686, Fax: [phone] Laboratory Director
e-mail: awal(i0wal-labs.corn, vveb: www awal-lahs.com
Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: LCS
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: LCS-54502
Test Code 8270-W-SIM-3511

Date Analyzed
Date Prepared
03/19/2018 1554h
03/08/2018 1233h

Benzo(a)pyrene 125 ilg/L SW82701) 2 00 2 00 100 0 0 125 10 - 140
Report Date 3/27/2018 Page 78 of 87 Au analyses applicable to the CWA qDWA, and RA RA arc pet formed in accordance to NI.L.A( molts:tat% Penmeni sampling mformation is located in the attached ( Curilidential Business lnfunnithon rim tepott ts pi otthIcd tor „he exclusive use of rho t.drh emee Privileges of subsequve use of the
name of this company or any member of Its stall or reproliction of this report in connection with the Ethernsement, pro notion or sale of any pt oduct ar pi ocess, or in connection with the le-publication of this report tor ae purpose othet than for the addiessee will be granted on4 on contact This
company accepts no responsibility e cent for the dae =frit mike of inspection and/or anal ir trocia Olin and .iceordi no. NI the rtiLas ti'tc track, ard 3,-enec
3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone], Toll Free: [phone], Fax. [phone]'7
awalgawal-labs.com, web: www.awal-lahs.corn
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Reporting Amount Spike Ref. RPD Ref. RPD Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: MB-54502 Date Analyzed 03/19/2018 1532h
Test Code 8270-W-SIM-3511 Date Prepared 03/08/2018 1233h
Benzo(a)pyrene < 0 100 pg/L SW8270D 0 100 0 100
Bis(2-ethylhexyl) phthalate 1 51 ligli- 5W8270D 0 100 0 100
Hexachlorobenzene < 1 00 ptg/L 8W8270D I 00 1 00
Pentaehlorophenol < 1 00 lig/L SW8270D 1 00 1 00
B - Bts(2-ethylhexyl)phthalate was present in the method blank at I 51 pg/L Levels of this compound at this concentratton is a common contamtnant and expected
Report Date 3/27/2018 Page 79 of 87
All anslyses rippl table to the CWA, SDWA, and R( RA arc per turned in ra.,cordance to NI I A( protocols Pertinent sampling informal un 19 loeatcd on the artsched ('OC ( onfidenticil Rosiness Informatron Mrs report is pro‘idcd for the esclucive use uf thc addressee Privileges o.'suirsequent lige of the name of this company or arre trernbcr of as staff_ or reproduction of flu, repo] in COTITIceti on with the cich,ensCIMIlt, prornotn co or sale 01 fc oduct or poi", Or In epic-in...too witkOlse c-pubhcation thr.•epori for In), purpose other thar for tho addicsAt nrantca only on ..ontaLt Ihrs co coarp, accep:, ill nipice 11$1,eCtlirl ilia ir iod t nth and c nrdond thc nth:, of th, tradt cnd f sPidn,
11111 Milli MO Sail OM MI MS WIWI MIN ONO NM NIB 11111
11111 1111111 0111 1111111 111110 IIIIIII 1111.1 1111111 011. Ma WI 3440 South 700 West
Salt Lake City. UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-lahs.com
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: MS
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDI, Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: 1803136-005IMS Date Analyzed 03/19/2018 I 745h
Test Code 8270-W-SIM-3511 Date Prepared 03/08/2018 1233h
Benzo(a)pyrene 166 ng/L SW8270D 1 95 1 95 97 58 0 170 15 - 169
' - Matrix spike recovery indicates matrix interference The method is in control as indicated by the LCS.
Report Date 3/27/2018 Page 80 of 87
All analyses applicable lo he CW A , SDWA and 0.( RA are per formed in taco-dance ar Nl.LAX pioloeols Pei intent inmpling mloonation is Mealed on the onaehed ( ( onlidemial Busine,s Information [his !port IS oc-dod for the exclusive use ol thc sildiessee Privilege, esuhsequemt use of the
name ot this company or a ty r of its stall or reproduction c: rep( n in connection with the a,lserilsement, promotiot or sale of any in oduct or pi ozess, or in connection vath the ic-pubneat.on of this report tor any purpose othei than for the addresike volt be granted only on eonteet {his
comninly accepts no respons esceM for thc dae ncrfoinianze inspection and/or ai alrsis ie yood fc lea and ace 31 dim! to the rules of Me trade mit of science
3440 South 700 West
Salt Lake City. (JT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-lahs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1 803 13 6 Dept: MSSV
Project: Payson City Landfill / 60544100.4 QC Type: MSD
Reporting Amount Spike Ref. RPD Ref. RPD Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample ID: 1803136-005IMSD Date Analyzed 03/19/2018 1807h
Test Code 8270- W-SIM-3511 Date Prepared 03/08/2018 1233h
Benzo(a)pyrene 142 ng/L SW8270D I 94 1 94 97 11 0 146 15 - 169 166 15 6 25
Report Date 3/27/2018 Page 81 of 87 All analyseu applicable lu the CWA, SDWA, and lt( RA are performed in acuordanee to NIA AC. protocols ['aliment oampling .nlni matron is locatcd on the stitched OC onlidennal Rosiness Informarron I hes 14:port is in osoled for the ext.larriye !sae ul the add. essee Privileges of subscquere use oP the la.nc ot thts compan or any member of Its staff_ or reprodr rayon of tins report m ednnectr on with the ads ernsement, prornotron or sale ot any r, oduct or pt ocess, or in c onnemon wrt the re-publicaboo of this report tor sP). porpos,; dther than tor the addressee will be yranted only or, cont<ret This compare,' accepts no respor s hr !Iry edcept for the air mame a'nspectron ard'or antlicsis nood forth and accordinu tO fire ra es of the track' and cf actcnce MN MB 111111-1111111-111111-11•11111111111111-11111111-1111111111111
111111 an an 111111 1111111 111111 On Alla an 011 3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Frs:c: [phone], Fax • [phone] I aboratory Director
e-mail: awal(tiOwal-labs.com, web: www.awal-lahs.com
Jose Rocha
QA Officer
QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSVOA
Project: Payson City Landfill / 60544100.4 QC Type: LCS
Analyte
Lab Sample ID: LCS VOC-1 030818A
Test Code 8260-W
Result
Date Analyzed
Units
03/08/2018
Method
801h
MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC
RPD Ref. RPD
Limits Amt % RPD Limit Qual
1,1,1-Trtchloroethane 22 0 ng/L SW8260C 0 264 2 00 20 00 0 110 73 - 139
1,1-Dichloroethene 23 2 41- SW8260C 0 263 2 00 20 00 0 116 37 - 144
1,2-Dichlorobenzene 20 8 µg/L SW8260C' 0 259 2 00 20 00 0 104 70 - 130
1,2-Dichloroethane 19 5 ng,./1_, 5W8260C 0 245 2 00 20 00 0 97 4 76 - 132
1,2-D ichloropropane 21 1 1-10- SW8260C 0 226 2 00 20 00 0 105 81 - 121
Benzene 21 8 lie, SW8260C 0 257 2 00 20 00 0 109 82 - 132
Chlorobenzene 21 0 ng/L SW8260C 1 99 2 00 20 00 0 105 74 - 126
Chloroform 21 1 ng/L SW8260C 0 320 2 00 20 00 0 106 85 - 124
Ethylbenzene 21 9 ng/L sW8260C 0 281 2 00 20 00 0 110 67 - 118
Methylene chloride 20 9 ng/L SW8260C 0 372 2 00 20 00 0 104 71 - 135
Naphthalene 18 7 ng/L SW8260C 0 479 2 00 20 00 0 93 4 63 - 129
Toluene 21 6 ng/L SW8260C 0 248 2 00 20 00 0 108 69 - 129
Trichloroethene 20 3 ng/L SW8260C 0 248 2 00 20 00 0 102 75 - 136
Xylenes, Total 67 1 ng/L SW8260C 0 720 2 00 60 00 0 112 66 - 124
Surr 1,2-Dichloroethane-d4 49 6 ng/L S W 8260C 50 00 99 1 80 - 136
Surr 4-Bromotluorobenzene 50 4 pg/L SW8260C 50 00 101 85 - 121
Surr Di bromotluoromethane 57 2 µWI,. SW8260C 50 00 114 78 - 132
Surr Toluene-d8 50 5 ng/L SW8260C 50 00 101 81 - 123
Report Date 3/27/2018 Page 82 of 87
All analyses applicable to the CWA, '411W A, and RCRA are pei formed in accordance .o pr ()week. Pertinent sampling infra mat on is located on the attached ( OC Coniidenlial Rusine,s Information 'This I epoit i piosidud for the exciusiee uae uf the ack'temee Priv lege,, of subsi..quent use of the
name of this company or anv member oîits stall or reproduction of ths repon in connection with the ads enisement promotion or sale of arn vroduct in pi ocess, or in correction with the lc-publication of this report tor any piirpose othoi than tor the addies,ec will be pranted only or. contact This
company accepts 50 iespons bola,/ escept for no duc nerfoim; e of irvection imam- anaNsi, in .11.1e1 taith ind cc, od no tit hi. fri.`c ti-e irwk rod: f sci.
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail. awal@av‘al-labs.com, v‘eb: www.awal-lahs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer QC SUMMARY REPORT
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSVOA
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt % RPD Limit Qual
Lab Sample Ill: MB VOC-1 030818A
Test Code 8260-W
Date Analyzed 03/08/2018 840h
I , 1,1,2-Tetrachloroethane < 2 00 pg/L SW8260C 0 272 2 00
1,1,1-Trichloroethane < 2 00 ag/L SW8260C 0 264 2 00
I ,1,2,2-Tetrachloroethane <2 00 pg/L SW8260C 0 291 2 00
I ,1,2-Trichloroethane < 2 00 tig/L SW8260C 0 463 2 00
1,1-Dichloroethane < 2 00 ttg/L SW8260C 0 474 2 00
1,1-Dichloroethene < 2 00 ug/L SW8260C 0 263 2 00
1, I -Dichloropropene < 2 00 ttg/L SW8260C 0 269 2 00
1,2,3-Trichloropropane < 2 00 tig/L SW8260C 0 407 2 00
1,2,4-Trichlorobenzene < 2 00 ti.g/L SW8260C 0 318 2 00
1,2-Di b rorn o-3-ch loropropane < 5 00 ti.g/L SW8260C 0 442 5 00
1,2-Di b rorn oethan e < 2 00 110- SW8260C 0 288 2 00
1,2-Dichlorobenzene < 2 00 itg/L SW8260C 0 259 2 00
1,2-Dichloroethane < 2 00 tig/L SW8260C 0 245 2 00
1,2-Dichloropropane < 2 00 ti.g/L SW8260C 0 226 2 00
1,3-Dichlorobenzene <2 00 µg/L SW8260C 0 332 2 00
1,3-Dichloropropane < 2 00 ttg/L 5W8260C 0 316 2 00
1,4-Dichlorobenzene < 2 00 ug/L SW8260C 0 329 2 00
2,2-Dichloropropane < 2 00 ttg/L SW8260C 0 286 2 00
2-Butanone < 10 0 ti.WL SW8260C l 05 10 0
2-Hexanone < 5 00 ttg/L. 5W8260C 0 318 5 00
4-Methy1-2-pentanone < 5 00 ttg/L 5W8260C 0 881 5 00
Acetone < 10 0 ag/L 5W8260C 1 70 10 0
Acetonarile < 5 00 pg/L SW8260C 3 38 5 00
Acrolein < 5 00 pg/L SW8260C 1 63 5 00
Acrylonitrile < 10 0 pg/L 5W8260C 1 06 10 0
Allyl chloride < 5 00 110- 5W8260C 1 73 5 00
Benzene <2 00 PO- SW8260C 0 257 2 00
Report Date 3/27/2018 Page 83 of 87
All analysts spplikstble to the OVA NDW snd RC R sre petformed kn ac,cotclanee to NIA AC otoeols Pet tment sampling Infoimation tk.. I oedled on ihe sttached COC onlideotial liminess lnformution this leper( lb Nos sled tor the MAO:Ave use id the addiessee Pr lieges of subsequent &se of the
name of tins company or any .nernher of' as staff_ or reproduction of this report tn connecuon svtds the ad vermernent promotion or sale of any ploduct la ocass, ur In comodrt io voth the e-publient on of this report for any purpose dthee thdr for th, act,tres.te wil s oranted unh ,„n eontdct t his abacceptsiminsIblifiltor jjjjj sts fad]] and a u ce ',Th° to Ore ruu?s of the trade aliens e. MINI INK MI MI MI ON
Client: AECOM
Lab Set ID: 1 80313 6
Project: Payson City Landfill / 60544100.4
11111 alle AM 11111 4111111 OM 111641
3440 South 700 West
Salt Lake city, UT 84119 Kyle F. Gross
Phone: [phone], Tull Free: [phone], Fax: [phone]
Laboratory Director
e-mail: awal*wal-labs.eom, web: www.awal-labs.com
Jose Rocha
QA Officer
_QC SUMMARY REPORT
Contact: Lawrence Cannon
Dept: MSVOA
QC Type: MBLK
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDI, Limit Spiked Amount %REC Limits Amt % RPD Limit Qua!
Lab Sample ID: MB VOC-1 030818A
I est Code 8260-W
Date Analyzed 03/08/2018 840h
Bromochloromethane < 2 00 !AWL SW8260C I 64 2 00
Bromodichloromethane < 2 00 ug/L SW8260C 0 239 2 00
Brornoform < 2 00 lig11-, SW8260C 0 212 2 00
Bromomethane < 5 00 ug/L SW8260c 2 23 5 00
Carbon disulfide < 2 00 Itg/L SW8260C 0 292 2 00
Carbon tetrachloride < 2 00 ug/L SW8260C 0 217 2 00
Chlorobenzene < 2 00 ug/L SW8260C 1 99 2 00
Chloroethane < 2 00 µg/L SW8260C 1 86 2 00
Chloroform <2 00 itg/L SW8260C 0 320 2 00
Chloromethane <3 00 ug/L SW8260C 0 681 3 00
Chloroprene < 2 00 ug/L SW 8260C 0 540 2 00
cis-1,2-Dichloroethene < 2 00 ug/L SW8260C 0 288 2 00
cis-1,3-Dichloropropene < 2 00 ug/L SW8260C 0 239 2 00
Dibromochloromethane < 2 00 ug/L SW8260C 0 355 2 00
Dibromomethane < 2 00 ug/L SW8260C 0 260 2 00
Dichlorodifluoromethane < 2 00 ug/L SW8260C 0 269 2 00
Ethyl methacrylate < 2 00 ug/L SW 8260C 0 240 2 00
Ethyl benzene < 2 00 ug/L SW8260C 0 281 2 00
lodomethane < 5 00 ug/L SW8260C 0 911 5 00
Isobutyl alcohol < 100 ug/L SW8260C 13 5 100
Methacrylonitrile <5 00 p.WL SW8260C 0 866 5 00
Methyl rnethacrylate <5 00 ug/L 5W8260C 0 279 5 00
Methylene chloride < 2 00 µg/L SW8260C 0 372 2 00
Naphthalene < 2 00 µg/L SW8260C 0 479 2 00
Propionitrile < 25 0 ug,/ SW8260C 9 40 25 0
Styrene < 2 00 1-10, 5W8260C 0 253 2 00
Tetrachloroethene < 2 00 llgil- SW8260C 0 262 2 00
Report Date 3/27/2018 Page 84 of 87
All analyses epplu—thle to rite (IN, A, qfPNA and leCRA dre pet formcd tn aetaedance .o Nl't At. pi utueols Psi.tient sampling mPuoratiun i. Irvated on the attrtelied COC ( ottitde'iiial l3usiriess Inrbmir.trori This iepurl is rtroaRkd for the lraiu.ive use of the addie‘see Privileges of subsuit.ei it use of the
name of this company or any member or- its stall. or reproduction ol th.s repo] t in connection with the ad am tisoment. promot c,ii ur sale of a.iy product or process or in conneetIon with the re-publ icatia.1 of this toport tor any purpose otho than for the addiessec wet be granted onl) on contact Ihis
compoily accepc. no responsibility eseent for th, doe pertb nlaee Inver lion arid/or analysis ir good feel', and .ird ne to -nes traae and ot rClt. rr
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: (888 ) 263-8686. Fax• [phone]
e-mail: awaNawal-labs.com, web: www.awal-lahs.corn
QC SUMMARY REPORT
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSVOA
Project: Payson City Landfill / 60544100.4 QC Type: MBLK
Analyte
Lab Sample ID: MB VOC-1 030818A
Test Code 8260-W
Result
Date Analyzed
Units
03/08/2018
Method
840h
MDL
Reporting
Limit

Amount Spike Ref.

Spiked Amount %REC
RPD Ref. RPD
Limits Amt % RPD Limit Qual
Toluene < 2 00 ug/L SW8260C 0 248 2 00
trans-1,2-Dichloroethene < 2 00 ug/L 5W8260C 0 828 2 00
trans-1,3-Dichloropropene < 2 00 µg/L SW8260C 0 255 2 00
trans- I ,4-Dichloro-2-butene < 2 00 ug/L SW8260C 0 656 2 00
Trichloroethene < 2 00 1-1-0- SW8260C 0 248 2 00
Trichlorotluoromethane < 2 00 ug/L 5W8260C 0 459 2 00
Vinyl acetate < 10 0 ug/L 5W8260C 0 787 10 0
Vinyl chloride < 1 00 ug/L SW8260C 0 265 1 00
Xylenes, Total < 2 00 ug/L SW8260C 0 720 2 00
Surr 1,2-Dichloroethane-d4 SO 9 pig/L SW8260C 50 00 102 80 - 136
Surr 4-Bromaluorobenzene 51 3 ug/L SWR260C 50 00 103 85 - 121
Surr Dibromotluoromethane 56 0 ug/L 5W8260C 50 00 112 78 - 132
Surr Toluene-d8 51 1 µg/L 5 W8260C 50 00 102 81 - 123
Report Date 3/27/2018 Page 85 of 87
All analyses appluAble to the CW A, SOW A, and RC RA ere pei formed "I moot-do-Nu to NUM. pi otocols Poilinert sampling info illation is [waled on the attache(' c OC ( ordideithal Rumness Information this iepori is pi os kled far Ole cscluaive uae ol the addiessee Prix lieges of suhsuptent Lek ache name of this company or any 1T1Crn be, o' as staff. or reprolianon of the; report in concealer with the ad, et-cam-tem promotion or sale of ails cioduct or process, or tn coneution titath the re-pubhent on of this ropert For ars purpose alto than for thr adifit ssott br ttrairnd onls ,MQLA VHS
citiaccentsaiinsrbOrnimitor stilton srs rn arid art, roo rir itir mie, irair ap MI MIN MI NIP 01111111-41111111 MP
111111 11.0 Iling 111111 11.11 3440 South 700 est
Salt Lake City. UT 84119 Kyle F. Gross
Phone. [phone], Toll Free: [phone]. Fax. [phone] Laboratory Director
e-mail: awalgawal-labs.com, web: www.awal-ltMs.com
Jose Rocha
QA Officer QC SUMMARY REPORT 61 •
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1 803 136 Dept: MSVOA
Project: Payson City Landfill / 60544100.4 QC Type: MS
Result
Date Analyzed
Units
03/08/2018
Method
1040h
MDL
Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC
RPD Ref. RPD Limits Amt % RPD Limit Qual
20 0 pg/L SW8260C 0 264 2 00 20 00 0 100 67 - 147
20 6 pg/L SW8260C 0 263 2 00 20 00 0 103 51 - 152
18 1 ug/L SW8260C 0 259 2 00 20 00 0 90 7 70 - 130
17 7 ug/L SW8260C 0 245 2 00 20 00 0 88 5 39 - 162
18 8 ug/L SW8260C 0 226 2 00 20 00 0 93 8 59 - 135
19 5 ug/L SW8260C 0 257 2 00 20 00 0 97 3 66 - 145
18 9 ug/L SW8260C 1 99 2 00 20 00 0 94 6 63 - 140
18 9 ug/L 5 W8260C 0 320 2 00 20 00 0 94 7 50 - 146
19 3 ug/L SW8260C 0 281 2 00 20 00 0 96 4 69 - 133
19 0 ug/L SW8260C 0 372 2 00 20 00 0 94 8 30 - 192
16 7 pg/L 3W8260C 0 479 2 00 20 00 0 83 6 41 - 131
19 5 ug/L SW8260C 0 248 2 00 20 00 0 97 6 18 - 192
17 9 ugiL SW8260C 0 248 2 00 20 00 0 89 4 61 - 153
58 8 pg/L SW8260C 0 720 2 00 60 00 0 98 0 42 - 167
50 8 ug/L SW8260C 50 00 102 72 - 151
50 5 ug/L SW8260C 50 00 101 80 - 152
61 0 ug/L SW8260C 50 00 122 72 - 135
51 3 ug/L SW8260C 50 00 103 80 - 124
Analyte
Lab Sample ID: 1803136-005AMS
Test Code 8260-W
1,1,1- Triehlo roethan e
1,1- D ichloroethene
1,2-Dichlorobenzene
1,2-Dichloroethane
1,2-Dichloropropane
Benzene
Chlorobenzene
Chloroform
Ethylbenzene
Methylene chloride
Naphthalene
Toluene
Trichloroethene
Xylenes, Total
Surr 1,2-Dichloroethane-d4
Surr 4-Brornal uorobenzene
Surr Dibrornofluorornethane
Surr Toluene-d8
Report date 3/27/2018 Page 86 of 87
All analyses applicable to the CWA, SDWA and KIR A are per formed in accordance ro Nl protocols Pertinent sampling +promotion is located on the attached (OC Confidential ltus+ne.s intbrinction his report is trios hied for .he exclucive use of too addressee Privileges of suhsequent use of the
name of this company or any member of its staff_ or repicy.hicrion of this report in connection with the advertisement, promotion or sale or any product or process or in c onreetion Y.rtli the re-publieabon of this report tor any purpose otbei than t'or the addiev.ec will be so-anted oply on contact I his
c moony accepts no rc'.,rrshiliry e. cent to, the due perrinmanze in‘pection cold:or analysis re good faith and accei &no lo tit, rules the t+ acle and of se e+ I
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Fre: [phone], Fax; [phone]
c-mail: awal(ifAmal-labs.corn, web: www.awal-lahs.com
QC SUMMARY REPORT
Kyle F. Gross
laboratory Director
lose Rocha
QA Officer
Client: AECOM Contact: Lawrence Cannon
Lab Set ID: 1803136 Dept: MSVOA
Project: Payson City Landfill / 60544100.4 QC Type: MSD
Analyte Result Units Method MDL Reporting
Limit
Amount
Spiked
Spike Ref.
Amount %REC Limits
RPD Ref.
Amt % RPD
RPD
Limit Qual
Lab Sample ID: 1803136-005AMSD Date Analyzed 03/08/2018 1101h
Test Code 8260-W
1,1,1-Trichloroethane 21 4 pg/L SW8260C 0 264 2 00 20 00 0 107 67 - 147 20 6 95 25
1,1-D ichl oroethene 22 3 ug/L SW8260C 0 263 2 00 20 00 0 111 5 l - 152 20 6 8 03 25
1,2-Dichlorobenzene 19 8 ug/L SW8260C 0 259 2 00 20 00 0 98 8 70 - 130 18 1 8 50 25
1,2-Dichloroethane 19 2 ug/L SW8260C 0 245 2 00 20 00 0 96 0 39 - 162 17 7 8 OS 25
1,2-Dichloropropane 20 2 ug/L SW8260C 0 226 2 00 20 00 0 101 59 - 135 18 8 7 24 25
Benzene 21 1 Piga- S W826(/C 0 257 2 00 20 00 0 106 66 - 145 19 5 8 18 25
Chlorobenzene 20 0 ug/L SW8260C 1 99 2 00 20 00 0 99 8 63 - 140 18 9 5 35 25
Chloroform 20 3 ug/L SW8260C 0 320 2 00 20 00 0 102 50 - 146 18 9 7 03 25
Ethylbenzene 20 6 ug/L SW8260C 0 281 2 00 20 00 0 103 69 - 133 19 3 6 38 25
Methylene chloride 20 4 ug/L 5 W8260C 0 372 2 00 20 00 0 102 30 - 192 19 7 17 25
Naphthalene 18 6 ug/L SW8260C 0 479 2 00 20 00 0 93 0 41 - 131 16 7 10 6 25
Toluene 21 0 ug/L SW8260C 0 248 2 00 20 00 0 105 18 - 192 19 5 7 45 25
Trichloroethene 19 1 ug/L SW8260C 0 248 2 00 20 00 0 95 4 61 - 153 17 9 6 44 25
Xylenes, Total 62 8 ug/L 5W8260C 0 720 2 00 60 00 0 105 42 - 167 58 8 6 60 25
Surr 1,2-Dichloroethane-d4 50 9 ug/L 5W8260C 50 00 102 72 - 151
Surr 4-Bromofluorobenzene 50 2 PO- SW8260C 50 00 100 80 - 152
Surr Dibromofluoromethane 59 0 pg/L 5 W8260C 50 00 118 72 - 135
Surr Toluene-d8 50 4 pg/L 5W8260C 50 00 101 80 - 124
Report Date 3/27/2018 Page 87 of 87 it analyscs applica)le to the OVA, ,:DWA, awl RCR A are pei formed in accordance to NIA A( r, olovois RN tment sampling information is localcd un Me attached COC Confidonial twaness Information -I his ieport provided for the tmlunive use of the addressee Privilege, of subsequcw Me of the name of this comparw adr member of as stall or reproduction of this report in a donecn on with the ads iisernent promotion or sale ot any in o‘incit or Is ocess, or trt conneetw w i tt ith the re-pubb o eatio of this Itiport for olly pd mit rpnse er tisar for the add, es_ee will be granted onl‘ on yonim t oar" acceptiminsibilitioNfor Orr n eilist109 aijjjjssis ir will and acifilo the r leialie trade lid toindin ìiï 1111. OM MN US 11111. MN MI MA
MI NS SIN MI MO Ma NO MI ,SMO MUM—
American West Analytical Laboratories Rpt Emailed: UL
Generic Landfill
WORK ORDER Summary Work Order: 1803136 Page 1 of 4
Client: AECOM Due Date: 3/21/2018
Client 10: AEC100 Contact: Lawrence Cannon
Project: Payson City Landfill / 60544100.4 QC Level: II+ WO Type: Project
Comments: QC 2+. Use sample #5 for the MS/MSD. Payson City Landfill. CC results to Sheri Fling, Chris Howell and Allia. Use SIM analysis for SVOC, including bis(2-ethylhexyl)phthalate.;
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1803136-001A TB-030718 3/7/2018 3/7/2018 1446h 8260-W Aqueous VOCFridge 6
Test Group: 8260-W-12; # of Anaoltes: 63 / # of Surr: 4
1803136-002A MW-X 3/7/2018 0800h 3/7/2018 1446h 8260-W Aqueous
Test Group: 8260-W-X2; # of Analytes: 63 / # of Surr: 4
VOCFridge 3
1803136-002B 8011-NV hall edb
Test Group: 8011-W-EDB-DBCP; # of Analytes: 2 / # of Sum: 1

8011-W-PR hall - edb

1803136-002C 300.0-W
2 SEL Anabites: CL SO4
DF - wc 1
ALK-W-2320B DF - we
2 SEL Analytes: ALKB ALKC
NO3-W-353.2 DF -wc
P11-450011+B DF -wc
1803136-002D TDS-W-2540C ww - tds
1803136-002E TOC-W-5310B DF -too 3
1803136-002F N113-W-350.1 DF - nh3 I
N113-W-PR DF - sh3
1803136-002G COD-1IAC1I8000 ww - cod
1803136-00211 3005A-ICPMS-1'R MET/HG
6010D-W MET/He
7 SEL Analytes: CA FE MG K NA SN Y
6020B-W mET/HG • 15 SEL Analytes: SB AS BA BE CD CR CO CU PB MN NI SE AG TL ZN
HG-W-7470A mET/BG
HG-W-PR mEr/I1G
1803136-0021 3511-SVOA-PR 3

8270-W-3511
Test Group: 8270-W-351I-X2; # of Analytes: 108 / # of Surr: 6
8270-W-S1M-3511
Test Group: 8270-W-3511-X2 SIM; # of Analytes: 4 / # of Surr:
Printed: 03/07/18 16:38 LABORATORY CHECK %M RT EJ CN TAT D QC 0 LUO HoK HOK HOK COC Emailed
WORK ORDER Summary
Client: AECOM
Work Order: 1803136
Due Date: 3/21/2018
Page 2 of 4
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1803136-003A MW-5 3/7/2018 1000h 3/7/2018 1446h 8260-W Aqueous
Test Group: 8260-W-12; # of Anabdes: 63 / # of Surr: 4
VOCFridge 3
1803136-0038 8011-W
Test Group: 801I-W-EDB-DBCP; # of AnaOtes: 2 / # of Surr: 1
hall - edb
8011-W-PR ball - edb
1803136-003C 300.0-W
2 SEL Ana4;tes: CL SO4
DF- wc 1
ALK-W-2320B
2 SEL Analytes: ALKB ALKC
DF - we
NO3-W-353.2 DF - we
PH-450011+B DF -we
1803136-003D TDS-W-2540C viw - tds
1803136-003E TOC-W-531011 DF - toe 3
1803136-003F NH3-W-350.1 DF ch3
NH3-W-PR DF-A0
1803136-003G COD-HACH8000 ww - cod
1803136-0031-1 3005A-ICPMS-PR METIHG
6010D-W
7 SEL Anables: CA FE MG K NA SN V
MET/HG
6020B-W
15 SEL Analytes: SB AS BA BE CD CR CO CU PB MNNISEÅG TL ZN
MET/110
IIG-W-7470A MET/HG
IIG-W-PR MET/HG
1803136-0031 3511-SVOA-PR 3
8270-W-3511
Test Group: 8270-W-3511-12; # of Anabaes: 108 / # of Surr: 6
8270-W-Sa1-3511
Test Group: 8270-W-3511-X2 SIM; # of Analytes; 4 / # of Surr:
1803136-004A MW-6 3/7/2018 1115h 3/7/2018 1446h 8260-W Aqueous
Test Group: 8260-W-.70; # of Analytes: 63 / # of Surr: 4
VOCFridge 3
1803136-004B 8011-W
Test Group: 8011-W-EDB-DBCP; # of AnabAtes: 2 / # of Surr: 1
hall - edb
8011-W-PR hall - edb
1803136-004C 300.0-W
2 SEL Anabaes: CL SO4
DF-um 1
ALK-W-23208
2 SEL Analytes: ALKB ALKC
DF -wc
Printed: 03/07/18 16:38 LABORATORY CHECK %td RT 0 CN TAT ED QC LUO HOK HOK HOK COC Emailed
—11161.1 MIIMINI 1111111111— MI or
SIM ON OM NIB 111111 —1101— In
WORK ORDER Summary
Client: AECOM
Work Order: 1803136
Due Date: 3/21/2018
Page 3 of 4
I !
I !
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1803136-004C
1803136-004D
1803136-004E
I803136-004F
1803136-004G
1803136-004H
1803136-0041
1803136-005A
1803136-005B
1803136-005C
1803136-005D
1803136-005E
1803136-005F
1803136-005G
1803136-005H
MW-6 3/7/2018 1115h 3/7/2018 1446h NO3-W-353.2 Aqueous DF - wc 1
PH-4500H+B DF - wc
TDS-W-2540C ww - tds
TOC-W-5310B DF-toe 3
NH3-W-350.1 DF - nh3 i
NH3-W-PR DF -nh3
COD-HACH8000 ww - cod
3005A-ICPMS-PR MET/HG
6010D-W
7 SEL Analytes: CA FE MG K NA SN V
MET/HG
6020B-W
15 SEL Anables: SB AS BA BE CD CR CO CU PB MN NI SE AG 7L ZN
MET/HG
IIG-W-7470A MET/HG
HG-W-PR mET/HG
3511-SVOA-PR 3
8270-W-3511
Test Group: 8270-W-3511-X2; # of Analytes: 108 / # of Swr: 6
8270-W-SIM-3511
Test Group: 8270-W-3511-n SIM; # of Analytes: 4 / # of Surr:
MW-4 3/7/2018 1230h 3/7/2018 1446h 8260-W Aqueous
Test Group. 8260-IV-AZ # of Anables: 63 / # of Sum 4
VOCFridge 6
8011-W
Test Group; 8011-W-EDB-DBCP; # of Analytes: 2 / # of Surr: 1
hall - edb
8011-W-PH halt - cdb
300.0-W
2 SEL Analytes: CL SO4
DF - wc 1
ALK-W-2320B
2 SEL Analytes: ALKB ALKC
DF - wc
NO3-W-353.2 DF - we
PH-450011+B DF wc
TDS-W-2540C ww - tds 2
TOC-W-5310B DF - toe 6
NH3-W-350.1 DF - nh3 1
N113-W-114. DF-1113
COD-HAC118000 ww - cod
3005A-ICPMS-PR hilET/HG
Printd: 03/07/18 16:38 LABORATORY CHECK %M RT CN E TAT QC D LUO El HOK HOK HOK COG Emailed
WORK ORDER Summary Work Order. 1803136 Page 4 of 4
Client: AECOM Due Date: 3/21/2018
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1803136-00511 MW-4 3/7/2018 1230h 3/7/2018 1446h 6010D-W Aqueous NEET/HG 1
7 SEL Analytes: CA FE MG K NA SN V
6020B-W NEET/HG
15 SEL Analytes: SB AS BA BE CD CR CO CU PB MN NI SE AG
TL ZINT
HG-W-7470A MET/11G
HG-W-PR MET/11G
1803136-0051 3511-SVOA-PR 8

8270-W-3511
Test Group: 8270-W-3511-X2; # of Analytes: 108 / # of Surr: 6
8270-W-SIM-3511
Test Group: 8270-W-3511-X2 SIM; # tjAnaVes: 4 / # of Surr:
1803136-006A FR-030718 3/7/2018 1045h 3/7/2018 1446h 8260-W Aqueous VOCFridge 3
Test Group: 8260-W-X2; # of Anables: 63 / # of Surr: 4
Printed: 03/07/18 16:38 LABORATORY CHECK: %M RT LJ CN Ei TAT E QC 0 LUO HOK HOK HOK COC Emailed

SW Mt 1011 MIS-11•11 111111 MI
WIRS PAGE ! OF • i
4 611 11.,1/1 ecky- . Co-1
CHAIN OF CUSTODY/LABORATORY ANALYSIS REQUEST FORM
URS Corporation • 756 East Winchester Street, Suite 400, Salt Lake City, UT 84107 • 801-904-4000 • Fax [phone]
11 ¿I Date/Tune Date/Time at ime
I 377 S D,771.7/ir /4/e/(0
Cooler of Pink- sample management T.IPayson eityvauerteny Reports1Payscm COC.cloc 4111/08 2.1)0 PM White and Yellow to lab
L.-1U 1-111U tAILJ
Project Name: Payson City Landfill ProjectNiunber.
105144 ( O), 44 ANALYSIS REQUESTED
Project Manager: Report CC: PM -.144-P-orter 44,4411commr_ CA „teAce. Coevoc"
kaff-AuuterCkniseozP4011). e t sbeg-oleesearseorreent 9,fe. R...••4; Cti.'? 140 J>CAk . S' ion Project Location:
Payson City Landfill
6211 W 10400 S, Payson, UT 84651 ii I -oe e Y- 2
Phone #
801-904-4000 '
FAX #
801-904-4100
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U -- .- . S ler' s Signature amp Sampler's Printed Name o . 5 E g t - TR 'r, 7 4
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FIELD SAMPLE 0 . d 0 g 1 -A g t REMARKS
SAMPLE ID DATE MATRIX cij TIME 0 f: ,, P• c' V) 6 0.. 8 Po _J Z
11,- o4,01155 1,916 (ti_ ,,,,e1 DiT I. X
Mw-- X W'os 7730 ao 1-1. .?‹: )‹ -,)C X
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hyli„-i-k N4gb. ro,r-> c\t.3 X 31 X x x X X
p&-cppolit, 3/7A 1.E, 5- Za -2) )(
_ t - INVOICE INFORMATION Matrix Key: GW =. Ground Water SPECIAL INSTRUCTIONS/COMMENTS . General Chemistry: .
BILL TO: SW - Surface Water 0 = Other pH 45.00H+B Bicarbonate/Carbonate 2320B COD HACH 8000 TDS 160.1 Sulfate 300.0 Ammonia 350.1 Chloride URS CORPORATION 300.0 Nitrate 353.2 TOC 5310B Metals and Organics: See Payson City Landfill target analyte lists for metals, VOCs, SVOCs, PCBs, pesticides, and herbicides (on reverse side). SVOCs with low reporting limits will require 8270C SIM/3510C.
SAMPLE RECEIPT: CONDITION/COOLER TEMP: I. . :Z CUSTODY SEALS: Y 61 ,
' RELINQUISHED BY RECEIVED BY RELINQUISHED BY RECEIVED BY
Signature
7
Signa,1.4
1...._ - .1-' ------------71
Signature Signature
Prin e
l'i
•
• /44
A. C •-•, Printed Name
2 . "11
Printed Name . Printed Name
Pesticides SW 846 8081A/3510C •
Endosulfan II
Endosulfan sulfate
Endrin
Endrin aldehyde
a-BHC (lindane)
Hep hlor
Heptach epoxide
Methoxychlo
Toxaphene
'-DDD
4,4.-
4,4'-DDT
Aldrin
alpha-BHC
beta-BHC
Chlordane
delta-BHC
Dleldrin
Endosulfan 1
General Chemistry
pH (§ 25° C SM 45001-H-B
Ammonia (as N) EPA 350.1
Bicarbonate (As CaCO3) SM 2320B
Carbonate (As CaCO3) SM 2320B
Chloride EPA 300.0
COD HACH 8000
Nitrate (as N) EPA 353.2
Sulfate EPA 300.0
TDS EPA 160.1
TOC SM 5310B
Cyanide (optIonal) EPA 335.4
Sutfide (optional) SM 4500(S2-)B
Metals SW846 6010B/6020/7470A
Antimony Copper Selenium
Arsenic iron Silver
Barium Lead Sodium
Beryllium Magnesium Thallium
Cadmium Manganese Tin
Calcium Mercury (SW 7470A)
Chromium Nickel Vanadium
Cobalt Potassiurn Zinc
Hei'bicides SW 846 8151A
2,4, - 2,4-D
2,4,5-TP ( Dlnoseb
ces SW 846 8082/3510C

or 1016 Aroclor 1248
Aroclo 1 Aroclor 1254
Aroclor 12 1 Arocfor 1260
Aroclor 1242
VOCs SW 846 8260B/5030B SVOCs SW 846 8270C/3510C
1,1,1,2-Tetrachloroethane Chlorobenzene 1,2,4,5-Tetrachlorobenzene Acenaphthylene m-Dlnitrobenzene
1,1,1-Trichloroethane Chloroethane 1,4-Naphthoquinone . Acetophenone Methapyrilene
1,1,2,2-Tetrachloroethane Chloroform 1-Naphthylamine Anthracene Methyl nnethanesulfonate
1,1,2-TrIchloroethane Chloromethane 2,3,4,6-Tetrachlorophenol Benz(a)anthracene M9thyl patathion
1,1-Dichloro-1-propene Chloroprene 2,4,5-TrIchlorophenol Benzo(b)fluoranthene MethylchlPanthrene
1,1-Dichloroethane cls-1,2-Dichloroethene 2,4,6-Trichlorophenol Benzo(g,h,i)perylene Nitrobenzene-
1,1-Dichloroethene' cis-1,3-DIchloropropene 2,4-Dichlorophenol Benzo(k)fluoranthene N-Nitrosodiethylamine
1,2,3-Trichloropropane Dibromochloromethane 2,4-Dimethylphenol Benzyl alcohol N-Nitrosodimethylamine
1,2,4-Trichlorobenzene Dibromomethane 2,4-Dinitrophenol Bis(2-chloroethoxy)methane N-Nitroso-di-n-butylamine
1,2-Dichlorobenzene Dlchlorodifluoromethane 2,4-Dinitrotoluene Bis(2-chloroethyl)ether N-Nitrosodi-n-propylamine
1,2-Dichloroethane Ethyl methacrylate 2,6-Dichlorophenol Bis(2-chloroisopropyl)ether N-Nitrosodiphenylamine
1,2-Dichloropropane Ethylbenzene 2,6-Dinitrotoluene Butyl benzyl phthalate N-Nitrosomethylethylamine
1,3-Dichlorobenzene lodomethene 2-Acetylarninofluorene Chlorobenzilate N-Nitrosopiperidine
1,3-Dichloropropane isobutyl alcohol 2-Chloronaphthalene Chryserie N-Nitrosopyrrolidine
1,4-Dichlorobenzene Methacrylonitrile 2-Chlorophenol Diallate 0,0,0-Triethylphosphorothloate
2,2-Dichloropropane Methyl methacrylate 2-Methylnaphthalene Dibenz(a,h)anthracene o-Toluidine
2-Butanone Methylene chloride 2-Methylphenol Dibenzofuran Parathion
2-Hexanone Naphthalene 2-Naphthylamine Diethyl phthalate p-Dimethylaminoazobenzene
4-Methy1-2-pentanone Propionitrlle 2-Nitroaniline Dimethoate Pentachlorobenzene
Acetone Styrene 2-Nitrophenol Dimethyl phthalate Pentachloronitrobenzene
Acetonitrile Tetrachloroethene 3-Methylphenol Di-n-butyl phthalate Phenacetin
Acrolein Toluene 3,3"-Dichlorobenzidine Di-n-octyl phthalate Phenanthrene
Acrylonitrile trans-1,2-Dichloroethene 3,3*-Dimethylbenzidine Diphenylamine Phenol
Ally! chloride trans-1,3-Dichloropropene 3-Nitroaniline Disulfoton Phorate
Benzene trans-1,4-Dichloro-2-butene 4,6-Dinitro-2-methylphenol Ethyl methanesulfonate p-Phenylenediamine
Brornochloromethane Trichloroethene 4-Aminobiphenyl Famphur Pronamide
Brornodichloromethane TrIchlorofluoromethane 4-Btornophenyl phenyl ether ' Fluoranthene Pyrene
Bromoform Vinyl acetate 4-Chloro-3-methylphenol Fluorene Safrole
Bromomethane Vinyl chloride 4-Chloroaniline Hexachlorobutadiene Sym-TrInitrobenzene
Carbon disulfula Xylenes (Total) 4-Chlorophenyl phenyl ether Hexachlorocyclopentadiene Thlonazin
Carbon tetrachloride 4-Methylphenol Hexachloroethane
4-Nitroaniline Hexachioropropene SVOCs
DBCP & EDB EPA 5044 4-Nitrophenol Indeno(1,2,3-cd)pyrene SW 846 8270C SIM/3510C
1,2-Dibromo-3-chloropropane (DBCP) 5-Nitro-o-toluidine lsodrin Benzo(a)pyrene
1,2-Dibromoethane (EDB) 7,12-Dimethylbenz(a)anthrace lsophorone Bis(2-ethylhexyl)phthalate
a,a-Dimethylphenethylamine lsosafrole Hexachlorobenzene
Acenaphthene Kepone Pentachlorophenol
Notes:
Laboratory reporting limit must be at or below the Utah ground water protection standard (UGWPS) listed In R315-308.
COD = Chemical Oxygen Demand
TDS = Total Dissolved Solids
TOC = Total Organic Carbon
Target analyte list updated 4/11/2008
non rin rin r••••••••,
MI SW IMO OM 11N11-6111 111111 11111•11•11
Lab Set ID:
pit Lot #:
Preservation Check Sheet
Sam le Set Extension and nH
Analysis Preservative z a t( „5--
Ammonia pH <2 H2SO4 yel—y...., A r
COD pH -,2 H2SO4 1A4 As yin- 7V,..5
Cyanide pH >12 NaOH 7 -
Metals pH <2 IMO 3 ).7.e.0 Xe.-.5 pc-
NO2 &
NO3 pH <2 H2SO4
0 & G _pH <2 HCL
Phenols _pH <2 H2SO4
Sulfide pH >9 Na0H,
Zn Acetate , TKN pH <2 H2SO4
T PO4 pH <2 H2SO4
Procedure: 1) Pour a small amount of sample in the sample lid 2) Pour sample from lid gently over wide range pH paper 3) Do Not dip the pH paper in the sample bottle or lid 4) If sample is not preserved, properly list its extension and receiving pH in the appropriate column above 5) Flag COC, notify client if requested 6) Place client conversation on COC
7) Samples may be adjusted
Frequency: All samples requiring preservation
• The sample required additional preservative upon receipt.
• The sample was received unpreserved.
A The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
• The sample pH was unadjustable to a pH > due to the sample matrix interference.
Payson City Landfill
2017/2018 Monitoring Program Groundwater Monitoring Report
Fourth Quarter: March 2018
APPENDIX D
STATISTICAL ANALYSES INFORMATION
AECOM
Assessment Monitoring
Wells MW4, MW-5 and MW-6
IIIIIIIIII— MOM— —11111M1111-1111-1■111—
v.9.0.32 For the statistical analyses of ground water by URS Corporation only. UG
Parametric Confidence Interval
Compliance Limit is not exceeded. Per-well alpha = 0.01. Normality Test: Shapiro Wilk at Alpha = 0.01.
0.3
0.24
0.18
0.12
_i Z3) E 0.06
Limit = 0.1
•41;1141<sr
Constituent: Nickel Analysis Run 4/9/2018 3:16 PM
Facility: Payson City LF Client: Payson City Data File: PaysonMW456
Confidence Interval Page 1
Constituent: Nickel (mg/L) Analysis Run 4/9/2018 3:17 PM
Facility: Payson City LF Client: Payson City Data File: PaysonMW456
MW-4
6/15/2017 0.118
9/14/2017 0.102
12/12/2017 0.0634
3/7/2018 0.058
Mean 0.08535
Std. Dev. 0.02929
Upper Lim. 0.1518
Lower Lim. 0.01886
MN in WM— MO MI MN 111110 MI MI MB NM MI an ON OM NM MI
v.9.0.32 For the statistical analyses of ground water by URS Corporation only. UG
Parametric Confidence Interval
Compliance Limit is not exceeded. Per-well alpha = 0.01. Normality Test: Shapiro Wilk at Alpha = 0.01.
30
22
14
6
2
-10
Limit= 6
Constituent: Bis-2-ethylhexyl-phthalate Analysis Run 4/9/2018 3:24 PM
Facility: Payson City LF Client: Payson City Data File: PaysonMW456
Confidence Interval Page 1
Constituent: Bis-2-ethylhexyl-phthalate (ug/L) Analysis Run 4/9/2018 3:24 PM
Facility: Payson City LF Client: Payson City Data File: PaysonMW456
MW-5
6/15/2017 5.86
9/14/2017 10.2
12/12/2017 <3.97
3/7/2018 <7.38
Mean 5.434
Std. Dev. 3.551
Upper Lim. 13.5
Lower Lim. -2.629
MO NM NM MI In MO MN MI NM MI GM MN MI NM MO INS MI
v.9.0.32 For the statistical analyses of ground water by URS Corporation only. UG
Parametric Confidence Interval
Compliance Limit is not exceeded. Per-well alpha = 0.01. Normality Test: Shapiro Wilk at Alpha = 0.01.
0.3
0.22
0.14
0.06
—J Z3) E -0.02
-0.1
Limit - 0.1
'49ffik
Constituent: Chromium Analysis Run 4/9/2018 3:19 PM
Facility: Payson City LF Client: Payson City Data File: PaysonMW456
Confidence Interval Page 1
Constituent: Chromium (mg/L) Analysis Run 4/9/2018 3:19 PM
Facility: Payson City LF Client: Payson City Data File: PaysonMW456
MW-6
6/15/2017 0.00842
9/14/2017 0.00652
12/12/2017 0.108
3/7/2018 0.0543
Mean 0.04431
Std. Dev. 0.04786
Upper Lim. 0.153
Lower Lim. -0.06435
NM IONII NM MO MI MI In MB INS SNP MN MI MI 1.11 OM 8111.1 NM NM On
v.9.0.32 For the statistical analyses of ground water by URS Corporation only. UG
Parametric Confidence interval
Compliance Limit is not exceeded. Per-well alpha = 0.01. Normality Test: Shapiro Wilk at Alpha = 0.01.
0.3
0.22
0.14
0.06
-J
? -0.02
-0.1
1 1 Limit = 0.1
'451'ik
Constituent: Nickel Analysis Run 4/9/2018 3:19 PM
Facility: Payson City LF Client: Payson City Data File: PaysonMW456
Confidence Interval Page 1
Constituent: Nickel (mg/L) Analysis Run 4/9/2018 3:19 PM
Facility: Payson City LF Client: Payson City Data File: PaysonMW456
MW-6
6/15/2017 0.0265
9/14/2017 0.0257
12/12/2017 0.107
3/7/2018 0.0584
Mean 0.0544
Std. Dev. 0.03823
Upper Lim. 0.1412
Lower Lim. -0.0324