DERR-2025-000168

WASATCH ENVIRONMENTAL, INC.
ENVIRONMENTAL SCIENCE AND ENGINEERING

2410 WEST CALIFORNIA AVENUE
SALT LAKE CITY, UTAH 84104
PHONE [phone]
e-mail: [e-mail]
www.wasatch-environmental.com

REMEDIAL ACTION PLAN IMPLEMENTATION REPORT
FORMER SOMMERS AUTO WRECKING
647 WEST 3300 SOUTH
SOUTH SALT LAKE, UTAH
VOLUNTARY CLEANUP PROGRAM SITE NO. C122

Project No. 2469-002H

Prepared for:

Mr. Mark Bond
Mountain Crest Wasatch, LLC
3150 West 900 South
Salt Lake City, Utah 84104

and

Utah Department of Environmental Quality
Division of Environmental Response and Remediation
Mr. Bill Rees and
Mr. Lincoln Grevengoed
P.O. Box 144840
Salt Lake City, UT 84114-4840

Prepared by:

Wasatch Environmental, Inc.
2410 West California Avenue
Salt Lake City, UT 84104

________________________________________
Jake Scott, P.G.
Senior Field Geologist

________________________________________
Blake B. Downey, P.G.
Vice President and Senior Project Hydrogeologist

December 27, 2024

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TABLE OF CONTENTS
Section Page No.
1. INTRODUCTION ............................................................................................................. 1
1.1 Site Description ................................................................................................................... 1
1.2 Site Background .................................................................................................................. 1
1.3 Conceptual Site Model ........................................................................................................ 3
1.4 Objectives ........................................................................................................................... 4
1.5 Contaminants of Concern ................................................................................................... 4
1.6 Cleanup Goals .................................................................................................................... 4
1.7 Remedial Action Measures ................................................................................................. 5
1.8 Proposed Engineering and Institutional Controls ................................................................ 5
1.8.1 Environmental Covenant (EC) and Site Management Plan (SMP) ........................ 5
2. PERMITTING AND NOTIFICATION REQUIREMENTS................................................... 5
2.1 Blue Stake Utility Clearance ............................................................................................... 5
2.2 Soult Salt Lake Permit ........................................................................................................ 5
2.3 Utah Division of Water Quality (UDWQ) Treated Groundwater Discharge Permit ............. 5
2.4 Notification to Salt Lake County Health Department .......................................................... 6
2.5 Public Notice ....................................................................................................................... 6
3. REMEDIAL ACTION METHODS ..................................................................................... 6
3.1 VCP-Requested Sampling .................................................................................................. 6
3.2 Test Pit Sampling ................................................................................................................ 6
3.3 Impacted Soil Excavation and Off-Site Disposal ................................................................ 7
3.3.1 EXC-1, EXC-2, and EXC-3 Excavations ................................................................ 7
3.3.2 EXC-4 Excavation ................................................................................................... 8
3.4 Extraction, Treatment, and Disposal of Petroleum-Impacted Groundwater ....................... 8
3.5 Soil Confirmation Sampling ................................................................................................. 8
3.6 Groundwater Confirmation Sampling .................................................................................. 9
3.7 Monitoring Well Installation, Development, Surveying, and Sampling ............................... 9
3.8 Waste Characterization Sampling ..................................................................................... 10
3.9 General Demolition and Construction Practices ............................................................... 11
4. REMEDIAL RESULTS ................................................................................................... 11
4.1 VCP-Requested Sampling ................................................................................................ 11
4.2 Test Pit Sampling .............................................................................................................. 11
4.3 Impacted Soil Excavation and Off-Site Disposal .............................................................. 12
4.3.1 EXC-1, EXC-2, and EXC-3 Excavations .............................................................. 12
4.3.2 EXC-4 Excavation ................................................................................................. 12
4.4 Extraction, Treatment, and Disposal of Petroleum-Impacted Groundwater ..................... 12
4.5 Soil Confirmation Sampling ............................................................................................... 12
4.6 Groundwater Confirmation Sampling ................................................................................ 14
4.7 Monitoring Well Installation, Development, Surveying, and Sampling ............................. 14
4.8 Waste Characterization Sampling ..................................................................................... 15
5. QUALITY ASSURANCE/QUALITY CONTROL (QA/QC) ............................................... 15
5.1 QA/QC Summary .............................................................................................................. 15
5.1.1 Precision (Field and Laboratory Data Precision) .................................................. 15
5.1.2 Accuracy (Field and Laboratory Data Accuracy) .................................................. 15
5.1.3 Representativeness (Field and Laboratory Data Representativeness) ................ 15
5.1.4 Completeness (Field and Laboratory Data Completeness) ................................. 15
5.1.5 Comparability (Field and Laboratory Data Comparability) ................................... 16
5.1.6 Sensitivity (Field and Laboratory Data Sensitivity) ............................................... 16
6. CONCLUSIONS AND RECOMMENDATIONS .............................................................. 16

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FIGURES

Figure 1 – Site Location Map
Figure 2 – Historical Sample Location and Site Feature Map
Figure 3 – Excavation and Sample Location Map

TABLES

Table 1 – Soil Analytical Data – Volatile Organic Compounds and Petroleum Hydrocarbons
Table 2 – Groundwater Analytical Data – Volatile Organic Compounds and Petroleum Hydrocarbons
Table 3 – Soil Analytical Data – Total Metals and PCBs
Table 4 – Groundwater Analytical Data – Dissolved Metals
Table 5 – Soil Analytical Data - Polycyclic Aromatic Hydrocarbons

APPENDICES

Appendix A – DERR SSCL Calculator Documents
Appendix B – Blue Stakes Documentation
Appendix C – South Salt Lake Permit Documentation
Appendix D – DWQ Treated Groundwater Discharge Permit and Documentation
Appendix E – SLCHD Notice Documentation
Appendix F – Public Notice
Appendix G – Photographic Log
Appendix H – Monitoring Well Construction Logs
Appendix I – Waste Disposal Documentation
Appendix J – Analytical Laboratory Reports
Appendix K – Data Validation Reports

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REMEDIAL ACTION PLAN IMPLEMENTATION REPORT
FORMER SOMMERS AUTO WRECKING
647 WEST 3300 SOUTH
SOUTH SALT LAKE, UTAH
VOLUNTARY CLEANUP PROGRAM SITE NO. C122

1. INTRODUCTION

On behalf of Mountain Crest Wasatch, LLC, the current property owner of the former Sommers Auto
Wrecking property (Site) and the Volunteer, Wasatch Environmental, Inc., (Wasatch) has prepared this
Remedial Action Plan (RAP) Implementation report that documents the remedial activities of heavy
metals and petroleum hydrocarbon impacts to soil and groundwater at the Mountain Crest Wasatch,
LLC., property (Site) located at 647 West 3300 South in South Salt Lake, Utah. All remedial activities at
the Site were performed by Wasatch and our subcontractors in accordance with Wasatch’s general health
and safety policy, RAP, Sampling and Analysis Plan (SAP), and Quality Analysis Project Plan (QAPP). A
site-specific health and safety plan was prepared and implemented on-Site during all remedial activities to
address specific health and safety concerns and establish protocols for conducting work -related activities
in a safe manner.

1.1 Site Description

The Site is located on the southeast corner of the 3300 South and 700 West intersection in South Salt
Lake, Utah (as shown on Figure 1). The Site totals 5.15 acres and is comprised of two parcels (15-25-
351-034 and 15-26-477-006).

The majority of the Site lies behind a vinyl and metal fence. The northern portion of the Site, outside of
this fence, consists of a small asphalt-paved parking area, and a gravel-covered storage yard. The
northeast portion of the Site is developed with an office building; two garage buildings; and a three-sided,
metal, former dismantling building. On the western portion of the Site is a three-sided, metal, former oil
storage building with a canopy-covered concrete secondary containment area. In the southwest corner of
the Site, there is a metal canopy. The remainder of the Site consists of storage yard areas with concrete
pads, pavement, and the majority of the area consisting of gravel.

Property use at the Site and surrounding properties is a mix of commercial and light industrial.

1.2 Site Background

The Site was formerly an auto wrecking yard previously occupied by Sommers Auto Wrecking. Currently,
the Site is occupied by a landscaping company but will be occupied by a metals recycling facility in the
near future.

Our research indicates that the Site was residential and agricultural until 1956 when the former Sommer
Auto Wrecking business started on the eastern portion of the Site. The wrecking yard expanded to the
west between the 1960s and 1990s. In 2019, Sommers Auto Wrecking vacated the Site.

Wasatch prepared an August 19, 2021, Phase I Environmental Site Assessment for the Site. During the
completion of the Phase I Environmental Site Assessment, Wasatch identified the following recognized
environmental conditions in connection with the Site:

• In 2012, the Utah Division of Solid and Hazardous Waste (DSHW) recommended the removal of
oil-impacted soil in the area of the dismantling building by the Site owner. Approximately 840
tons of impacted soil was removed and disposed off-Site. The excavation reportedly stopped at a
clay layer approximately 4 feet below ground surface (bgs) and confirmation soil samples were
not collected. No formal closeout documentation was created. Given that no confirmation soil
samples were collected, there is a potential for residual impacts in this area.
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• Total petroleum hydrocarbons as gasoline-range organics (TPH-GRO) and oil and grease (O&G)
impacts to soil and groundwater exceeding Utah Initial Screening Levels (ISLs) and/or Utah Risk -
Based Corrective Action (RBCA) Tier 1 Screening Levels were identified by DSHW in 2012.

• Low concentrations of tetrachloroethene (PCE) were detected in soil and water samples in two
areas in 2012 indicating that PCE was either brought onto, or used at, the Site; therefore, there is
a potential for elevated concentrations of PCE to be present in soil and groundwater in other
areas of the Site.

• Soil samples collected in 2012 were analyzed for Toxicity Characteristic Leaching Procedure
(TCLP) metals, which is an analysis that measures leaching potential when evaluating soil
disposal options. While the TCLP metals concentrations were below United States
Environmental Protection Agency (U.S. EPA) landfill regulations, this analysis does not measure
the concentration of contaminant of concern in a sample. Later in 2012, lead was detected in a
waste characterization soil sample that was collected dur ing excavation activities at
concentrations that exceeded U.S. EPA Residential and Commercial Regional Screening Levels
(RSLs), indicating that elevated metals concentrations are likely present at the Site.

• There was a drainage system and sump in the former oil storage building that was reportedly not
working and has since been filled with concrete. There is a potential for impacts to the
subsurface from this former drainage system.

• Given the long-term use of the Site for auto wrecking and evidence of long-term poor
housekeeping practices, there is a potential for impacts to the Site in areas that were not
investigated in 2012.

• There is a potential for impacts to the Site from releases associated with the long -term use of the
east adjoining Pick-n-Pull property for auto wrecking.

From 2021 through 2023, Wasatch completed three soil and groundwater sampling events that identified
and characterized heavy metals and petroleum hydrocarbon impacts at the Site. During this time,
Wasatch recommended that these impacts be reported to the Utah DEQ. The owner/operator of the Site
reported the release to the Utah DEQ. As of July 22, 2022, the Site has been entered into the Utah
Voluntary Cleanup Program (VCP) for regulatory oversight and has been assigned VCP Site #C122. The
Utah VCP requested that additional Site characterization activities be completed at the Site, at the time of
entry into the VCP, to facilitate the development of a RAP.

The Site was sufficiently characterized and documented in the VCP-approved “Site Characterization
Report – Revised” dated November 2023, which was completed by Wasatch (see this report for full
details). Based on this report, lead and arsenic were detected in soils at concentrations that exceeded
the U.S. EPA RSL for Industrial Soil, and petroleum hydrocarbons were detected in soil and groundwater
at concentrations that exceeded their applicable Utah Initial Screening Level, U.S. EPA RSL for Industrial
Soil, U.S. EPA MCL, and/or the calculated Site-Specific Cleanup Levels (SSCLs) calculated used the
Utah DERR-approved DERR RBCA SSCL calculator. See Section 1.3 for additional details. Four
impacted areas were identified by Wasatch and recommended for active remediation.

Given the totality of the Site characterization data, Wasatch submitted a RAP to the VCP which was
approved in a letter from the VCP dated January 30, 2024. In the RAP, an arsenic in soil cleanup goal of
45 mg/kg was requested by Wasatch and accepted by the VCP.

Given the totality of the VOC and petroleum hydrocarbon data, it does not appear that these impacts are
migrating off-Site. This is likely due to the clay lithology of the Site.

See Figure 2 for the historical sample locations and Site features.
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1.3 Conceptual Site Model

The Site is located within the discharge area for the principal basin-fill aquifer system. The discharge
area of the basin-fill aquifer system is characterized by a shallow unconfined aquifer overlying a deep
confined aquifer, with a confining layer (aquitard) separating the shallow unconfined aquifer from the deep
confined aquifer. The discharge area typically exhibits an upward vertical hydraulic gradient.

Soils at the Site generally consist of gravelly sand (SW/SP), gravel (GP), and clay (CL) fill materials
ranging in thickness from 1 to 5 feet bgs. The fill is underlain primarily by clay (CL) and clayey sand (SC)
with some silt (ML) and sand (SP). The dominant lithology of the Site is clay (CL). Based on previous
borings and monitoring wells, depth to groundwater at the Site ranges from approximately 5 to 9 feet bgs.
The hydraulic gradient is generally to the northwest. Soils consisting primarily of si lts and clays are
potential contaminant storage zones.

The majority of the metals impacts to soil was located within the surface soils or the upper 3 to 4 feet of
soil at the Site, and the petroleum hydrocarbon impacts are typically located within the upper 6 feet of soil
but extend down to 10 feet in localized areas.

The southwest portion of the Site exhibited evidence of significant petroleum hydrocarbon contamination
(exceeding U.S. EPA RSLs for Residential Soil and Industrial Soil) in shallow and deep soil indicative of a
surface release(s) in this area. The distribution of these impacts was localized in the southwestern
portion of the Site.

Based on the groundwater samples collected by Wasatch, groundwater samples GP -14, GP-15, GP-16,
GP-22, GP-23, and GP-23 exhibited petroleum hydrocarbon impacts (including benzene, ethylbenzene,
and xylenes) concentrations that exceeded the applicable U.S. EPA MCL or Utah ISLs.

All soil samples collected by Wasatch for metals analysis exhibited arsenic concentrations in soil that
exceeded the U.S. EPA RSL for Residential and Industrial Soil. The detected arsenic concentrations in
soil has been properly characterized and do not require active remediation except as discussed below
and in Section 1.6.

Wasatch soil samples GP-9 (2’-3’) and GP-11 (3’-4’) exhibited lead (1,270 mg/kg and 5,390 mg/kg) and
arsenic (109 mg/kg and 141 mg/kg) concentrations in soil that exceeded the U.S. EPA RSLs for both
Residential and Industrial Soil. No soil samples were collected below these samples; however, these
impacts are located in an area of former battery storage as part of the former automotive wrecking
activities at the Site. It has been Wasatch’s experience that heavy metal impacts from battery storage
typically do not extend below 5 feet bgs and typically do not significantly spread laterally from the footprint
of the battery storage area. No other metals were detected at concentrations exceeding applicable U.S.
EPA RSLs for Industrial Soil in these samples.

Wasatch soil sample DU-2E exhibited a lead (1,270 mg/kg) concentration that exceeded the U.S. EPA
RSLs for both Residential and Industrial Soil. No other surface soil samples exhibited heavy metals
concentrations that exceed the U.S. EPA RSLs for Industrial Soil (except for arsenic, see Section 1.6 for
further details)

No other heavy metals impacts were detected in soil samples collected by Wasatch at concentrations that
exceeded their applicable U.S. EPA RSLs for Industrial Soil.

Based on the totality of the arsenic in groundwater data, the concentration range of arsenic -impacted
groundwater entering the Site (highest concentration entering the Site is located at the southeast corner)
is approximately equal to the arsenic impacted groundwater hydraulically downgradient of the Site. Only
one arsenic hot spot in groundwater was identified within the petroleum release area located on the
southwestern corner of the Site. It is our opinion that the release of pe troleum hydrocarbons in this area
has likely increased the leachability of arsenic for this area resulting in elevated arsenic concentrations in
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groundwater. This area was excavated during the active remediation activities which should result in the
reduction of arsenic in groundwater to concentration ranges entering the Site.

Based on the groundwater samples collected by Wasatch, no other metals were detected at
concentrations that exceeded their applicable U.S. EPA MCL. Given the Site will be using a municipal
water supply and not the shallow groundwater, this exposure pathway for metals is considered to be
incomplete. Therefore, Wasatch plans to mitigate these impacts and potential exposure risks through the
use of institutional controls.

The source areas have been identified at the Site. See Figure 3 for source area locations.

1.4 Objectives

Mountain Crest Wasatch, LLC, plans to redevelop the Site mainly for use as an industrial metal recycling
facility. Therefore, the objective of this remedial action was to remediate soil and groundwater at the Site
to meet the U.S. EPA RSLs for Industrial Soil (not including arsenic) and U.S. EPA MCLs for groundwater
or to site-specific fractionation risk thresholds. Given that the Site will be using a municipal water supply
and not the shallow groundwater, this exposure pathway is considered to be incomplete and exposure
risks to the arsenic in groundwater impacts will be mitigated using institutional controls described below .

1.5 Contaminants of Concern

Contaminants of concern at the Site are arsenic, lead, benzene, toluene, ethylbenzene, xylenes,
naphthalene (BTEXN), TPH-GRO, total petroleum hydrocarbons as diesel-range organics (TPH-DRO),
and total recoverable petroleum hydrocarbons (TRPH)/O&G.

1.6 Cleanup Goals

For arsenic in soil, a cleanup goal of 45 mg/kg was approved by the VCP.

The cleanup goals for soil at the Site are the U.S. EPA RSLs for Industrial Soil (except for arsenic as
discussed above) or for TPH-GRO, TRPH, O&G, and TPH-DRO site-specific fractionation risk-based
cleanup goals (calculated using the DERR-approved DERR RBCA SSCL calculator using post
remediation exposure risk potential, see Appendix A) for the following exposure pathways: surface soil
ingestion and subsurface soil ambient air vapor inhalation. The site-specific fractionation risk for
subsurface soil indoor air vapor inhalation will also be evaluated, but is not considered a remediation
goal, as if this threshold is exceeded this exposure will be mitigated using engineering controls.
Remediation of soil to this standard is protective of composite workers and construction workers with
respect to the soil ingestion and inhalation exposure pathways.

No active remediation was proposed for the arsenic impacts to groundwater; however, it is Wasatch’s
opinion that the active remediation proposed for the petroleum hydrocarbons will likely reduce the arsenic
in groundwater concentrations within that area to concentrations ranges en tering the Site.

Groundwater at the Site would be remediated to meet the U.S. EPA MCLs (except for arsenic as
discussed above) or site-specific fractionation risk-based goals for the groundwater outdoor air vapor
inhalation pathway. The site-specific fractionation risk for groundwater indoor air vapor inhalation
pathway would be evaluated, but would not be considered a remediation goal, as if this threshold is
exceeded this exposure would be mitigated using engineering controls. Groundwater is not used at the
Site; therefore, the ingestion of groundwater exposure is not complete and this exposure would be
mitigated using engineering or institutional controls.

Residual risk to on-Site receptors will be managed through the use of engineering and institutional
controls (discussed in Section 1.8 below), and Wasatch will coordinate to obtain VCP approval of the
required environmental covenant and site management plan under a separate cover.

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1.7 Remedial Action Measures

Given the Site characteristics, nature and distribution of contaminants, and proposed future land use;
Wasatch selected over-excavation and off-Site disposal of the impacted soil within the source areas.
Additionally, petroleum-impacted groundwater was extracted from the petroleum soil excavation (EXC-4),
then treated on-Site and properly discharged under permit to the stormwater sewer. Details regarding the
remedial action measures are provided in Section 3 of this report.

1.8 Proposed Engineering and Institutional Controls

The following engineering and institutional controls are proposed to manage residual exposure risks post
remedial actions.

1.8.1 Environmental Covenant (EC) and Site Management Plan (SMP)

Wasatch and the Volunteer understand that a SMP and EC would be required to facilitate
regulatory closure of the release. Institutional controls (i.e., an EC and/or SMP, etc.) and
engineering controls will be implemented as needed to reduce the probability of exposure to the
contaminated soil and/or groundwater by restricting how the Site may be used (i.e., forbidding the
extraction and use of shallow groundwater, providing directions for managing impacted
groundwater in the future [groundwater monitoring, obtaining groundwater dewatering permits if
needed], etc.). This would be protective of Site occupants and could facilita te regulatory closure
of the release at the Site with residual soil and/or groundwater contamination left in place on -Site.
The EC and SMP would be subject to review and approval by the Utah Division of Environmental
Response and Remediation (DERR). Engineering and institutional controls would be protective
of Site occupants.

At a minimum, these documents would restrict property use to non-residential use (without further
remedial activities and additional sampling to verify this property use is safe) in contact with the
ground surface and prohibit the extraction and use of shallow groundwater. The specific wording
of these restrictions, the need for engineering controls (i.e., vapor barriers, etc.), and the potential
need for long-term monitoring requirements (i.e., groundwater monitoring, etc. [if required]),
would be based on the outcome of the remedial action effort as indicated by laboratory analytical
results from the soil and groundwater confirmation sampling.

2. PERMITTING AND NOTIFICATION REQUIREMENTS

2.1 Blue Stake Utility Clearance

Wasatch submitted a utility clearance request (Ticket Number C41210893-00C) to Blue Stake Utility
Notification Center on July 30, 2024, prior to the excavation work. The Blue Stake Ticket Number was
communicated via email to the contractors on the same date so that they could duplicate the request. A
copy of the email confirmation sent from Blue Stake of Utah is presented in Appendix B.

2.2 Soult Salt Lake Permit

Wasatch submitted an “Engineering Application” to the South Salt Lake Engineering Department to
facilitate the on-Site excavation activities. The permit was approved and issued by Soult Salt Lake on
August 1, 2024. Documentation related to this permit is presented in Appendix C.

2.3 Utah Division of Water Quality (UDWQ) Treated Groundwater Discharge Permit

Wasatch submitted an “UPDES [Utah Pollutant Discharge Elimination System] general Permit for Treated
Groundwater and Surface Water” notice of intent to the UDWQ on June 24, 2024, to facilitate the
treatment and disposal of petroleum-impacted groundwater from the EXC-4 excavation. The UDWQ
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approved the permit by email on July 16, 2024, and assigned the Site permit number UTG7901107. On
September 27, 2024, following completion of the treatment and groundwater discharge (which was
completed as a single batch discharge), Wasatch submitted a “Notice of Termination” (NOT) form to
terminate the permit. Documentation related to this permit is presented in Appendix D.

2.4 Notification to Salt Lake County Health Department

Wasatch notified the office of Dorothy Adams, the Salt Lake County Health Department Director, of the
pending remedial action by telephone on July 30, 2024. The telecommunication was documented on a
Wasatch telecom form. The notification stated that the remedial action would commence on
approximately August 5, 2024. A copy of the telecom form is presented in Appendix E.

2.5 Public Notice

On December 15, 2023, Wasatch distributed written notices to the occupants of the neighboring
businesses notifying them of the pending remedial action and advising them of the schedule for the
corrective action. A copy of the written notice is presented in Appendix F.

3. REMEDIAL ACTION METHODS

The following sections of this report present the methods and results of the remedial activities conducted
in connection with the documented petroleum hydrocarbon and metals impacts at the Site. All remedial
action activities were performed by the Volunteers subcontractors and by Wasatch and our
subcontractors in accordance with Wasatch’s general health and safety policy. The health and safety
plan was on-Site at all times during the remedial activities. Daily health and safety tailgate meetings were
conducted by Wasatch during the corrective action. See Appendix G for a photographic log of field
remedial activities.

3.1 VCP-Requested Sampling

Given that TRPH and O&G concentrations from surface soil sample DU-1 and a TPH-DRO concentration
from surface soil sample DU-2 exceeded Utah ISLs during the previous 2023 investigation, the VCP
requested that a second sample be collected from each of these DUs to further evaluate the risks
associated with these impacts.

On June 17, 2024, Wasatch collected one 20-point composite surface soil sample from each of these
DUs. Each aliquot location was randomly selected to provide sufficient spatial distribution. The samples
were designated “DU-1” and “DU-2” to correspond to the DUs shown on Figures 2 and 3. Additionally, a
duplicate sample of DU-1 was collected and designated DU-10.

Each aliquot for the 20-point composite soil samples was collected using gloved hands and a clean 2 -
ounce glass jar. A new 2-ounce glass jar was used for each individual DU. Each aliquot consisted of 2
ounces of soil, which was placed inside a plastic Ziploc ® bag and homogenized for a minimum of 5
minutes prior to dispensing the soil into the laboratory-supplied sample containers. The sample
containers were each labeled with the sample location, sample identification, date, required analysis, and
time of sample collection. All composite soil samples were placed on ice in a sample cooler. The coolers
containing the soil samples were hand delivered, under chain-of-custody protocol to Chemtech-Ford
Laboratory (CF), a Utah-certified analytical laboratory, for analysis. These samples were analyzed for
TPH fractionation using U.S. EPA Method 8270E to further evaluate the risks associated with these
impacts.

3.2 Test Pit Sampling

Prior to commencing remedial activities at the Site, Wasatch submitted utility clearance requests to Blue
Stake Utility Notification Center on June 12, 2024, and July 30, 2024.
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On June 17, 2024, a total of six test pits (designated TP-1 through TP-6) were completed at the Site that
facilitated the collection and analysis of soil samples. The test pits were excavated using a mini
excavator operated by Direct Push Services (DPS), the subcontractor. The test pits were completed in
the vicinity of the proposed petroleum-impacted soil excavation (EXC-4) in an effort to better define the
lateral extent of petroleum impacts to soil and to potentially reduce the area of active remediation. See
Figure 3 for test pit soil sample locations.

Soil excavated from the test pits was screened in the field using a photoionization detector (PID)
equipped with a 10.6 electron volt lamp. The PID was calibrated with a 100-parts per million (ppm)
isobutylene standard calibration gas. The PID is utilized to identify soils which may have been impacted
by volatile organic compounds (VOCs) such as those found in petroleum fuels and some solvents. One
soil sample was collected from each test pit location at the depth interval exhibiting the most significant
indications of contamination based on field screening and field observations (e.g., elevated PID readings,
soil staining, and petroleum or solvent odors). However, soil samples collected from test pit locations that
coincide with previous sample locations were collected at that same depth interval.

The soil samples were collected using gloved hands and dispensed into appropriate laboratory-
supplied/prepared containers and immediately placed in iced coolers. Soil samples collected for TPH-
GRO fractionation analysis were collected following the U.S. EPA Method 5035A sampling procedure.
Soil samples collected for TPH-DRO fractionation were collected into 4-ounce glass jars. Each sample
was labeled with date of collection, sample time, sample identification, and requested analysis. The soil
samples were submitted under chain-of-custody protocol CF for analysis. The soil samples were
analyzed for TPH-GRO fractionation using U.S. EPA Method 8260D and TPH-DRO fractionation using
U.S. EPA Method 8270E.

Following completion of the test pit soil sampling activities, the test pits were backfilled and compacted
with clean imported fill material.

3.3 Impacted Soil Excavation and Off-Site Disposal

Remedial activities at the Site were performed by Wasatch Senior Field Geologist Jake Scott; P.G.,
between August 6, 2024, and September 20, 2024. Remedial activities involved the completion of one
shallow impacted area excavation (EXC-1) and the completion of three deep impacted area excavations
(EXC-2, EXC-3, and EXC-4). See Figure 3 for excavation locations and boundaries.

3.3.1 EXC-1, EXC-2, and EXC-3 Excavations

EXC-1 was completed along a portion of the northeastern boundary of the Site, where lead
impacts to shallow soil were identified. EXC-2 was completed in the vicinity of soil boring GP-9,
where deep lead and arsenic soil impacts were identified. EXC-3 was completed in the vicinity of
soil boring GP-11, where deep lead and arsenic to soil impacts were identified.

Excavations EXC-1, EXC-2, and EXC-3 were guided based upon field screening using a
handheld X-ray fluorescence (XRF) analyzer. The XRF analyzer is utilized to identify the
presence of a wide range of elements in the soil, namely heavy metals. Impacted soil for each
excavation was directly loaded into haul trucks using an excavator and then transported to IRL for
disposal. Each load was documented with a non-hazardous waste manifested by Wasatch. The
excavations continued until there were little to no remaining indications of lead and arsenic
impacts (i.e., no staining, no odors, or elevated XRF readings).

Soil under the on-Site buildings was not excavated as the buildings are not planned for
demolition. A large area of the planned EXC-1 area was covered with concrete pavement. The
concrete pavement was excavated and disposed of off -Site and the soil beneath the concrete
was screened with an XRF and sampled as a composite surface soil sample (EXC -1-Comp) to
determine if this soil required excavation and off-Site disposal. Based on the soil XRF screening
and the composite soil sample, Wasatch determined the area under the former concrete
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pavement did not require remediation. The remainder of the area within the EXC -1 boundary was
excavated to approximately 0.5 feet bgs.

The Volunteer provided their own in-house Occupational Safety and Health Administration
(OSHA)-certified excavator and transportation subcontractors.

3.3.2 EXC-4 Excavation

EXC-4 was completed on the southwestern corner of the Site where petroleum hydrocarbon
impacts were identified. Excavation EXC-4 was guided based upon past data, test pit data, soil
confirmation data, field observations of grey to black staining and petroleum hydrocarbon odors,
as well as field screening using a photoionization detector (PID) equipped with a 10.6 electron
volt lamp.

Impacted soil for each excavation was directly loaded into haul trucks using an excavator and
then transported to IRL for disposal. Each load was documented with a non-hazardous waste
manifested by Wasatch. The excavations continued until there were little to no remaining
indications of petroleum hydrocarbon impacts (i.e., no staining, no petroleum odors, or elevated
PID readings).

3.4 Extraction, Treatment, and Disposal of Petroleum-Impacted Groundwater

Groundwater was encountered at approximately 6 to 7 feet bgs during the excavation activities in
excavation EXC-4. The groundwater was petroleum-impacted as evident by a strong hydrocarbon odors,
observed sheens, and observed free product on the water surface. During the excavation activities,
sorbent pads were placed in the excavation pit to soak up and remove as much free product as possible.
Once the observed free product appeared to be removed from the water within EXC-4, the absorbent
materials were collected and placed within a 55-gallon drum for disposal. This drum was picked up by
Safety Kleen and disposed at the Clean Harbors Grassy Mountain facility.

Petroleum-impacted groundwater was removed from the EXC-4 excavation pit using a trash pump and a
2-inch diameter water hose, which was then discharged into two separate 21,000-gallon holding tanks
located on-Site. An aeration system constructed of 1-inch diameter PVC was installed within each
holding tank. Both aeration systems were continuously operated during the dewatering process using a
gas-powered air compressor to aerate and remove VOCs. Once the holding tanks were near full
capacity, the water was then discharged through a bag filter and granular activated carbon vessel, and
was then discharged to the storm sewer located off-Site just southwest of EXC-4.

Prior to discharging the water from the holding tanks into the storm sewer, water samples (designated
“Fack Tank 1” and Frac Tank 2”) were collected from the discharge hose of the granular activated carbon
vessel to verify the treated groundwater water met the UDWQ permit discharge requirements. The
treated groundwater was discharged as a single batch discharge event.

3.5 Soil Confirmation Sampling

Following the completion of each excavation, soil confirmation samples were collected from the floors and
side walls to establish that cleanup levels had been met. The sample locations were spaced at intervals
to provide sufficient coverage of the entire excavation and not allow more than 50 linear feet of sidewall
and no more than 2,000 square feet of floor to go unsampled. See Figure 3 for soil confirmation sample
locations.

Soil confirmation samples collected for analysis of methyl tertiary-butyl ether, benzene, toluene,
ethylbenzene, xylenes, and naphthalene (MBTEXN), and TPH-GRO were collected using a laboratory-
supplied sampling device, sample preservation methods, and sample containers consistent with U.S.
EPA Method 5035A for the collection of VOCs. Soil confirmation samples were collected from each
sample interval for both low-range (0.5 to 250 micrograms per kilogram [µg/kg]) and high-range (>250
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µg/kg) laboratory analysis for VOCs. Low-range soil samples were collected as 5-gram (g) aliquots and
placed in laboratory-supplied, unpreserved volatile organic analysis (VOA) bottles. High-range samples
were collected as 10g aliquots and placed in laboratory-supplied VOA bottles preserved with methanol.
Soil confirmation samples collected for analysis of TPH -DRO, lead, and arsenic were dispensed into
laboratory-supplied 4-ounce glass jars.

The confirmation soil samples were collected using gloved hands. The vials and jars were each labeled
with the sample location, sample identification, date, time of sample collection, and requested analysis.
The soil confirmation samples were placed in a cooler with ice and transported under chain -of-custody
protocol to CF for analysis. The soil confirmation samples collected from EXC-1 were analyzed for lead
using U.S. EPA Method 6020A. The soil confirmation samples collected from EXC-2 and EXC-3 were
analyzed for lead and arsenic using U.S EPA Method 6020A. The soil confirmation samples collected
from EXC-4 were analyzed for MBTEXN and TPH-GRO using U.S. EPA Method 8260D and TPH-DRO
using U.S. EPA Method 8015D with silica get treatment (SGT). To expedite the process, laboratory
analysis was performed on a 24-hour turnaround time. Additionally, selected soil confirmation samples
collected from EXC-4 were also analyzed for TPH-GRO fractionation using U.S. EPA Method 8260D and
TPH-DRO fractionation using U.S. EPA Method 8270E.

After completion of the excavations, and receipt of the confirmation sample analytical results confirming
cleanup goals had been met or additional excavation was not possible due to the presence of
underground utilities, the excavations were backfilled and compacted with clean imported fill material.

3.6 Groundwater Confirmation Sampling

Following completion of the dewatering activities, a total of two groundwater confirmation samples
(designated “EXC-4-GW1” and “EXC-4-GW2”) were collected from the upgradient and downgradient
portion of the open excavation pit to verify that cleanup levels for groundwater had been met. See Figure
3 for excavation confirmation groundwater sample locations.

Groundwater confirmation samples collected from the open excavation were collected using gloved
hands and a Teflon dipper. The groundwater confirmation samples were then dispensed into 40-milliliter
(mL) capacity glass vials with Teflon® septa caps. The vials, which were supplied by the analytical
laboratory contained several drops of hydrochloric acid as a preservative. The vials were filled slowly
until a meniscus formed at the top of each vial, then each vial was sealed with a septa cap. This
procedure eliminates headspace within the vials and minimizes the loss of volatiles. The sample
containers were each labeled with the sample location, sample identification, date and time of sample
collection, and requested analysis. The groundwater confirmation samples were placed in an iced cooler
and transported under chain-of-custody procedure, to CF for analysis. The groundwater confirmation
samples were analyzed for MBTEXN and TPH-GRO using U.S. EPA Method 8260D and TPH-DRO using
U.S. EPA Method 8015D with SGT.

3.7 Monitoring Well Installation, Development, Surveying, and Sampling

On October 4, 2024, after completion of the remedial activities, two properly constructed monitoring wells
(MW-6 and MW-7) were installed at the Site. Monitoring well MW-6 was completed within the footprint,
but on the hydraulically downgradient portion, of EXC-4, and monitoring well MW-7 was completed just
north (hydraulically downgradient) of EXC-4. Both monitoring well locations are shown on Figures 2 and
3. Monitoring well construction logs are presented as Appendix H.

Each well was completed as follows:

• Well screen was placed from 5 to 15 feet bgs and consisted of 0.01-slot, schedule 40, 2-inch
polyvinyl chloride (PVC) well screen material.

• Placement of a flat bottom well foot at the bottom of the screen.

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• Well casing attached to the top of the screen and extending to approximately 0.5 feet bgs
consisting of schedule 40, 2-inch PVC, well casing material.

• A 10/20 filter pack sand material was placed in the annulus space from approximately 3 to 15 feet
bgs.

• A bentonite well seal was placed in the annulus space from approximately 1 to 3 feet bgs.

• A surface completion consisting of a steel flush-mount well vault placed in concrete.

Approximately 24 hours after the monitoring wells were installed, Wasatch developed each monitoring
using over pumping techniques with a submersible pump. Well development was performed to reduce
the turbidity of each well to provide low turbidity samples during the groundwater sampling activities.
Wasatch considered well development to be completed once a minimum of five casing volumes of
groundwater had been purged from the well or the well showed significant improvement in turbidity.

The wells were allowed to equilibrate for at least 72 hours prior to the collection of groundwater samples.
On October 7, 2024, Wasatch collected groundwater samples from and surveyed the top-of-casing (TOC)
elevations of monitoring wells MW-6 and MW-7.

The well TOCs were surveyed using LaserPlane surveying equipment to the nearest one-hundredth of a
foot and were surveyed into the previously established arbitrary datum of 100.00 feet at the Site.

Prior to groundwater sample collection, Wasatch collected depth-to-water measurements with an
electronic interface water level probe from both monitoring wells. The interface probe was
decontaminated between each well by washing with an Alconox® and distilled water solution, followed by
a triple rinse of distilled water.

A new disposable bailer was used to purge each monitoring well prior to sample collection. Both
monitoring wells were sampled using standard purge sampling techniques and purged of at least three
casing volumes of water.

Groundwater samples were dispensed into appropriate laboratory-supplied sample containers, using
gloved hands, placed in a cooler with ice, and transported under chain-of-custody protocol to CF for
analysis. The groundwater samples were analyzed for TPH-GRO and MBTEXN using U.S. EPA Method
8260D and TPH-DRO using U.S. EPA Method 8015D with SGT. Additionally, groundwater sample MW-7
was also analyzed for TPH-GRO fractionation using U.S. EPA Method 8260D.

Produced groundwater was thin spread on the ground surface near the wells they originated from.

3.8 Waste Characterization Sampling

On June 17, 2024, Wasatch completed several test pits within the proposed excavation areas (EXC-1
through EXC-4) at the Site to complete waste characterization of the proposed soil waste. The soil
samples collected from EXC-1, EXC-2, and EXC-3 were composited to represent a single sample
(designated EXC-1-3 WCS) representing the metals-impacted soil waste. Additionally, the test pits
completed within EXC-4 were composited to represent a single sample (designated Test Pit WCS)
representing the petroleum-impacted soil waste. This was done to obtain approval to dispose of the
waste at the Intermountain Regional Landfill (IRL). The RAP stated that soil waste would be disposed at
the Salt Lake County Landfill (for metals impacted soil) and at ET Technologies Soil Regeneration Site
(for petroleum hydrocarbon-impacted soil); however, the Volunteer elected to dispose of the soil waste at
the IRL. Wasatch coordinated with the VCP on this change and obtained VCP concurrence that we could
dispose of the soil waste at the IRL.

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Soil sample aliquots were collected from every foot of each test pit for the planned depths of the
associated excavations and placed into a Ziploc® bag. Once all aliquots had been collected for each
waste characterization sample, the aliquots were properly homogenized.

The soil waste characterization samples were collected using gloved hands, placed in appropriate
laboratory-supplied sample containers, and placed on ice. The soil waste characterization samples were
delivered under chain-of-custody to CF for analysis. The EXC-1-3 WCS sample was analyzed for total
and TCLP arsenic and lead by U.S. EPA Method 6010D. The Test Pit WCS sample was analyzed for pH
using U.S. EPA Method 9045D, flash point using U.S. EPA Method 1010Mod, Resource Conservation
and Recovery Act (RCRA) D and F-list toxicity characteristic leaching procedure (TCLP) and total VOCs
using U.S. EPA Method 8260D, O&G using U.S. EPA Method 1664BMod, percent passing using U.S.
EPA Method 1311, and RCRA D and F-list TCLP and total metals using U.S. EPA Methods
6010D/7471A.

This sampling was conducted to facilitate the completion of the appropriate waste profiles to be approved
by IRL. The Volunteer submitted the waste characterization data and completed waste profiles to the IRL
for approval. IRL approved the waste for disposal prior to commencement of the excavation work. See
Appendix I for waste approval and disposal documentation.

3.9 General Demolition and Construction Practices

The following best management practices were employed during the implementation of the remedies:

• The VCP was notified and provided with an opportunity to be present on-Site to observe the
remedial activities.

• No storm drains were located near any of the excavations or haul routes; therefore, no mitigation
activities were required to prevent contaminants from entering the storm sewer system.

• The soil excavation subcontractor was required to decontaminate their equipment prior to arrival
at the Site, and prior to demobilization from the Site.

• A track-out area was constructed by the excavation subcontractor and utilized for any heavy
equipment leaving the Site to prevent tracking mud and/or contaminants onto public roadways.

• Site access was limited by the existing fencing located at the Site.

4. REMEDIAL RESULTS

4.1 VCP-Requested Sampling

Analyte concentrations in the composite surface soil samples were compared to the calculated SSCLs.
The composite surface soil sample analytical data are summarized in Table 1. The laboratory analytical
report for the soil samples is presented in Appendix J.

No analytes were detected at concentrations exceeding the calculated SSCL risk thresholds in any of the
samples.

4.2 Test Pit Sampling

Analyte concentrations in the test pit soil samples were compared to the U.S. EPA RSLs for Residential
and Industrial Soil, Utah ISLs, and the calculated SSCLs. The test pit soil sample analytical data are
summarized in Table 1. The laboratory analytical report for the soil samples is presented in Appendix J.

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Soil sample TP-2 (5’-6’) exhibited a benzene concentration of 0.75 mg/kg which exceeds the Utah ISL for
benzene of 0.2 mg/kg. However, this concentration was below U.S. EPA RSL for Residential Soil (1.2
mg/kg) and Industrial Soil (5.1 mg/kg). Additionally, this concentration is below the all compared
calculated SSCLs. No other analytes were detected in any other sample at concentrations that exceed
the applicable cleanup goals.

4.3 Impacted Soil Excavation and Off-Site Disposal

Four excavations (EXC-1, EXC-2, EXC-3, and EXC-4) were completed at the Site that facilitated the
removal and disposal of petroleum hydrocarbon and metal-impacted soil exceeding the applicable U.S.
EPA RSLs for Industrial Soil and/or calculated SSCLs at the Site. See Figure 3 for the excavation
locations and extents.

A total of 4,065.81 tons of petroleum hydrocarbon and metal-impacted soil was excavated and disposed
off-Site at IRL. The waste disposal documentation (including the waste profile, waste characterization
laboratory report, and waste manifests) is presented in Appendix I.

4.3.1 EXC-1, EXC-2, and EXC-3 Excavations

Excavation EXC-1 extended to a depth of approximately 0.5 feet bgs and measured
approximately 80 feet east to west and 120 feet north to south with an approximate area of 9,600
square feet.

Excavation EXC-2 extended to a depth of approximately 4 feet bgs and measured approximately
32 feet east to west and 31 feet north to south with an approximate area of 992 square feet.

Excavation EXC-3 extended to a depth of approximately 5 feet bgs and measured approximately
25 feet east to west and 37 feet north to south with an approximate area of 925 square feet.

4.3.2 EXC-4 Excavation

Excavation EXC-4 extended to a depth of approximately 9 feet bgs within the western portion of
the excavation and 4 feet bgs within the eastern portion of the excavation, and measured
approximately 120 feet east to west and 100 feet north to south with an approximate area of
12,000 square feet.

4.4 Extraction, Treatment, and Disposal of Petroleum-Impacted Groundwater

Groundwater was encountered at approximately 6 to 7 feet bgs in the EXC-4 excavation. Free product
was absorbed using absorbent pads, contained into a metal 55-gallon drum, and properly disposed of at
the Clean Harbors Grassy Mountain Facility.

The extracted groundwater was successfully aerated to remove VOCs and discharge through a bag filter
and GAC vessel. Prior to discharging the treated groundwater, Wasatch collected a batch discharge
sample just after the treatment train. Based on the analytical results of the discharge sample, all analyte
concentration permit requirements were met and approximately 40,000 gallons of petroleum-impacted
groundwater were treated and disposed of to the municipal the stormwater sewer. Upon completion of
the batch discharge, Wasatch submitted a NOT form to the UDWQ to terminate the permit. UDWQ has
since terminated this permit.

4.5 Soil Confirmation Sampling

Analyte concentrations in the soil confirmation samples were compared to the U.S. EPA RSLs for
Residential and Industrial Soil (for MBTEXN and metals), the Utah ISLs (for TPH-GRO, TPH-DRO, and
O&G), and the calculated SSCLs (for TPH-GRO, TPH-DRO, and O&G). The soil confirmation sample
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analytical data are summarized in Table 1 and 3. The laboratory analytical reports for the soil
confirmation samples are presented in Appendix J.

A total of 19 soil confirmation samples (including two duplicate samples) were collected from excavation
EXC-1. Soil confirmation samples collected from excavation EXC -1 exhibited the following:

• Lead was detected in all twenty soil confirmations samples at concentrations ranging from 112
mg/kg to 629 mg/kg. Thirteen of the 19 soil confirmation samples collected from EXC-1 exhibited
lead concentrations above the U.S. EPA RSL for Residential Soil; however, none of these
concentrations exceeded the U.S. EPA RSL for Industrial Soil for lead.

A total of seven soil confirmation samples (including one duplicate sample) were collected from
excavation EXC-2. Soil confirmation samples collected from excavation EXC-2 exhibited the following:

• Lead was detected in all seven soil confirmations samples at concentrations ranging from 165
mg/kg to 668 mg/kg. Six out of the seven soil confirmation samples collected from excavation
EXC-2 exhibited lead concentrations above the U.S. EPA RSL for Residential Soil; however, none
of these concentrations exceeded the U.S. EPA RSL for Industrial Soil for lead.

• Arsenic was detected in all seven soil confirmations samples at concentrations ranging from 12.6
mg/kg to 24.4 mg/kg. All seven soil confirmation samples collected from EXC-2 exhibited arsenic
concentrations exceeding both the U.S. EPA RSLs for Residential (0.68 mg/kg) and Industrial Soil
(3 mg/kg); however, none of these concentrations exceed the VCP-approved arsenic cleanup
goal for soil of 45 mg/kg.

A total of six soil confirmation samples (including one duplicate sample) were collected from excavation
EXC-3. Soil confirmation samples collected from excavation EXC -3 exhibited the following:

• Lead was detected in all six soil confirmations samples at concentrations ranging from 47.5
mg/kg to 766 mg/kg. One out of six soil confirmation samples collected from excavation EXC-3
exhibited a lead concentration above the U.S. EPA RSL for Residential Soil; however, this
concentration did not exceed the U.S. EPA RSL for Industrial Soil for lead.

• Arsenic was detected in all six soil confirmations samples at concentrations ranging from 11.0
mg/kg to 21.4 mg/kg. All six soil confirmation samples collected from EXC-3 exhibited arsenic
concentrations exceeding both the U.S. EPA RSLs for Residential and Industrial Soil; however,
none of these concentrations exceed the VCP-approved arsenic in soil cleanup goal.

A total of eighteen soil confirmation samples (including two duplicate samples) were collected from
excavation EXC-4. Soil confirmation samples collected from excavation EXC-4 exhibited the following:

• Soil confirmation sample EXC-4-NE exhibited a TPH-DRO concentration of 10,000 mg/kg, which
exceeds the Utah ISL for TPH-DRO of 500 mg/kg. Following receipt of the analytical results,
additional soil was excavated from the area where soil confirmation sample EXC-4-NE was
collected and a second soil confirmation sample (designated EXC -4-NE2) was collected
approximately 10 feet north of the previous sample. No analytes were detected in soil
confirmation sample EXC-4-NE2 at concentrations exceeding their applicable Utah ISLs.

• Soil confirmation sample EXC-4-West 3 exhibited TPH-GRO (1,500 mg/kg), ethylbenzene (164
mg/kg), and total xylenes (794 mg/kg) concentrations that exceeded their applicable Utah ISLs for
TPH-GRO (150 mg/kg), ethylbenzene (5 mg/kg), and total xylenes (142 mg/kg). Naphthalene
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was detected at a concentration of 50.4 mg/kg. This concentration does not exceed the Utah ISL
for naphthalene (51 mg/kg), but exceeds the U.S. EPA RSL for Residential (2 mg/kg) and
Industrial Soil (8.6 mg/kg). The detected ethylbenzene concentration in EXC-4-West 3 also
exceeded the U.S. EPA RSL for Industrial Soil of 25 mg/kg. Following receipt of the analytical
results, additional soil was excavated from the area (the western EXC-4 sidewall) where soil
confirmation sample EXC-4-West 3 was collected and a second soil confirmation sample
(designated EXC-4-West 4) was collected as close to the west boundary of the Site as possible.
Soil confirmation sample EXC-4-West 4 also exhibited TPH-GRO (3,150 mg/kg), ethylbenzene
(103 mg/kg), and total xylenes (604 mg/kg) concentrations that were still above their respective
Utah ISLs and/or U.S. EPA RSLs for Industrial Soil. Naphthalene was detected at a
concentration of 28.1 mg/kg. This concentration does not exceed the Utah ISL for naphthalene,
but exceeds the U.S. EPA RSL for Residential and Industrial Soil. Additionally, benzene (4.41
mg/kg) was detected in soil confirmation sample EXC-4-Floor 4 at a concentration that exceeded
the Utah ISL of 0.2 mg/kg, but was below the U.S. EPA RSL for Industrial Soil of 5.1 mg/kg. Due
to the presence of multiple underground utilities, additional excavation to the west was not
possible.

• Soil confirmation sample EXC-4-West 4 was also analyzed for TPH-GRO fractionation and TPH-
DRO fractionation and exhibited the following concentrations: C5-C6 aliphatic hydrocarbons at
229 mg/kg, C7-C8 aliphatic hydrocarbons at 313 mg/kg, C9-C10 aliphatic hydrocarbons at 453
mg/kg, and C9-C10 alkyl benzenes at 1,420 mg/kg. These detections are below the calculated
SSCLs for their applicable Outdoor Air Vapor Inhalation (OAVI) SSCLs and Ingestion of Soil
SSCLs. See Table 1 for the calculated SSCLs.

• No other soil confirmation samples collected from excavation EXC -4 exhibited analyte
concentrations above their applicable Utah ISLs and/or U.S. EPA RSLs for Industrial Soil.

4.6 Groundwater Confirmation Sampling

Analyte concentrations in the groundwater confirmation samples were compared to the Utah ISLs, the
calculated SSCLs, and the U.S. EPA MCLs. The groundwater confirmation sample analytical data are
summarized in Table 2. The laboratory analytical reports for the groundwater confirmation samples are
presented in Appendix J.

Benzene was detected in groundwater confirmation samples EXC -4-GW1 and EXC-4-GW2. Both
groundwater confirmation samples exhibited a benzene concentration of 8 micrograms per liter (µg/L),
which exceeds both the Utah ISL and the U.S. EPA MCL for benzene of 5 µg/L, but was well below the
calculated OAVI SSCL of 283.

No other analytes were detected in the groundwater confirmation samples at concentrations exceeding
their applicable Utah ISLs, SSCLs, or U.S. EPA MCLs.

4.7 Monitoring Well Installation, Development, Surveying, and Sampling

Monitoring wells MW-6 and MW-7 were successfully installed, developed, surveyed, and sampled. Each
well was developed by purging approximately 20 to 25 gallons of water from the well, which reduced the
groundwater turbidity observed in the purge water.

Analyte concentrations in the groundwater samples were compared to the Utah ISLs, the calculated
SSCLs, and the U.S. EPA MCLs. The groundwater sample analytical data are summarized in Table 2.
The laboratory analytical reports for the groundwater samples are presented in Appendix J.

No analytes were detected in the MW-6 groundwater sample.
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The MW-7 groundwater sample exhibited a TPH-GRO concentration of 1,780 µg/L and a TPH-DRO
concentration of 1,400 µg/L. Both of these concentrations slightly exceed their Utah ISLs for TPH-GRO
of 1,000 µg/L and TPH-DRO of 1,000 µg/L. Given these detections the TPH-GRO fractionation of this
sample was completed. None of the TPH-GRO fractionation analytes exhibited concentrations that
exceed the calculated OAVI SSCLs.

No other analytes were detected at concentrations that exceed their applicable Utah ISLs or U.S. EPA
MCLs in the MW-7 groundwater sample.

4.8 Waste Characterization Sampling

The laboratory analytical results from the soil waste characterization samples indicated that the soil was,
in Wasatch’s opinion, non-hazardous and suitable for disposal at a Subtitle D solid waste landfill. IRL
approved the waste for disposal prior to the commencement of the excavation activities. See Appendix I
for waste approval and disposal documentation.

5. QUALITY ASSURANCE/QUALITY CONTROL (QA/QC)

QA/QC checks were performed for both field sampling and laboratory analysis of the environmental
samples to allow for the evaluation of data quality, documentation of data quality, and to help identify
irregularities in the field sampling or laboratory analyses that may require correction.

5.1 QA/QC Summary

QA/QC samples were collected as specified in the approved QAPP.

5.1.1 Precision (Field and Laboratory Data Precision)

As determined by the third-party data validator, the overall field/laboratory precision for this
project is 93.6%, and no data was rejected; therefore, the precision is considered to be
acceptable and under control.

5.1.2 Accuracy (Field and Laboratory Data Accuracy)

As determined by the third-party data validator, the overall field/laboratory accuracy for this
project is 92.7%, and no data was rejected; therefore, the accuracy is considered to be
acceptable and under control.

5.1.3 Representativeness (Field and Laboratory Data Representativeness)

Field: For this project, the environmental samples were collected from locations either
reasonably believed to be, or established to be, representative to identify source areas, evaluate
the nature of the release(s), and delineate the extent of contamination.

Laboratory: For this project, method blanks were free of target analytes, sample holding times
were not exceeded, all samples were properly preserved, receiving temperatures were not
exceeded; therefore, representativeness for the project is considered acceptable an d under
control.

Overall, 99.6% of the representativeness-related parameters met the project requirements.

5.1.4 Completeness (Field and Laboratory Data Completeness)

All samples (100%) collected were deemed valid based on an independent data validation.
Completeness for the project is considered acceptable and under control.
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5.1.5 Comparability (Field and Laboratory Data Comparability)

Comparability for the project is considered acceptable and under control.

5.1.6 Sensitivity (Field and Laboratory Data Sensitivity)

Laboratory detection limits were less than the regulatory screening levels (except in limited
instances where sample dilution was required); therefore, sensitivity for the project is considered
acceptable and under control.

The data validation reports completed by an independent third-party are presented as Appendix K for
detailed review. No significant QA/QC, QAPP, SAP, or RAP deviations were discovered for this project.

6. CONCLUSIONS AND RECOMMENDATIONS

It is Watch’s opinion that remedial actions completed at the Site have been successful at reducing
contaminant impacts at the Site.

None of the DU surface soil samples collected to further evaluate the petroleum hydrocarbon impacts
exhibited petroleum hydrocarbon impacts that exceeded the applicable SSCLs. Therefore, remedial
activities are not required for the areas sampled.

None of the test pit soil samples exceeded their applicable U.S. EPA RSL for Industrial Soil and/or their
applicable calculated SSCLs. Therefore, the originally anticipated EXC-4 extent was reduced in size
accordingly.

Based on the EXC-1, EXC-2, and EXC-3 soil confirmation data, metals impacts to soil at the Site have
been remediated to concentrations below the VCP-approved cleanup goals.

No EXC-4 soil confirmation samples exceeded their applicable calculated OAVI or Ingestion of Soil
SSCLs. Although not considered a cleanup goal, Wasatch compared the test pit and soil confirmation
samples to the calculated Indoor Air Vapor Inhalation (IAVI) SSCLs. Only one soil confirmation sample
(EXC-4-West 4) exceeded the IAVI SSCL for benzene. Additionally, only one test pit sample (TP-2 (5’-6’)
exceeded the IAVI SSCL for benzene. Given this, and to be conservative, Wasatch recommends that if
future buildings are constructed in this area, a vapor mitigation system be installed to mitigate potential
vapor intrusion risks in this area. Wasatch would include the details of potential vapor mitigation systems
in an EC and SMP to be completed and submitted to the VCP for approval under a separate cover.

Only one final soil confirmation sample (EXC-4-West 4), located along the northwestern sidewall of EXC-
4, exhibited an ethylbenzene and naphthalene concentration that exceeded their U.S. EPA RSL for
Industrial Soil. The sidewall where EXC-4-West 4 was collected was extended to the west to the Site
boundary and to where multiple underground utilities were encountered, thus prohibiting additional
excavation of these impacts. However, the detected ethylbenzene and naphthalene concentrations were
below the calculated Ingestion of Soil and OAVI SSCLs. Based on the EXC-4 soil confirmation data,
petroleum-impacted soil located on-Site has been sufficiently remediated and now met the VCP-approved
cleanup goals. Given the number of utilities present adjacent west of EXC-4 which are impeding further
remediation or investigation, and that the petroleum impacts to soil adjacent west of EXC-4 are likely
minor, it is Wasatch’s opinion that potential exposures to these potential residual petroleum impacts be
mitigated through the use of a Blue Stakes of Utah Notice. This would notify future construction workers
that may encounter these impacts, allowing them to take the appropriate precautions to work safely in
that environment.

The extraction, treatment, and disposal of petroleum-impacted groundwater originating from EXC-4
appear to have been effective. Benzene was the only analyte detected in the groundwater confirmation
samples collected from EXC-4 at a concentration that slightly exceeded the Utah ISL. However, the
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detected benzene concentrations were well below the groundwater cleanup goal for the calculated OAVI
SSCL. Given this and the EXC-4 soil confirmation data, it is Wasatch’s opinion that the petroleum
hydrocarbon source area has been sufficiently remediated.

MW-6 was installed on the downgradient portion of EXC-4 (within the former petroleum hydrocarbon
source area), and MW-7 was installed hydraulically downgradient of EXC-4 to evaluate impacts migrating
to the boundary of the Site. No analytes were detected in the MW-6 groundwater sample, and only low
concentrations of TPH-GRO and TPH-DRO were detected in the MW-7 groundwater sample at a
concentration just above the applicable Utah ISLs. Based on the MW-7 fractionation data, none of the
SSCLs were exceeded by these reported concentrations. Benzene was not detected in either of the MW-
6 and MW-7 groundwater samples. Therefore, it is Wasatch’s opinion that petroleum hydrocarbon
groundwater impacts reaching the Site boundary are likely not of concern and do not require active
remediation.

None of the groundwater confirmation or the MW-6 and MW-7 groundwater samples exhibited analyte
concentrations that exceeded any of the calculated SSCLs. Previous groundwater samples (GP -19, GP-
20, and GP-21) collected hydraulically downgradient (and across 700 West) of the Site and EXC-4, did
not detect any petroleum hydrocarbons at concentrations that exceed the Utah ISLs or U.S. EPA MCLs.
Given that benzene in groundwater is not reaching the Site boundary (based on the sampled locations)
and that no petroleum hydrocarbons were detected hydraulically downgradient of the Site even prior to
remedial actions, it is Wasatch’s opinion that any petroleum-impacted groundwater leaving the Site is
likely minor and considered to be a de minimis condition.

Wasatch recommends that an EC and SMP be completed for the Site, and that upon completion of those
documents that the release be granted regulatory closure by the DERR. Wasatch anticipates the EC and
SMP may include, but is not limited to, the following restrictions: restrict the use of groundwater at the
Site, no ground floor residential structures, properly impacted media handling instructions for construction
workers at the Site, and if impacted soil is required to be removed from the Site coordination with the VCP
may be required.

Figures

The use or reuse of this information is restricted to the referenced document unless otherwise authorized.
Wasatch Environmental Copyright 2006
FORMER SOMMERS AUTO WRECKING WEI 2469-002H
Figure 1 Site Location Map
Approximate
Location of Site
1 inch is equal
to 840 feet
The use or reuse of this information is restricted to the referenced document unless otherwise authorized.
Wasatch Environmental Copyright 2006
Figure 2
Office
(1940)
Inaccessible
Garage
(2000s)
Original
Garage
(1950s)
Dismantling
Building (2013/2014)
(Area of 2012 Soil Removal)
Oil
Building
(1990s)
(Former Sump
in This Building)
Secondary
Containment (Added in 2012)
(Area Where Oil and Grease
Concentration Exceeded
Tier 1 in Soil and Low Concentration
of PCE Was Detected in Water [2012])
Canopy
Stained
Concrete
Stained
Soil and
Concrete
Former Diesel
AST Location
Former Significant Current
and Historical Staining
on Degraded Concrete
Former
Drum StorageFormer Engine Storage
Area Where
TPH-GRO
Exceeded ISLs in Soil
(2012)
Area of Where
TPH-GRO Exceeded
ISLs and Low Concentration
of PCE in Soil Detected (2012)
Building and
Wrecked Vehicles
Where Previously
Located in This Area
(1950s-1980s)
Historical Sample Location and Site Feature Map
FORMER SOMMERS AUTO WRECKING WEI 2469-002H
GP-1
GP-2
GP-3
GP-4
GP-6
GP-7GP-8
GP-9 GP-10 GP-11
GP-12
GP-13
GP-15
GP-16
GP-17
GP-18
1 inch is equal
to 50 feet
GP-25 GP-24
GP-23
3300 South
70
0

W
es
t
GP-26
GP-27
DU-1
DU-2
DU-3DU-4
DU-5
GP-22
GP-14
Monitoring Well Location
LEGEND
DU-X Initial Surface Soil Sampling Decision Unit
Boring Location
GP-30
GP-32
GP-28
GP-29
GP-31
MW-2
MW-3
MW-4
MW-5
MW-1
GP-33
DU-XX Sub-Divided Surface Soil Sampling Decision Unit
GP-5
DU-1A
DU-1B DU-1C DU-1D DU-1E
DU-2A
DU-2B
DU-2C DU-2D DU-2E
70
0

W
es
t
Overhead Power
Sanitary Sewer Line
Storm Water Sewer Line
Communications Line
Water Line
Test Pit Sample Location
TP-1
TP-6
TP-5
TP-2
TP-4
TP-3
MW-6
MW-7
GP-19
GP-20
GP-21
*Map does not include confirmation samples
The use or reuse of this information is restricted to the referenced document unless otherwise authorized.
Wasatch Environmental Copyright 2006
Figure 3Excavation and Sample Location Map
FORMER SOMMERS AUTO WRECKING WEI 2469-002H
1 inch is equal
to 50 feet
3300 South
70
0

W
es
t
LEGEND
Excavation Area
Soil Confirmation Sample Location
EXC-1
Test Pit Sample Location
TP-1
TP-6
TP-5
TP-2
TP-4
EXC-4
EXC-3
Area of Concrete
Removal and Confirmation
Composite Surface Soil Sample Area
Area of Concrete Removal
EXC-4-NW
EXC-4-NE2
EXC-4-East2
EXC-4-East1/
EXC-4-East10
EXC-4-SEEXC-4-SW
TP-3
EXC-4-Floor3 EXC-4-Floor4
EXC-4 Floor40
EXC-4-Floor2
EXC-4-Floor5
EXC-2-N
EXC-2
EXC-2-W/
EXC-2-W2
EXC-2-S
EXC-2-SE
EXC-2-E
EXC-2-Floor
EXC-3-N
EXC-3-Floor/
EXC-3-Floor10
EXC-3-W
EXC-3-S
EXC-3-E
EXC-1-1
EXC-1-2
EXC-1-4
EXC-1-5
EXC-1-3
EXC-1-16/
ECC-1-160
EXC-1-6
EXC-1-7
EXC-1-8
EXC-1-9
EXC-1-10
EXC-1-11
EXC-1-12
EXC-1-13/
EXC-1-130
EXC-1-14
EXC-1-15
MW-6
MW-6
Monitoring Well Location
Excavation Groundwater Sample Location
EXC-4-GW1
Approximate Site Boundary
Overhead Power
Sanitary Sewer Line
Storm Water Sewer Line
Communications Line
Water Line
EXC-4-West1
EXC-4-West2
EXC-4-Floor1
EXC-4-West3/
EXC-4-West4
EXC-4-GW2
DU-1
DU-2
DU-X Surface Soil Sampling Decision Unit
EXC-4-NE
EXC-1-COMP

Tables

GP-1 (4-5')4-5 9/10/21 <0.00607 <0.0121 <0.00243 <0.00243 <0.00243 0.0284 <0.00243 <0.00243 <0.00243 <0.00607 <0.00243 <0.00243 <0.00243 <0.00243 NA <0.00243 <0.00243 <0.00243 NA NA NA NA NA NA NA NA NA NA NA NA
GP-2 (6-7')6-7 9/10/21 <0.00542 <0.00217 <0.00217 <0.00217 <0.00217 0.0131 <0.00217 <0.00217 <0.00217 <0.00542 <0.00217 <0.00217 <0.00217 <0.00217 NA <0.00217 <0.00217 <0.00217 NA NA NA NA NA NA NA NA NA NA NA NA
GP-3 (6-7')6-7 9/10/21 0.130 <0.0111 <0.00223 <0.00223 <0.00223 0.0472 <0.00223 <0.00223 <0.00223 <0.00557 <0.00223 <0.00223 <0.00223 <0.00223 NA <0.00223 <0.00223 <0.00223 NA NA NA NA NA NA NA NA NA NA NA NA
GP-4 (5-6')5-6 9/9/21 <0.00495 <0.0099 <0.00198 <0.00198 <0.00198 0.023 <0.00198 <0.00198 <0.00198 <0.00495 <0.00198 <0.00198 <0.00198 <0.00198 NA <0.00198 <0.00198 <0.00198 NA NA NA NA NA NA NA NA NA NA NA NA
GP-5 (6-7')6-7 9/9/21 <0.00656 <0.0131 <0.00262 <0.00262 <0.00262 0.0545 <0.00262 <0.00262 <0.00262 <0.00656 <0.00262 <0.00262 <0.00262 <0.00262 NA <0.00262 <0.00262 0.0406 NA NA NA NA NA NA NA NA NA NA NA NA
GP-6 (6-7')6-7 9/9/21 <0.00504 <0.0101 <0.00202 <0.00202 <0.00202 0.0115 <0.00202 <0.00202 <0.00202 <0.00504 <0.00202 <0.00202 <0.00202 <0.00202 NA <0.00202 <0.00202 <0.00202 NA NA NA NA NA NA NA NA NA NA NA NA
GP-7 (5-6')5-6 9/10/21 <0.00496 <0.00993 <0.00199 <0.00199 <0.00199 <0.00199 <0.00199 <0.00199 <0.00199 <0.00496 <0.00199 <0.00199 <0.00199 <0.00199 NA <0.00199 <0.00199 <0.00199 NA NA NA NA NA NA NA NA NA NA NA NA
GP-8 (5-6')5-6 9/10/21 <0.00582 <0.0116 <0.00233 <0.00233 <0.00233 <0.00233 <0.00233 <0.00233 <0.00233 <0.00582 <0.00233 <0.00233 <0.00233 <0.00233 NA <0.00233 <0.00233 <0.00233 NA NA NA NA NA NA NA NA NA NA NA NA
GP-9 (2-3')2-3 9/10/21 <0.00541 <0.0108 <0.00217 0.00232 <0.00217 0.0341 <0.00217 <0.00217 <0.00217 <0.00541 0.00679 <0.00217 <0.00217 0.00402 NA <0.00217 <0.00217 0.376 NA NA NA NA NA NA NA NA NA NA NA NA
GP-10 (3-4')3-4 9/10/21 <0.00744 <0.0149 <0.00298 <0.00298 <0.00298 0.0765 <0.00298 <0.00298 <0.00298 <0.00744 0.00348 <0.00298 <0.00298 <0.00298 NA <0.00298 <0.00298 1.29 NA NA NA NA NA NA NA NA NA NA NA NA
GP-11 (3-4')3-4 9/9/21 1.17 <0.783 0.346 1.47 0.388 <0.783 0.299 <0.157 <0.157 0.530 0.106 1.91 2.59 5.71 NA 2.17 1.71 62 NA NA NA NA NA NA NA NA NA NA NA NA
GP-12 (5-6')5-6 9/9/21 <0.0069 0.0409 0.00312 0.00327 <0.00276 0.135 <0.00276 0.0191 <'0.00276 <0.0069 0.00518 <0.00276 0.0129 0.0169 NA <0.00276 <0.00276 1.07 NA NA NA NA NA NA NA NA NA NA NA NA
GP-13 (6-7')6-7 9/9/21 <0.00576 <0.0115 <0.00230 <0.00230 <0.00230 <0.00230 <0.00230 <0.00230 '<0.0023 <0.00576 <0.00230 <0.00230 <0.00230 <0.00230 NA <0.00230 <0.00230 <0.00230 NA NA NA NA NA NA NA NA NA NA NA NA
GP-14 (6-7')6-7 9/9/21 <0.362 <0.724 17.1***63.9 4.63 <0.724 16.8 <0.145 <0.145 <0.362 46.8 19.6 93.7 383 NA <0.145 1.77 1,320 1,100 NA NA NA NA NA NA NA NA NA NA NA
GP-15 (5-6')5-6 9/9/21 <0.363 <0.725 0.239 <0.145 <0.145 <0.145 <0.145 <0.145 '<0.145 <0.363 <0.145 2.11 <0.145 <0.145 NA <0.145 <0.145 44 NA NA NA NA NA NA NA NA NA NA NA NA
GP-16 (5-6')5-6 9/9/21 <0.286 <0.572 6.89**1.57 5.9 <0.572 10.6 <0.114 <0.114 <0.286 28.1 36.8 <0.114 1.47 NA <0.114 <0.114 625 NA NA NA NA NA NA NA NA NA NA NA NA
GP-22 (3-4')3-4 12/16/21 NA NA 26.3***3.78 NA NA NA NA <1.15 NA NA 22.8 NA NA 29.5 NA 49.8 576 15,100 NA NA NA NA NA NA NA NA NA NA NA
GP-22 (9-10')9-10 12/16/21 NA NA 0.0179 0.00966 NA NA NA NA <0.00613 NA NA <0.00613 NA NA 0.0153 NA 0.0448 0.0877 <24.4 NA NA NA NA NA NA NA NA NA NA NA
GP-23 (2-3')2-3 12/16/21 NA NA 1.25 3.49 NA NA NA NA <1.10 NA NA 1.25 NA NA 33.0 NA 3.17 200 6,310 NA NA NA NA NA NA NA NA NA NA NA
GP-23 (4-5')4-5 12/16/21 NA NA 0.0280 <0.00561 NA NA NA NA 0.00788 NA NA <0.00561 NA NA 0.0141 NA 0.0271 0.330 <23.7 NA NA NA NA NA NA NA NA NA NA NA
GP-24 (2-3')2-3 12/16/21 NA NA 1.92 2.61 NA NA NA NA <0.108 NA NA 0.809 NA NA 19.8 NA 13.0 137 5,350 NA NA NA NA NA NA NA NA NA NA NA
GP-24 (4-5)4-5 12/16/21 NA NA 0.0244 <0.00578 NA NA NA NA 0.00818 NA NA <0.00578 NA NA 0.0177 NA 0.0407 0.247 <23.0 NA NA NA NA NA NA NA NA NA NA NA
GP-25 (6-7')6-7 12/16/21 NA NA 0.0175 <0.00598 NA NA NA NA <0.00598 NA NA <0.00598 NA NA 0.0125 NA 0.0358 0.184 <24.5 NA NA NA NA NA NA NA NA NA NA NA
GP-26 (2-3')2-3 12/16/21 NA NA 0.0262 0.130 NA NA NA NA <0.0234 NA NA <0.0234 NA NA 0.631 NA 0.223 6.30 2,500 NA NA NA NA NA NA NA NA NA NA NA
GP-27 (2-3')2-3 12/16/21 NA NA 0.0681 0.209 NA NA NA NA <0.0226 NA NA 0.203 NA NA 1.38 NA 0.0386 11.3 4,580 NA NA NA NA NA NA NA NA NA NA NA
GP-28-8'8 3/9/2023 NA NA <0.002 <0.006 NA NA NA NA <0.002 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 <62 <311 <311 NA NA NA NA NA NA NA NA NA
GP-29'8'8 3/9/2023 NA NA <0.002 <0.006 NA NA NA NA <0.002 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 <62 <311 <311 NA NA NA NA NA NA NA NA NA
GP-30-8'8 3/9/2023 NA NA <0.002 <0.006 NA NA NA NA <0.002 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 <64 <316 <316 NA NA NA NA NA NA NA NA NA
GP-31-5'5 3/9/2023 NA NA 0.01 0.006 NA NA NA NA <0.002 NA NA 0.03 NA NA 0.02 NA <0.005 5.97 924 <305 <305 NA NA NA NA NA NA NA NA NA
GP-32-10'10 3/9/2023 NA NA <0.002 <0.006 NA NA NA NA <0.002 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 <63 <315 <315 NA NA NA NA NA NA NA NA NA
GP-320-10'10 3/9/2023 NA NA <0.003 <0.006 NA NA NA NA <0.003 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 <65 <324 <324 NA NA NA NA NA NA NA NA NA
GP-33-6'6 3/9/2023 NA NA <0.002 <0.006 NA NA NA NA <0.002 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 <63 <314 <314 NA NA NA NA NA NA NA NA NA
MW-1-7'7 3/10/2023 NA NA <0.002 <0.005 NA NA NA NA <0.002 NA NA <0.005 NA NA <0.005 NA <0.005 <0.05 <63 <309 <309 NA NA NA NA NA NA NA NA NA
MW-2-14'14 3/9/2023 NA NA <0.003 <0.007 NA NA NA NA <0.003 NA NA <0.007 NA NA <0.007 NA <0.007 <0.07 <69 <342 <342 NA NA NA NA NA NA NA NA NA
MW-3-12'12 3/9/2023 NA NA <0.002 <0.006 NA NA NA NA <0.002 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 <65 <326 <326 NA NA NA NA NA NA NA NA NA
MW-4-11'11 3/9/2023 NA NA <0.002 <0.005 NA NA NA NA <0.002 NA NA <0.005 NA NA <0.005 NA <0.005 <0.05 <65 <321 <321 NA NA NA NA NA NA NA NA NA
MW-5-15'15 3/9/2023 NA NA <0.002 <0.006 NA NA NA NA <0.002 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 <68 <335 <335 NA NA NA NA NA NA NA NA NA
DU-1 0 3/6/2023 NA NA <0.002 <0.005 NA NA NA NA <0.002 NA NA <0.005 NA NA <0.005 NA <0.005 <0.05 427 1,940 1,270 NA NA NA NA NA NA NA NA NA
DU-2 0 3/6/2023 NA NA <0.003 <0.008 NA NA NA NA <0.003 NA NA <0.008 NA NA <0.008 NA <0.008 <0.08 570 <315 <315 NA NA NA NA NA NA NA NA NA
DU-20 0 3/6/2023 NA NA <0.002 <0.004 NA NA NA NA <0.002 NA NA <0.004 NA NA <0.004 NA <0.004 <0.04 286 281 <281 NA NA NA NA NA NA NA NA NA
DU-3 0 3/6/2023 NA NA <0.003 <0.006 NA NA NA NA <0.003 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 498 435 <290 NA NA NA NA NA NA NA NA NA
DU-4 0 3/6/2023 NA NA <0.002 <0.006 NA NA NA NA <0.002 NA NA <0.006 NA NA <0.006 NA <0.006 <0.06 230 <271 <271 NA NA NA NA NA NA NA NA NA
DU-5 0 3/6/2023 NA NA <0.003 <0.007 NA NA NA NA <0.003 NA NA <0.007 NA NA <0.007 NA <0.007 <0.07 1,420 1,450 716 NA NA NA NA NA NA NA NA NA
TP-1 (2'-3')2-3 6/17/24 NA NA <0.01 <0.03 NA NA NA NA <0.03 NA NA <0.03 NA NA <0.09 NA <0.03 NA NA NA NA <0.29 <0.29 <0.29 <0.29 0.53 11.2 2.46 14.3 <0.24
TP-2 (5'-6')5-6 6/17/24 NA NA 0.75 0.18 NA NA NA NA <0.03 NA NA 1.88 NA NA 0.36 NA <0.03 NA NA NA NA 3.63 13.2 5.85 13.0 2.91 1,330 81.9 44.7 5.14
TP-3 (2'-3')2-3 6/17/24 NA NA <0.08 2.48 NA NA NA NA <0.21 NA NA 0.81 NA NA 17.0 NA 5.28 NA NA NA NA 5.08 6.93 3.64 29.3 26.8 859 320 1,400 <13.1
TP-4 (2'-3')2-3 6/17/24 NA NA 0.10 0.73 NA NA NA NA <0.03 NA NA 0.44 NA NA 3.50 NA 0.14 NA NA NA NA 1.04 3.49 1.51 13.6 11.2 530 112 588 <5.40
TP-5 (4'-5')4-5 6/17/24 NA NA <0.01 <0.03 NA NA NA NA <0.03 NA NA <0.03 NA NA <0.09 NA <0.03 NA NA NA NA <0.30 <0.30 <0.30 <0.30 0.65 20.6 7.11 28.6 <0.26
TP-6 (4'-5')4-5 6/17/24 NA NA <0.01 <0.03 NA NA NA NA <0.03 NA NA <0.03 NA NA <0.09 NA <0.03 NA NA NA NA <0.30 <0.30 <0.30 <0.30 0.67 13.7 1.66 12.1 <0.26
TP-60 (4'-5')4-5 6/17/24 NA NA <0.01 <0.03 NA NA NA NA <0.03 NA NA <0.03 NA NA <0.09 NA <0.03 NA NA NA NA <0.30 <0.30 <0.30 <0.30 0.57 13.7 7.07 31.8 <0.24
DU-1 0 6/17/24 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 5.11 149 44.5 262 <4.00
DU-10 0 6/17/24 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 5.79 167 121 695 <4.00
DU-2 0 6/17/24 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA 5.96 223 644 2,270 <4.00
EXC-4-SW 6 8/7/24 NA NA <0.003 <0.007 NA NA NA NA <0.004 NA NA 0.03 NA NA <0.02 NA <0.007 0.644 <64 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-SE 4 8/12/24 NA NA <0.003 <0.007 NA NA NA NA <0.004 NA NA <0.007 NA NA <0.02 NA <0.007 0.0716 <62 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-West 1 6 8/12/24 NA NA 0.04 0.01 NA NA NA NA <0.004 NA NA 0.007 NA NA 0.04 NA <0.006 0.651 <63 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-Floor 1 8 8/13/24 NA NA 0.02 0.02 NA NA NA NA <0.003 NA NA 0.02 NA NA 0.12 NA <0.005 1.91 77 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-Floor 2 4 8/13/24 NA NA 0.01 0.01 NA NA NA NA <0.004 NA NA 0.007 NA NA 0.15 NA 0.05 1.04 <67 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-East 1 3 8/14/24 NA NA 0.04 <0.007 NA NA NA NA 0.02 NA NA <0.007 NA NA <0.02 NA <0.007 0.33 <63 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-East 10 3 8/14/24 NA NA 0.02 <0.007 NA NA NA NA 0.01 NA NA <0.007 NA NA <0.02 NA <0.007 0.17 <62 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-West 2 6 8/15/24 NA NA 0.11 0.006 NA NA NA NA 0.03 NA NA 0.007 NA NA <0.02 NA <0.006 0.69 <60 NA NA 0.19 0.17 0.08 0.12 <2.41 <2.41 <2.41 23.9 <2.41
EXC-4-NW 6 8/15/24 NA NA <0.002 0.02 NA NA NA NA 0.006 NA NA 0.02 NA NA 0.17 NA <0.006 1.19 <62 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-Floor 3 8 8/15/24 NA NA 0.007 <0.006 NA NA NA NA 0.01 NA NA <0.006 NA NA 0.02 NA <0.006 0.18 <61 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-West 3 6 8/15/24 NA NA <0.12 164 NA NA NA NA <0.18 NA NA 50.4 NA NA 794 NA 3.00 1,500 1,310 NA NA 251 390 181 671 25.4 10.4 12.0 26.5 <2.37
EXC-4-West 4 6 8/19/24 NA NA 4.41 103 NA NA NA NA <1.90 NA NA 28.1 NA NA 604 NA <3.17 3,150 3,640 NA NA 229 313 453 1,420 165 46.6 35.0 35.8 1.92
EXC-4-NE 5 8/19/24 NA NA <0.13 <0.32 NA NA NA NA <0.19 NA NA 0.61 NA NA <0.95 NA <0.32 19.5 10,000 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-East 2 3 8/19/24 NA NA <0.002 <0.006 NA NA NA NA 0.007 NA NA <0.006 NA NA <0.02 NA <0.006 <0.0599 <64 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-Floor 4 5 8/19/24 NA NA <0.002 0.008 NA NA NA NA 0.004 NA NA 0.01 NA NA 0.07 NA <0.006 0.889 <63 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-Floor 40 5 8/19/24 NA NA <0.002 <0.005 NA NA NA NA 0.005 NA NA <0.005 NA NA 0.02 NA <0.005 0.154 <63 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-Floor 5 4 8/19/24 NA NA 0.01 0.06 NA NA NA NA <0.004 NA NA 0.07 NA NA 0.66 NA 0.08 4.38 <62 NA NA NA NA NA NA NA NA NA NA NA
EXC-4-NE2 5 8/22/24 NA NA <0.12 <0.30 NA NA NA NA <0.18 NA NA <0.30 NA NA <0.91 NA <0.30 <3.03 296 NA NA NA NA NA NA NA NA NA NA NA
------0.2 5 ------------0.3 ------51 ------142 ---9 150 500 ---------------------------------
33,000 27,000 1.2 5.8 ---61,000 6,500 770 47 78,000 ---2 640 550 580 6,000 4,900 ------1,000 1,000 ---------------------------
140,000 190,000 5.1 25 ---670,000 27,000 3,500 210 1,200,000 ---8.6 2,800 2,400 2,500 35,000 47,000 ------10,000 10,000 ---------------------------
------8 73,700 ------------77,800 ------5,490 ------10,600 ---5,140 ------------272 606 11,100 35,600 145,000 2,650,000 2,560,000,000 2,560,000,000 1,490,000
------5.13 6,210 ------------340 ------792 ------4,620 ---5,370 ------------3,190 3,190 6,210 2,370 6,280 6,680 136,000 136,000 13,200
NOTES:
Only analytes detected in one or more samples at concentrations above the laboratory reporting limit are presented.
< = Concentration was below the laboratory reporting limit.
NA = Not analyzed.
BOLD = Measured concentration exceeds the applicable U.S. EPA RSL for Residential Soil or Utah ISL.
= Measured concentration exceeds the applicable U.S EPA RSL for Industrial Soil.
U.S. EPA RSL = United States Environmental Protection Agency Regional Screening Level.
= Duplicate sample of the sample above.
SSCLs = Site-Specific Cleanup Levels.
= Area was excavated out and resampled.
* = Measured concentration exceeds the applicable Outdoor Air Vapor Inhalation SSCLs.
** = Measured concentration exceeds the applicable Ingestion of Soil SSCLs.
*** = Measured concentration exceeds the applicable Outdoor Air Vapor Inhalation and Ingestion of Soil SSCLs.
** = Calculated SSCLs are for post remediation exposure risks.
Petroleum Hydrocarbons
all concentrations are expressed in milligrams per kilogram (mg/kg)
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Table 1
Soil Analytical Data - Volatile Organic Compounds and Petroleum Hydrocarbons
647 West 3300 South
Former Sommers Auto Wrecking
South Salt Lake, Utah
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Subsurface Soil Sampling 2021
Utah Initial Screening Levels (ISLs)
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Surface Soil Sampling 2024
Sample
Collection
Date
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EXC-4 Soil Confirmation Sampling 2024
**Outdoor Air Vapor Inhalation SSCLs
Ingestion of Soil SSCLs
--- = Not established.
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U.S. EPA RSLs for Residential Soil
U.S. EPA RSLs for Industrial Soil
TP
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Sample
Depth
(feet)
Sample I.D.
Volatile Organic Compounds
Surface Soil Sampling 2023
GP-1 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-2 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-3 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-4 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-5 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-6 ---------<5.00 <2.00 <2.00 <2.00 <2.00 4.35 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-7 ---------<5.00 <2.00 <2.00 <2.00 <2.00 6.06 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-8 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-9 ---------<50.0 <20.0 <20.0 <20.0 <20.0 <20.0 <20.0 <20.0 <20.0 <20.0 NA <20.0 <200 NA NA NA NA NA
GP-10 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-11 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 2.08 2.31 4.30 NA 2.21 <20.0 NA NA NA NA NA
GP-12 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-13 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-14 ---------69.2 14,200 457 2,910 92.3 <20.0 320 609 2,020 10,700 NA 888 39,700 11,800 NA NA NA NA
GP-15 ---------<50.0 55.9 <20.0 <20.0 <20.00 24.7 <20.0 52.4 <20.0 <20.0 NA <20.0 <200 NA NA NA NA NA
GP-16 ---------<5.00 116 32.6 16.0 14.5 18.5 40.4 92.1 3.79 83.7 NA 2.23 1,020 NA NA NA NA NA
GP-17 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-18 ---------<5.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 <2.00 NA <2.00 <20.0 NA NA NA NA NA
GP-19 ---------NA <10.0 U NA <20.0 NA <20.0 NA <20.0 NA NA <20.0 <20.0 <200 <502 NA NA NA NA
GP-20 ---------NA <10.0 U NA <20.0 NA <20.0 NA <20.0 NA NA <20.0 <20.0 <200 <505 NA NA NA NA
GP-21 ---------NA <10.0 U NA <20.0 NA <20.0 NA <20.0 NA NA <20.0 <20.0 <200 <528 NA NA NA NA
GP-22 ---------NA 2,670 NA 119 NA 183 NA 501 NA NA 232 130 7,860 715,000 NA NA NA NA
GP-23 ---------NA 72 NA 25.8 NA 17.3 NA 8.47 NA NA 184 41.1 620 8,680 NA NA NA NA
GP-24 ---------NA 37.9 NA 12.4 NA 19.2 NA 2.25 NA NA 94 44.1 233 2,400 NA NA NA NA
GP-28 ---------NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
GP-29 ---------NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 5,000 NA NA NA
GP-30 ---------NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
GP-31 ---------NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
GP-32 ---------NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 5,000 NA NA NA
GP-320 ---------NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 6,000 NA NA NA
GP-33 ---------NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
MW-1 95.32 2.74 92.58 NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
MW-2 97.48 1.7 95.78 NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
MW-3 97.98 2.82 95.16 NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
MW-4 96.86 2.45 94.41 NA <5 NA <12 NA 7 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
MW-5 100.00 2.52 97.48 NA <5 NA <12 NA <5 NA <12 NA NA <12 <12 <125 <1,000 <5,000 NA NA NA
EXC-4-GW1 ---8 ---NA 8 NA <12 NA <8 NA <12 NA NA 115 14 345 <1,000 NA NA NA NA
EXC-4-GW2 ---8 ---NA 8 NA <12 NA <8 NA <12 NA NA 118 14 351 <1,000 NA NA NA NA
MW-6 96.69 1.32 95.37 NA <5 NA <12 NA <8 NA <12 NA NA <38 <12 <125 <1,000 NA NA NA NA
MW-7 97.54 7.02 90.52 NA <5 NA 55 NA <8 NA 48 NA NA 190 <12 1,780 1,400 NA 0.142 0.139 <0.125
MW-70 97.54 7.02 90.52 NA <5 NA 55 NA <8 NA 41 NA NA 168 <12 1,730 1,200 NA 0.131 0.147 1.19
---5 ---700 ---200 ---700 ------10,000 1,000 1,000 1,000 10,000 ---------
---283,000 ---1,070,000,000 ---262,000,000 ---3,300,000 93,700,000 93,700,000 93,700,000 4,780,000,000 ---------207,000,000 251,000,000 230,000,000
---5 ---700 ------------10,000 10,000 10,000 1,000 ------------------
NOTES:
Only analytes detected in one or more samples at concentrations above the laboratory reporting limit are presented.
< = Concentration was below the laboratory reporting limit.
NA = Not analyzed.
BOLD = Measured concentration exceeds the applicable Utah Initial Screening Level.
= Measured concentration exceeds the applicable U.S. EPA MCL.
U = The laboratory reporting limit exceeded the Utah ISL/U.S. EPA MCL, but the analyte was not detected above the laboratory method detection limit which is below the Utah ISL/U.S. EPA MCL.
= Duplicate sample of the sample above.
SSCLs = Site-Specific Cleanup Levels.
** = Calculated SSCLs are for post remediation exposure risks.
Groundwater Analytical Data - Volatile Organic Compounds and Petroleum Hydrocarbons
Table 2
**Outdoor Air Vapor Inhalation Calculated SSCLs
all concentrations are expressed in micrograms per liter (µg/L)
South Salt Lake, Utah
647 West 3300 South
Former Sommers Auto Wrecking
Sample I.D.
3/9/2023
3/20/2023
3/20/2023
3/20/2023
3/9/2023
3/9/2023
3/9/2023
3/9/2023
3/9/2023
9/10/21
9/10/21
--- = Not established or not applicable.
12/16/21
12/16/21
3/20/2023
Groundwater Sampling 2023
10/7/2024
10/7/2024
10/7/2024
Grounwater Sampling 2024
8/19/2024
8/19/2024
3/9/2023
3/20/2023
Utah Initial Screening Levels
U.S. EPA Maximum Contaminant Level (MCL)
9/9/21
9/10/21
9/9/21
9/9/21
9/9/21
9/10/21
9/10/21
9/10/21
9/10/21
9/9/21
9/9/21
12/20/21
12/20/21
12/16/21
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Volatile Organic Compounds Petroleum Hydrocarbons
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Groundwater Sampling 2021
9/9/21
9/10/21
9/10/21
Top-of-
Casing
Elevation
Depth to
Water
(feet)
Groundwater
Elevation
(feet)
9/9/21
Sample
Collection
Date
Ar
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EXC-1-Comp **0.5 8/22/24 10.3 NA NA NA 290 NA NA NA NA NA
EXC-1-1 0.5 9/20/24 NA NA NA NA 131 NA NA NA NA NA
EXC-1-2 0.5 9/20/24 NA NA NA NA 628 NA NA NA NA NA
EXC-1-3 0.5 9/20/24 NA NA NA NA 159 NA NA NA NA NA
EXC-1-4 0.5 9/20/24 NA NA NA NA 629 NA NA NA NA NA
EXC-1-5 0.5 9/20/24 NA NA NA NA 599 NA NA NA NA NA
EXC-1-6 0.5 9/20/24 NA NA NA NA 198 NA NA NA NA NA
EXC-1-7 0.5 9/20/24 NA NA NA NA 279 NA NA NA NA NA
EXC-1-8 0.5 9/20/24 NA NA NA NA 112 NA NA NA NA NA
EXC-1-9 0.5 9/20/24 NA NA NA NA 141 NA NA NA NA NA
EXC-1-10 0.5 9/20/24 NA NA NA NA 223 NA NA NA NA NA
EXC-1-11 0.5 9/20/24 NA NA NA NA 309 NA NA NA NA NA
EXC-1-12 0.5 9/20/24 NA NA NA NA 536 NA NA NA NA NA
EXC-1-13 0.5 9/20/24 NA NA NA NA 303 NA NA NA NA NA
EXC-1-130 0.5 9/20/24 NA NA NA NA 420 NA NA NA NA NA
EXC-1-14 0.5 9/20/24 NA NA NA NA 411 NA NA NA NA NA
EXC-1-15 0.5 9/20/24 NA NA NA NA 272 NA NA NA NA NA
EXC-1-16 0.5 9/20/24 NA NA NA NA 188 NA NA NA NA NA
EXC-1-160 0.5 9/20/24 NA NA NA NA 213 NA NA NA NA NA
EXC-2-N 2 8/20/24 24.4 NA NA NA 668 NA NA NA NA NA
EXC-2-E 2 8/20/24 21.9 NA NA NA 643 NA NA NA NA NA
EXC-2-SE 2 8/20/24 22.6 NA NA NA 165 NA NA NA NA NA
EXC-2-S 2 8/20/24 12.6 NA NA NA 312 NA NA NA NA NA
EXC-2-W 2 8/20/24 16.8 NA NA NA 352 NA NA NA NA NA
EXC-2-W2 2 8/20/24 13.9 NA NA NA 293 NA NA NA NA NA
EXC-2-Floor 4 8/20/24 16.6 NA NA NA 221 NA NA NA NA NA
EXC-3-N 3 8/22/24 15.9 NA NA NA 121 NA NA NA NA NA
EXC-3-E 3 8/22/24 16.2 NA NA NA 183 NA NA NA NA NA
EXC-3-S 3 8/22/24 21.4 NA NA NA 766 NA NA NA NA NA
EXC-3-W 3 8/22/24 15.5 NA NA NA 120 NA NA NA NA NA
EXC-3-Floor 5 8/22/24 11.0 NA NA NA 47.5 NA NA NA NA NA
EXC-3-Floor 10 5 8/22/24 11.6 NA NA NA 107 NA NA NA NA NA
0.68 15,000 71 120,000 200 ---390 390 0.17 0.24
3 220,000 980 1,800,000 800 ---5,800 5,800 0.72 0.99
45 ---------------------------
NOTES:
= Duplicate sample of the sample above.
U.S. EPA RSL = United States Environmenatl Protection Agency Regional Screening Level.
* = Measured concentration exceeds the DERR-approved Arsenic Cleanup Level.
** = Composite surface soil sample of area under the removed concrete within this excavation area.
BOLD = Measured concentration exceeds the applicable U.S. EPA RSL for Residential So
= Measured concentration exceeds the applicable U.S EPA RSL for Industrial Soil.
--- = Not established.
NA = Not Analyzed.
Only analytes detected in one or more samples at concentrations that exceed the laboratory reporting limit are presented.
< = Concentration was below the laboratory reporting limit.
EXC-1 Soil Confirmation Sampling 2024
U.S. EPA RSL for Soil
DERR-Approved Arsenic Cleanup Level
Polychlorinated
Biphenyls
Sample I.D.
Sample
Depth
(feet)
Sample
Collection
Date
Metals
EXC-2 Soil Confirmation Sampling 2024
EXC-3 Soil Confirmation Sampling 2024
U.S. EPA RSL for Industrial Soil
all concentrations are expressed in milligrams per kilogram (mg/kg)
Table 3
Soil Analytical Data - Total Metals and PCBs
Former Sommers Auto Wrecking
647 West 3300 South
South Salt Lake, Utah
Ar
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Ba
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Ch
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Se
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Si
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GP-1 9/10/21 0.0349 0.140 <0.0400 <0.00200 <0.00200 <0.00200
GP-2 9/10/21 0.0212 0.179 <0.0400 <0.00200 <0.00200 <0.00200
GP-3 9/10/21 0.154 0.0970 <0.0400 <0.00200 <0.00200 <0.00200
GP-4 9/9/21 0.0276 0.0782 <0.0400 <0.00200 <0.00200 <0.00200
GP-5 9/9/21 0.0607 0.100 <0.0400 <0.00200 <0.00200 <0.00200
GP-6 9/9/21 0.0706 0.120 <0.0400 <0.00200 <0.00200 <0.00200
GP-7 9/10/21 0.159 0.123 <0.0400 <0.00200 <0.00200 <0.00200
GP-8 9/10/21 0.151 0.206 <0.0400 <0.00200 <0.00200 <0.00200
GP-9 9/10/21 0.254 0.270 <0.0400 <0.00200 <0.00200 <0.00200
GP-10 9/10/21 0.0367 0.0242 <0.0400 <0.00200 <0.00200 <0.00200
GP-11 9/9/21 0.0194 0.0685 <0.0400 <0.00200 <0.00200 <0.00200
GP-12 9/9/21 0.0947 0.0980 <0.0400 <0.00200 <0.00200 <0.00200
GP-13 9/9/21 0.0552 0.0804 <0.0400 <0.00200 <0.00200 <0.00200
GP-14 9/9/21 0.307 0.332 <0.0400 <0.00200 <0.00200 <0.00200
GP-15 9/9/21 0.373 0.185 <0.0400 <0.00200 <0.00200 <0.00200
GP-16 9/9/21 0.254 0.159 <0.0400 <0.00200 <0.00200 <0.00200
GP-17 9/10/21 0.1220 0.0901 <0.0400 <0.00200 <0.00200 <0.00200
GP-18 9/10/21 0.0131 0.0778 <0.0400 0.00212 <0.00200 <0.00200
GP-19 12/20/21 0.0736 NA NA NA NA NA
GP-20 12/20/21 0.110 NA NA NA NA NA
GP-21 12/20/21 0.126 NA NA NA NA NA
GP-28 3/9/2023 <0.0500 0.120 <0.0050 <0.0200 <0.0500 <0.005
GP-29 3/9/2023 0.0613 0.197 0.0088 0.0480 0.0082 <0.005
GP-30 3/9/2023 0.101 0.148 <0.0050 <0.0200 0.0168 <0.005
GP-31 3/9/2023 <0.0500 0.081 <0.0050 <0.0200 <0.0116 <0.005
GP-32 3/9/2023 <0.0500 0.151 <0.0050 <0.0200 0.0070 <0.005
GP-320 3/9/2023 <0.0500 0.149 <0.0050 <0.0200 0.0149 <0.005
GP-33 3/9/2023 <0.0500 0.105 <0.0050 <0.0200 <0.0500 <0.005
MW-1 3/20/2023 0.0178 0.106 <0.0005 <0.0005 <0.0005 <0.0005
MW-2 3/20/2023 0.0591 0.0851 <0.0005 0.0007 0.0008 0.0005
MW-3 3/20/2023 0.109 0.183 <0.0005 0.0005 <0.0005 <0.0005
MW-4 3/20/2023 0.157 0.150 <0.0005 <0.0005 0.0007 <0.0005
MW-5 3/20/2023 0.182 0.103 <0.0005 <0.0005 <0.0005 <0.0005
0.01 2 0.1 0.015 0.05 ---
0.05 2 0.1 0.015 0.05 0.10
NOTES:
Only analytes that were detected in one or more samples at concentrations that exceed the laboratory reporting
limit are presented.
< = Concentration was below the laboratory reporting limit.
NA = Not analyzed.
U.S. EPA = United States Environmenatl Protection Agency.
BOLD = Measured concentration exceeds the applicable U.S. EPA MCL.
= Measured concentration exceeds applicable Utah Groundwater Quality Standard.
= Duplicate sample of the sample above.
Utah Groundwater Quality Standards
U.S. EPA Maximum Contaminant Levels
Groundwater Sampling 2021
Table 4
Groundwater Sampling 2023
Sample I.D.Sample Collection Date
Metals
all concentrations are expressed in milligrams per liter (mg/L)
South Salt Lake, Utah
647 West 3300 South
Former Sommers Auto Wrecking
Groundwater Analytical Data - Dissolved Metals
GP-1 (4-5')4-5 9/10/21 <0.00844 <0.00844 <0.00844 <0.00844 <0.00844 <0.0169 <0.00844 <0.00844 <0.00844 <0.00844 <0.00844 <0.00844 <0.00844 <0.00844 <0.00844 <0.00844 <0.00844 <0.0169 <0.00844
GP-2 (6-7')6-7 9/10/21 <0.00825 <0.00825 <0.00825 <0.00825 <0.00825 <0.0165 <0.00825 <0.00825 <0.00825 <0.00825 <0.00825 <0.00825 <0.00825 <0.00825 <0.00825 <0.00825 <0.00825 <0.0165 <0.00825
GP-3 (6-7')6-7 9/10/21 <0.00848 <0.00848 <0.00848 <0.00848 <0.00848 <0.017 <0.00848 <0.00848 <0.00848 <0.00848 <0.00848 <0.00848 <0.00848 <0.00848 <0.00848 <0.00848 <0.00848 <0.017 <0.00848
GP-4 (5-6')5-6 9/9/21 0.0160 0.0152 <0.00776 <0.00776 <0.00776 0.0179 0.0212 0.0158 0.0286 <0.00776 0.033 <0.00776 0.036 <0.00776 <0.00776 <0.00776 0.014 0.032 0.0516
GP-5 (6-7')6-7 9/9/21 <0.00799 <0.00799 <0.00799 <0.00799 <0.00799 <0.016 <0.00799 <0.00799 <0.00799 <0.00799 <0.00799 <0.00799 <0.00799 <0.00799 <0.00799 <0.00799 <0.00799 <0.016 <0.00799
GP-6 (6-7')6-7 9/9/21 <0.00759 <0.00759 <0.00759 <0.00759 <0.00759 <0.0152 <0.00759 <0.00759 <0.00759 <0.00759 <0.00759 <0.00759 <0.00759 <0.00759 <0.00759 <0.00759 <0.00759 <0.0152 <0.00759
GP-7 (5-6')5-6 9/10/21 <0.00827 <0.00827 <0.00827 <0.00827 <0.00827 <0.0165 <0.00827 <0.00827 <0.00827 <0.00827 <0.00827 <0.00827 <0.00827 <0.00827 <0.00827 <0.00827 <0.00827 <0.0165 <0.00827
GP-8 (5-6')5-6 9/10/21 <0.00836 <0.00836 <0.00836 <0.00836 <0.00836 <0.0167 <0.00836 <0.00836 <0.00836 <0.00836 <0.00836 <0.00836 <0.00836 <0.00836 <0.00836 <0.00836 <0.00836 <0.0167 <0.00836
GP-9 (2-3')2-3 9/10/21 0.0287 0.0542 <0.00707 <0.00707 <0.00707 <0.0141 0.0699 <0.00707 <0.00707 0.0292 0.059 <0.00707 0.021 <0.00707 <0.00707 <0.00707 0.039 0.0216 0.105
GP-10 (3-4')3-4 9/10/21 0.196 0.239 <0.00760 <0.00760 0.00941 <0.0152 <0.00760 <0.00760 <0.00760 <0.00760 <0.00760 <0.00760 <0.00760 <0.00760 <0.00760 <0.00760 0.141 <0.0152 <0.00760
GP-11 (3-4')3-4 9/9/21 0.482 0.835 <0.00679 <0.00679 <0.00679 <0.00679 <0.00679 <0.00679 <0.00679 <0.00679 <0.00679 0.014 <0.00679 <0.00679 0.031 <0.00679 0.464 <0.0136 <0.00679
GP-12 (5-6')5-6 9/9/21 <0.00854 <0.00854 <0.00854 <0.00854 <0.00854 <0.0171 <0.00854 <0.00854 <0.00854 <0.00854 <0.00854 <0.00854 <0.00854 <0.00854 <0.00854 <0.00854 <0.00854 <0.0171 <0.00854
GP-13 (6-7')6-7 9/9/21 <0.00856 <0.00856 <0.00856 <0.00856 <0.00856 <0.0171 <0.00856 <0.00856 <0.00856 <0.00856 <0.00856 <0.00856 <0.00856 <0.00856 <0.00856 <0.00856 0.016 <0.0171 <0.00856
GP-14 (6-7')6-7 9/9/21 0.821 1.44 0.0355 0.0098 0.0177 0.0207 0.0195 0.0178 0.0117 <0.00834 0.0284 <0.00834 0.0566 0.0564 0.112 <0.00834 1.40 0.181 0.083
GP-15 (5-6')5-6 9/9/21 7.09 10 0.482 0.484 3.97 <0.0166 <0.00828 <0.00828 <0.00828 <0.00828 0.0492 <0.00828 0.203 0.353 0.0093 <0.00828 2.43 <0.0166 0.123
GP-16 (5-6')5-6 9/9/21 7.52 12.6 0.321 0.0952 0.0958 0.0462 0.160 0.0598 0.0112 0.0145 0.164 0.0089 0.206 0.491 0.135 0.0317 8.36 <0.0168 0.369
TP-1 (2'-3')2-3 6/17/24 NA NA <0.49 <0.49 <0.49 <0.49 <0.49 <0.49 <0.49 <0.49 <0.49 NA <0.49 <0.49 NA <0.49 <0.03 <0.49 <0.49
TP-2 (5'-6')5-6 6/17/24 NA NA <1.50 <1.50 <1.50 <1.50 <1.50 <1.50 <1.50 <1.50 <1.50 NA <1.50 <1.50 NA <1.50 <1.50 3.44 <1.50
TP-3 (2'-3')2-3 6/17/24 NA NA <26.3 <26.3 <26.3 <26.3 <26.3 <26.3 <26.3 <26.3 <26.3 NA <26.3 <26.3 NA <26.3 <26.3 <26.3 <26.3
TP-4 (2'-3')2-3 6/17/24 NA NA <10.8 <10.8 <10.8 <10.8 <10.8 <10.8 <10.8 <10.8 <10.8 NA <10.8 <10.8 NA <10.8 <10.8 <10.8 <10.8
TP-5 (4'-5')4-5 6/17/24 NA NA <0.51 <0.51 <0.51 <0.51 <0.51 <0.51 <0.51 <0.51 <0.51 NA <0.51 <0.51 NA <0.51 <0.51 <0.51 <0.51
TP-6 (4'-5')4-5 6/17/24 NA NA <0.53 <0.53 <0.53 <0.53 <0.53 <0.53 <0.53 <0.53 <0.53 NA <0.53 <0.53 NA <0.53 <0.53 <0.53 <0.53
TP-60 (4'-5')4-5 6/17/24 NA NA <0.49 <0.49 <0.49 <0.49 <0.49 <0.49 <0.49 <0.49 <0.49 NA <0.49 <0.49 NA <0.49 <0.49 <0.49 <0.49
DU-1 0 6/17/24 NA NA <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 NA <8.00 <8.00 NA <8.00 <8.00 <8.00 <8.00
DU-10 0 6/17/24 NA NA <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 NA <8.00 <8.00 NA <8.00 <8.00 <8.00 <8.00
DU-2 0 6/17/24 NA NA <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 <8.00 NA <8.00 <8.00 NA <8.00 <8.00 <8.00 <8.00
18 240 3,600 ---18,000 1.1 0.11 1.1 ---11 110 0.11 2,400 2,400 ---1.1 2 ---1,800
73 3,000 45,000 ---230,000 21 2 21 ---210 2,100 2.1 30,000 30,000 ---21 8.6 ---23,000
NOTES:
< = Concentration was below the laboratory reporting limit.
BOLD = Concentration exceeds the United States Environmental Protection Agency (U.S. EPA) Refional Screening Level (RSL) for Residential Soil.
all concentrations are expressed in milligrams per kilogram (mg/kg)
Table 5
Soil Analytical Data - Polycyclic Aromatic Hydrocarbons
Former Sommers Auto Wrecking
647 West 3300 South
South Salt Lake, Utah
Be
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,
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)
p
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Sample I.D.
Sample
Depth
(feet)
Sample
Collection
Date
1-
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U.S. EPA RSL for Industrial Soil
--- = Not established.
Soil Sampling 2024
U.S. EPA RSL for Soil
Soil Sampling 2021

Appendix A
DERR Calculator Documents

Page 1 of 3
SSCL Calculator Prepared for:SSCL Calculator Prepared by:
Site name:
Site address:
Facility ID:
Release ID:
Contact name:
Contact phone:
Contact e-mail:
Site-Specific Cleanup Levels* for Commercial/ Industrial Receptors
Air Groundwater Soil
SSCLair SSCLwing SSCLwesp SSCLwamb SSCLs-leach SSCLsesp SSCLsamb SSCLss
(See Eq. D.1)(See Eq. D.2)(See Eq. D.3)(See Eq. D.4)(See Eq. D.5)(See Eq. D.6)(See Eq. D.7)(See Eq. D.8)
Air Groundwater Groundwater Groundwater Subsurface soil Subsurface soil Subsurface soil Surface Soil
Inhalation Ingestion Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Leaching to
groundwater
(groundwater
ingestion)
Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Ingestion of soil,
inhalation of
vapors and
particles, and
dermal contact
µg/m3 air µg/m3 air mg/L water mg/L water mg/L water mg/L water mg/kg soil mg/kg soil mg/kg soil mg/kg soil mg/kg soil
Benzene (71-43-2)c 4.93E-01 9.87E-03 3.53E+00 2.83E+02 4.30E-03 7.21E-01 8.00E+00 5.13E+00
Toluene (108-88-3)nc 7.31E+03 8.18E+00 5.27E+04 4.78E+06 7.26E+00 1.85E+04 2.06E+05 5.37E+03
Ethylbenzene (100-41-4)nc 1.48E+03 1.02E+01 1.09E+04 1.07E+06 1.82E+01 6.65E+03 7.37E+04 6.21E+03
Xylenes (1330-20-7)nc 1.48E+02 2.04E+01 1.12E+03 9.37E+04 3.93E+01 9.60E+02 1.06E+04 4.62E+03
Naphthalene (91-20-3)nc 4.39E+00 2.04E+00 2.03E+02 3.30E+03 5.46E+00 4.95E+02 5.49E+03 7.92E+02
MTBE (1634-04-04)nc 4.38E+03 5.11E-01 3.25E+04 2.62E+05 1.13E-01 7.02E+03 7.78E+04 3.40E+02
Alkyl benzenes (C9-C10)
[average values]nc 3.07E+02 4.09E+00 2.36E+03 2.30E+05 1.60E+01 3.21E+03 3.56E+04 2.37E+03 29.3 TP-3 (2'-3')
Alkyl naphthalenes (C11-C13)
[average values]nc 3.07E+02 4.09E+00 1.34E+04 2.25E+05 8.57E+01 2.57E+05 2.85E+06 1.86E+04 0.15 Non-detect in all samples
Total PAHs (C12-C22)
[average values]nc 1.53E+02 3.07E+00 1.05E+03 5.20E+04 5.68E+02 1.34E+05 1.49E+06 1.32E+04 5.14 TP-2 (5'-6')
Aliphatics (C5-C6)
[Hexane (110-54-3)]nc 3.07E+02 6.13E+00 1.41E+03 2.07E+05 2.49E+01 2.45E+01 2.72E+02 3.19E+03 5.08 TP-3 (2'-3')
Aliphatics (C7-C8)
[Heptane (142-82-5)]nc 3.07E+02 6.13E+00 1.70E+03 2.51E+05 8.15E+01 5.47E+01 6.06E+02 3.19E+03 6.93 TP-3 (2'-3')
Aliphatics (C9-C10)
[Nonane (111-84-2)]nc 1.48E+03 1.02E+01 9.59E+03 1.41E+06 1.03E+03 1.00E+03 1.11E+04 6.21E+03 5.85 TP-2 (5'-6')
Aliphatics (C11-C12)
[Undecane (1120-21-4)]nc 1.48E+03 1.02E+01 1.09E+04 1.61E+06 9.59E+03 1.31E+04 1.45E+05 6.28E+03 26.8 TP-3 (2'-3')
Aliphatics (C13-C16)
[Hexadecane (544-76-3)]nc 1.48E+03 1.02E+01 1.26E+04 1.85E+06 1.50E+05 2.39E+05 2.65E+06 6.68E+03 1330 TP-2 (5'-6')
Aliphatics (C17-C21)
[Heptadecane (629-78-7)]nc 1.02E+04 2.04E+02 1.04E+05 1.53E+07 2.41E+08 2.30E+08 2.56E+09 1.36E+05 320 TP-3 (2'-3')
Aliphatics (C22-C35)
[Heptadecane (629-78-7)]nc 1.02E+04 2.04E+02 1.04E+05 1.53E+07 2.41E+08 2.30E+08 2.56E+09 1.36E+05 1400 TP-3 (2'-3')
435-760-8269
[e-mail]
Blake Downey
C-0268
Wasatch Environmental
435-760-8269
[e-mail]
Date prepared:7/3/2024
Sommers Auto Wrecking
647 W 3300 S
Blake Downey
Soil
Comments
(e.g. Sample ID,
Sample Depth,
Sample Date, etc.)
Highest
Soil
Concentrations
Remaining at the
Site
Name:
Company, Agency, other:
Phone:
E-mail:
UST Consultant Cert. #:
Highest
Air
Concentrations
Remaining at the
Site
Air
Comments
(e.g. Sample ID,
Sample Date, etc.)
Groundwater Comments
(e.g. Sample ID,
Sample Date, etc.)Chemical Name (CAS #)
Pr
i
m
a
r
y

C
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m
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a
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s

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H
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d
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o
c
a
r
b
o
n

F
r
a
c
t
i
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n
s
Highest
Groundwater
Concentrations
Remaining at the
Site
DERRsRBCASSCCalculatorv for Test Pits Page 1 of 3
12/12/2024
9:14 AM
Page 2 of 3
Site-Specific Cleanup Levels* for Commercial/ Industrial Receptors
Air Groundwater Soil
SSCLair SSCLwing SSCLwesp SSCLwamb SSCLs-leach SSCLsesp SSCLsamb SSCLss
(See Eq. D.1)(See Eq. D.2)(See Eq. D.3)(See Eq. D.4)(See Eq. D.5)(See Eq. D.6)(See Eq. D.7)(See Eq. D.8)
Air Groundwater Groundwater Groundwater Subsurface soil Subsurface soil Subsurface soil Surface Soil
Inhalation Ingestion Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Leaching to
groundwater
(groundwater
ingestion)
Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Ingestion of soil,
inhalation of
vapors and
particles, and
dermal contact
µg/m3 air µg/m3 air mg/L water mg/L water mg/L water mg/L water mg/kg soil mg/kg soil mg/kg soil mg/kg soil mg/kg soil
Soil
Comments
(e.g. Sample ID,
Sample Depth,
Sample Date, etc.)
Highest
Soil
Concentrations
Remaining at the
Site
Highest
Air
Concentrations
Remaining at the
Site
Air
Comments
(e.g. Sample ID,
Sample Date, etc.)
Groundwater Comments
(e.g. Sample ID,
Sample Date, etc.)Chemical Name (CAS #)

Highest
Groundwater
Concentrations
Remaining at the
Site
Acenaphthylene (208-96-8)nc 1.53E+02 3.07E+00 1.43E+04 1.15E+05 2.56E+01 1.16E+05 1.28E+06 1.31E+04
Acenaphthene (83-32-9)nc 8.69E+01 6.13E+00 7.43E+03 6.36E+04 4.41E+01 5.18E+04 5.74E+05 1.74E+04
Fluorene (86-73-7)nc 5.62E+01 4.09E+00 5.26E+03 4.02E+04 4.77E+01 5.98E+04 6.63E+05 1.29E+04
Phenanthrene (85-01-8)nc 1.53E+02 3.07E+00 1.66E+04 1.16E+05 7.40E+01 3.92E+05 4.35E+06 1.42E+04
Anthracene (120-12-7)nc 4.38E+02 3.07E+01 4.52E+04 3.19E+05 7.00E+02 1.01E+06 1.12E+07 1.12E+05
Fluoranthene (206-44-0)nc 5.83E+01 4.09E+00 7.73E+03 5.16E+04 3.35E+02 6.22E+05 6.90E+06 1.76E+04
Pyrene (129-00-0)nc 4.38E+01 3.07E+00 5.13E+03 3.41E+04 2.32E+02 3.82E+05 4.24E+06 1.30E+04
Benz(a)Anthracene (56-55-3)c 1.96E-01 3.92E-04 1.85E+01 1.23E+02 1.18E-01 5.45E+03 6.05E+04 2.00E+00
Chrysene (218-01-09)c 1.96E+00 3.92E-02 2.70E+02 1.78E+03 9.40E+00 6.36E+04 7.05E+05 1.95E+02
Benzo(b)Fluoranthene (205-99-2)c 1.96E-02 3.92E-04 2.92E+00 1.98E+01 9.58E-02 7.01E+02 7.77E+03 1.95E+00
Benzo(k)-Fluoranthene (207-08-09)c 1.96E-01 3.92E-03 3.04E+01 1.98E+02 1.40E+00 1.06E+04 1.18E+05 1.96E+01
Benzo(a)-Pyrene (50-32-8)c 2.35E-03 3.92E-05 2.24E-01 1.47E+00 1.51E-02 8.51E+01 9.44E+02 1.96E-01
Indeno(1, 2, 3-Cd)Pyrene (193-39-
5)c 2.35E-02 3.92E-04 1.14E+03 1.16E+03 9.30E-03 2.57E+04 2.68E+04 1.88E+00
Dibenzo-(a, h)Anthracene (53-70-
3)c 2.35E-02 3.92E-04 3.86E+00 2.52E+01 8.55E-01 8.27E+03 9.17E+04 1.99E+00
Benzo (g, h, i)-Perylene (191-24-2)nc 1.53E+02 3.07E+00 2.37E+04 1.55E+05 2.81E+03 2.13E+07 2.36E+08 1.55E+04
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not usedAd
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(
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DERRsRBCASSCCalculatorv for Test Pits Page 2 of 3
12/12/2024
9:14 AM
Page 3 of 3
Site-Specific Cleanup Levels* for Commercial/ Industrial Receptors
Air Groundwater Soil
SSCLair SSCLwing SSCLwesp SSCLwamb SSCLs-leach SSCLsesp SSCLsamb SSCLss
(See Eq. D.1)(See Eq. D.2)(See Eq. D.3)(See Eq. D.4)(See Eq. D.5)(See Eq. D.6)(See Eq. D.7)(See Eq. D.8)
Air Groundwater Groundwater Groundwater Subsurface soil Subsurface soil Subsurface soil Surface Soil
Inhalation Ingestion Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Leaching to
groundwater
(groundwater
ingestion)
Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Ingestion of soil,
inhalation of
vapors and
particles, and
dermal contact
µg/m3 air µg/m3 air mg/L water mg/L water mg/L water mg/L water mg/kg soil mg/kg soil mg/kg soil mg/kg soil mg/kg soil
Soil
Comments
(e.g. Sample ID,
Sample Depth,
Sample Date, etc.)
Highest
Soil
Concentrations
Remaining at the
Site
Highest
Air
Concentrations
Remaining at the
Site
Air
Comments
(e.g. Sample ID,
Sample Date, etc.)
Groundwater Comments
(e.g. Sample ID,
Sample Date, etc.)Chemical Name (CAS #)

Highest
Groundwater
Concentrations
Remaining at the
Site
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
* - Site-Specific Cleanup Levels assume a Natural Attenuation Factor of 1 (i.e. no natural attenuation). c - carcinogen; nc - non-carcinogen
Site-specific Parameters used in Calculations
Parameter Comments
Soil
Receptor
i
Lgw
Ls
Pavement
Precip.
Soil Zone
W
inches/year
Not applicable
ft
Units
Not applicable
Not applicable
ft-vertical/ft-lateral
ft
Not applicable
ft
15.38
Yes
145
Value
Clay
Commercial/ Industrial
0.07
5
4
UNPAVED: contamination beneath
bare soils
Depth to groundwater
Hydraulic gradient
Select the most sensitive Receptor that is present at the site
Soil type representative of site
Description
Width of contaminated source area parallel to groundwater flow or wind direction
Annual precipitation
Is contamination present in the saturated zone?
Is contamination beneath pavement or bare soils?
Depth to contaminated soil
Ad
d
i
t
i
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DERRsRBCASSCCalculatorv for Test Pits Page 3 of 3
12/12/2024
9:14 AM
Page 1 of 3
SSCL Calculator Prepared for:SSCL Calculator Prepared by:
Site name:
Site address:
Facility ID:
Release ID:
Contact name:
Contact phone:
Contact e-mail:
Site-Specific Cleanup Levels* for Commercial/ Industrial Receptors
Air Groundwater Soil
SSCLair SSCLwing SSCLwesp SSCLwamb SSCLs-leach SSCLsesp SSCLsamb SSCLss
(See Eq. D.1)(See Eq. D.2)(See Eq. D.3)(See Eq. D.4)(See Eq. D.5)(See Eq. D.6)(See Eq. D.7)(See Eq. D.8)
Air Groundwater Groundwater Groundwater Subsurface soil Subsurface soil Subsurface soil Surface Soil
Inhalation Ingestion Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Leaching to
groundwater
(groundwater
ingestion)
Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Ingestion of soil,
inhalation of
vapors and
particles, and
dermal contact
µg/m3 air µg/m3 air mg/L water mg/L water mg/L water mg/L water mg/kg soil mg/kg soil mg/kg soil mg/kg soil mg/kg soil
Benzene (71-43-2)c 4.93E-01 9.87E-03 3.56E+00 8.36E+02 0.008 EXC-4-GW1/2 4.70E-03 7.21E-01 2.32E+01 5.99E+00 1.92 GP-24
Toluene (108-88-3)nc 7.31E+03 8.18E+00 5.31E+04 1.40E+07 0.014 EXC-4-GW1/2 7.93E+00 1.85E+04 5.96E+05 5.42E+03 13.00 GP-24
Ethylbenzene (100-41-4)nc 1.48E+03 1.02E+01 1.09E+04 3.13E+06 0.055 MW-7 1.99E+01 6.65E+03 2.14E+05 6.59E+03 3.49 GP-23
Xylenes (1330-20-7)nc 1.48E+02 2.04E+01 1.13E+03 2.76E+05 0.19 EXC-4-GW1/2 4.29E+01 9.60E+02 3.09E+04 8.15E+03 33 GP-23
Naphthalene (91-20-3)nc 4.39E+00 2.04E+00 2.06E+02 1.11E+04 0.048 MW-7 5.96E+00 4.95E+02 1.59E+04 2.01E+03 1.88 TP-2 (5'-6')
MTBE (1634-04-04)nc 4.38E+03 5.11E-01 3.31E+04 1.03E+06 Non-detect in all samples 1.24E-01 7.02E+03 2.26E+05 3.40E+02 0.00818 GP-24
Alkyl benzenes (C9-C10)
[average values]nc 3.07E+02 4.09E+00 2.37E+03 6.73E+05 0.00119 MW-7 1.75E+01 3.21E+03 1.03E+05 2.59E+03 29.3 TP-3 (2'-3')
Alkyl naphthalenes (C11-C13)
[average values]nc 3.07E+02 4.09E+00 1.37E+04 7.56E+05 Not Evaluated 9.36E+01 2.57E+05 8.26E+06 2.01E+04 0.15 Non-detect in all samples
Total PAHs (C12-C22)
[average values]nc 1.53E+02 3.07E+00 1.07E+03 1.57E+05 Not Evaluated 6.21E+02 1.34E+05 4.31E+06 1.48E+04 5.14 TP-2 (5'-6')
Aliphatics (C5-C6)
[Hexane (110-54-3)]nc 3.07E+02 6.13E+00 1.41E+03 6.00E+05 0.00142 MW-7 2.72E+01 2.45E+01 7.89E+02 3.73E+03 5.08 TP-3 (2'-3')
Aliphatics (C7-C8)
[Heptane (142-82-5)]nc 3.07E+02 6.13E+00 1.70E+03 7.26E+05 0.00147 MW-7 8.91E+01 5.47E+01 1.76E+03 3.73E+03 6.93 TP-3 (2'-3')
Aliphatics (C9-C10)
[Nonane (111-84-2)]nc 1.48E+03 1.02E+01 9.59E+03 4.10E+06 Non-detect in all samples 1.13E+03 1.00E+03 3.23E+04 6.59E+03 5.85 TP-2 (5'-6')
Aliphatics (C11-C12)
[Undecane (1120-21-4)]nc 1.48E+03 1.02E+01 1.09E+04 4.66E+06 Not Evaluated 1.05E+04 1.31E+04 4.20E+05 6.62E+03 26.8 TP-3 (2'-3')
Aliphatics (C13-C16)
[Hexadecane (544-76-3)]nc 1.48E+03 1.02E+01 1.26E+04 5.38E+06 Not Evaluated 1.64E+05 2.39E+05 7.67E+06 6.77E+03 1330 TP-2 (5'-6')
Aliphatics (C17-C21)
[Heptadecane (629-78-7)]nc 1.02E+04 2.04E+02 1.04E+05 4.44E+07 Not Evaluated 2.63E+08 2.30E+08 7.41E+09 1.36E+05 320 TP-3 (2'-3')
Aliphatics (C22-C35)
[Heptadecane (629-78-7)]nc 1.02E+04 2.04E+02 1.04E+05 4.44E+07 Not Evaluated 2.63E+08 2.30E+08 7.41E+09 1.36E+05 1400 TP-3 (2'-3')
Highest
Air
Concentrations
Remaining at the
Site
Air
Comments
(e.g. Sample ID,
Sample Date, etc.)
Groundwater Comments
(e.g. Sample ID,
Sample Date, etc.)Chemical Name (CAS #)
Pr
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Highest
Groundwater
Concentrations
Remaining at the
Site
Soil
Comments
(e.g. Sample ID,
Sample Depth,
Sample Date, etc.)
Highest
Soil
Concentrations
Remaining at the
Site
Name:
Company, Agency, other:
Phone:
E-mail:
UST Consultant Cert. #:
435-760-8269
[e-mail]
Blake Downey
C-0268
Wasatch Environmental
435-760-8269
[e-mail]
Date prepared:12/10/2024
Sommers Auto Wrecking - After Remediation
647 W 3300 S
Blake Downey
DERR Cal Post Remediation USE Page 1 of 3
12/12/2024
9:12 AM
Page 2 of 3
Site-Specific Cleanup Levels* for Commercial/ Industrial Receptors
Air Groundwater Soil
SSCLair SSCLwing SSCLwesp SSCLwamb SSCLs-leach SSCLsesp SSCLsamb SSCLss
(See Eq. D.1)(See Eq. D.2)(See Eq. D.3)(See Eq. D.4)(See Eq. D.5)(See Eq. D.6)(See Eq. D.7)(See Eq. D.8)
Air Groundwater Groundwater Groundwater Subsurface soil Subsurface soil Subsurface soil Surface Soil
Inhalation Ingestion Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Leaching to
groundwater
(groundwater
ingestion)
Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Ingestion of soil,
inhalation of
vapors and
particles, and
dermal contact
µg/m3 air µg/m3 air mg/L water mg/L water mg/L water mg/L water mg/kg soil mg/kg soil mg/kg soil mg/kg soil mg/kg soil
Highest
Air
Concentrations
Remaining at the
Site
Air
Comments
(e.g. Sample ID,
Sample Date, etc.)
Groundwater Comments
(e.g. Sample ID,
Sample Date, etc.)Chemical Name (CAS #)

Highest
Groundwater
Concentrations
Remaining at the
Site
Soil
Comments
(e.g. Sample ID,
Sample Depth,
Sample Date, etc.)
Highest
Soil
Concentrations
Remaining at the
Site
Acenaphthylene (208-96-8)nc 1.53E+02 3.07E+00 1.45E+04 4.50E+05 2.79E+01 1.16E+05 3.72E+06 1.47E+04
Acenaphthene (83-32-9)nc 8.69E+01 6.13E+00 7.57E+03 2.45E+05 4.82E+01 5.18E+04 1.66E+06 2.46E+04
Fluorene (86-73-7)nc 5.62E+01 4.09E+00 5.36E+03 1.60E+05 5.21E+01 5.98E+04 1.92E+06 1.73E+04
Phenanthrene (85-01-8)nc 1.53E+02 3.07E+00 1.69E+04 4.72E+05 8.09E+01 3.92E+05 1.26E+07 1.51E+04
Anthracene (120-12-7)nc 4.38E+02 3.07E+01 4.61E+04 1.30E+06 7.64E+02 1.01E+06 3.25E+07 1.38E+05
Fluoranthene (206-44-0)nc 5.83E+01 4.09E+00 7.88E+03 2.14E+05 3.66E+02 6.22E+05 2.00E+07 1.97E+04
Pyrene (129-00-0)nc 4.38E+01 3.07E+00 5.23E+03 1.41E+05 2.54E+02 3.82E+05 1.23E+07 1.47E+04
Benz(a)Anthracene (56-55-3)c 1.96E-01 3.92E-04 1.88E+01 5.09E+02 1.29E-01 5.45E+03 1.75E+05 2.01E+00
Chrysene (218-01-09)c 1.96E+00 3.92E-02 2.75E+02 7.39E+03 1.03E+01 6.36E+04 2.04E+06 1.99E+02
Benzo(b)Fluoranthene (205-99-2)c 1.96E-02 3.92E-04 2.98E+00 8.18E+01 1.05E-01 7.01E+02 2.25E+04 1.99E+00
Benzo(k)-Fluoranthene (207-08-09)c 1.96E-01 3.92E-03 3.10E+01 8.28E+02 1.53E+00 1.06E+04 3.42E+05 1.99E+01
Benzo(a)-Pyrene (50-32-8)c 2.35E-03 3.92E-05 2.29E-01 6.12E+00 1.65E-02 8.51E+01 2.74E+03 1.99E-01
Indeno(1, 2, 3-Cd)Pyrene (193-39-
5)c 2.35E-02 3.92E-04 1.14E+03 1.26E+03 1.02E-02 2.57E+04 2.90E+04 1.96E+00
Dibenzo-(a, h)Anthracene (53-70-
3)c 2.35E-02 3.92E-04 3.93E+00 1.05E+02 9.34E-01 8.27E+03 2.66E+05 2.00E+00
Benzo (g, h, i)-Perylene (191-24-2)nc 1.53E+02 3.07E+00 2.41E+04 6.47E+05 3.07E+03 2.13E+07 6.86E+08 1.56E+04
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not used
Not used c Not used Not used Not used Not used Not used Not used Not used Not usedAd
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DERR Cal Post Remediation USE Page 2 of 3
12/12/2024
9:12 AM
Page 3 of 3
Site-Specific Cleanup Levels* for Commercial/ Industrial Receptors
Air Groundwater Soil
SSCLair SSCLwing SSCLwesp SSCLwamb SSCLs-leach SSCLsesp SSCLsamb SSCLss
(See Eq. D.1)(See Eq. D.2)(See Eq. D.3)(See Eq. D.4)(See Eq. D.5)(See Eq. D.6)(See Eq. D.7)(See Eq. D.8)
Air Groundwater Groundwater Groundwater Subsurface soil Subsurface soil Subsurface soil Surface Soil
Inhalation Ingestion Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Leaching to
groundwater
(groundwater
ingestion)
Indoor air
(enclosed space)
vapor inhalation
Outdoor air
(ambient) vapor
inhalation
Ingestion of soil,
inhalation of
vapors and
particles, and
dermal contact
µg/m3 air µg/m3 air mg/L water mg/L water mg/L water mg/L water mg/kg soil mg/kg soil mg/kg soil mg/kg soil mg/kg soil
Highest
Air
Concentrations
Remaining at the
Site
Air
Comments
(e.g. Sample ID,
Sample Date, etc.)
Groundwater Comments
(e.g. Sample ID,
Sample Date, etc.)Chemical Name (CAS #)

Highest
Groundwater
Concentrations
Remaining at the
Site
Soil
Comments
(e.g. Sample ID,
Sample Depth,
Sample Date, etc.)
Highest
Soil
Concentrations
Remaining at the
Site
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
Not used nc Not used Not used Not used Not used Not used Not used Not used Not used
* - Site-Specific Cleanup Levels assume a Natural Attenuation Factor of 1 (i.e. no natural attenuation). c - carcinogen; nc - non-carcinogen
Site-specific Parameters used in Calculations
Parameter Comments
Soil
Receptor
i
Lgw
Ls
Pavement
Precip.
Soil Zone
W
Ad
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(n
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-
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)
Width of contaminated source area parallel to groundwater flow or wind direction
Annual precipitation
Is contamination present in the saturated zone?
Is contamination beneath pavement or bare soils?
Depth to contaminated soil
Depth to groundwater
Hydraulic gradient
Select the most sensitive Receptor that is present at the site
Soil type representative of site
Description
15.38
Yes
50
Value
Clay
Commercial/ Industrial
0.07
6
4
UNPAVED: contamination beneath
bare soils
inches/year
Not applicable
ft
Units
Not applicable
Not applicable
ft-vertical/ft-lateral
ft
Not applicable
ft
DERR Cal Post Remediation USE Page 3 of 3
12/12/2024
9:12 AM

Appendix B
Blue Stakes Documentation

From:Jacob Scott
To:Blake Downey
Subject:FW: [EXTERNAL] UTAH EMLCFM 2024/07/30 #02077 C42120893-00C NORM NEW LREQ
Date:Wednesday, July 31, 2024 8:17:54 AM
-----Original Message-----
From: [e-mail] <[e-mail]>
Sent: Tuesday, July 30, 2024 3:45 PM
To: Jacob Scott <[e-mail]>
Subject: [EXTERNAL] UTAH EMLCFM 2024/07/30 #02077 C42120893-00C NORM NEW LREQ
EMLCFM 02077 UTAHc 07/30/24 15:44:58 C42120893-00C NORM NEW POLY
Thank you for contacting Blue Stakes of Utah 811 regarding your upcoming digging project. Please review your locate request below and save it for your records.
If any of the information is incorrect, please contact Blue Stakes ASAP by dialing 811 or 801-208-2100, option 1 and reference your locate request number.
Locate Specialists are available Monday - Friday, 8 AM - 4 PM, except Holidays.
DO IT YOURSELF ONLINE! Visit
https://urldefense.proofpoint.com/v2/url?u=https-3A__www.bluestakes.org_how-2Dit-2Dworks_-23locate-2Drequest&d=DwIDAw&c=euGZstcaTDllvimEN8b7jXrwqOf-
v5A_CdpgnVfiiMM&r=Z09QEQdNZvGCaYx7MVcY9fHEHsw_JsMsQBC1Lz7Rg9c&m=LpGGbJ0kQbnP7p6VFFNrlZz7r8Eu3Z2nHjPS2WqRWrkbLpjX1V9hnOTbrlVYpEgI&s=inINC33kUNHL0FWN_2llPeT00ULJlUOUKwWoTjkDsYM&e=
before your next project! Existing locate requests can be updated and new locate requests can be created online quickly and easily, 24 hours a day. No need to wait on hold!
Please allow up to 3 full business days for the facility lines to be marked. To view responses regarding the status of your locate request, visit https://urldefense.proofpoint.com/v2/url?u=https-
3A__www.bluestakes.org_epr_&d=DwIDAw&c=euGZstcaTDllvimEN8b7jXrwqOf-
v5A_CdpgnVfiiMM&r=Z09QEQdNZvGCaYx7MVcY9fHEHsw_JsMsQBC1Lz7Rg9c&m=LpGGbJ0kQbnP7p6VFFNrlZz7r8Eu3Z2nHjPS2WqRWrkbLpjX1V9hnOTbrlVYpEgI&s=sAbgATI2R89bvFuRgKNAX7jjOdsOu5I5tOiLTbXfsjI&e= and
then "Check Locate Request Response".
If an Excavator is aware of or observes indications of a facility that was not marked in the work area covered by a current locate request, they are required to submit a No Response Notice (NRSP) before they can start digging and provide which
facility operator(s) or facility type(s) have not responded or marked.
This can be done anytime online at https://urldefense.proofpoint.com/v2/url?u=https-3A__otr.bluestakes.org_&d=DwIDAw&c=euGZstcaTDllvimEN8b7jXrwqOf-
v5A_CdpgnVfiiMM&r=Z09QEQdNZvGCaYx7MVcY9fHEHsw_JsMsQBC1Lz7Rg9c&m=LpGGbJ0kQbnP7p6VFFNrlZz7r8Eu3Z2nHjPS2WqRWrkbLpjX1V9hnOTbrlVYpEgI&s=bGACchR-FXORDLZzV8Dq2O-
PDBo9_K3y1gHEUzGeiv8&e= or by calling 811 during business hours.
Utah Code Title 54, Chapter 8a, Damage to Underground Utility Facilities Act has been amended effective May 1, 2024. Visit https://urldefense.proofpoint.com/v2/url?u=https-
3A__www.bluestakes.org_law_&d=DwIDAw&c=euGZstcaTDllvimEN8b7jXrwqOf-
v5A_CdpgnVfiiMM&r=Z09QEQdNZvGCaYx7MVcY9fHEHsw_JsMsQBC1Lz7Rg9c&m=LpGGbJ0kQbnP7p6VFFNrlZz7r8Eu3Z2nHjPS2WqRWrkbLpjX1V9hnOTbrlVYpEgI&s=FZEtNsZBv3GhLy7FhpSX-EKvG-MEvx0LsxsqqR_KXIw&e=
for additional details.
For additional information about the next steps in the process, other pertinent details, or frequently asked questions, please visit https://urldefense.proofpoint.com/v2/url?u=https-
3A__www.bluestakes.org_faqs_&d=DwIDAw&c=euGZstcaTDllvimEN8b7jXrwqOf-
v5A_CdpgnVfiiMM&r=Z09QEQdNZvGCaYx7MVcY9fHEHsw_JsMsQBC1Lz7Rg9c&m=LpGGbJ0kQbnP7p6VFFNrlZz7r8Eu3Z2nHjPS2WqRWrkbLpjX1V9hnOTbrlVYpEgI&s=aVcEZVPqVZMmBI3hboMRb1mrngXKOj83mcq6M5JIXNo&e=.
Dig Safely!
Ticket : C42120893 Rev:00C Taken: 07/30/24 15:44 Old Tkt: C42120893 Taken: 07/30/24 15:44 Oper: _DESTINEE
Submitted: 07/30/24 15:44 Oper: _DESTINEE Chan:ITE Legal date: 08/02/24 08:00 Good Thru : 08/20/24 08:00 Update By: 08/16/24 08:00
State: UT Cnty: SALT LAKE Place: SOUTH SALT LAKE
Subdivision:
Address : 647
Street : W 3300 S
Side of St: Side of Lot: Digging in Rd: N
Svc Side of St: Depth:
Location: MARK ENTIRE LOT
:
Grids : 4041A11154B 4042D11154B
P&D: N Work type: SOIL REMOVAL
Ug/Oh/Both: U Expl/Blast: N Boring: N Railroad: Emergency: N Meet: N
Company : WASATCH ENVIRONMENTAL Phone: [phone] Co addr : 2410 W CALIFORNIA AVE
City : SALT LAKE CITY State: UT Zip: 84104
Caller : JACOB SCOTT Phone: [phone] Type: E Contact : JAKE SCOTT Phone: [phone]
BestTime:
Email : [e-mail]
Members:
Code Company Description Phone
---------- ---------------------------------------- ------------------------------ -----------------
CCUT00 COMCAST CATV & FIBER MARKED BY USIC 800-778-9140
QGCOCL ENBRIDGE GAS UTAH GAS MARKED BY ELM LOCATING 888-728-9343
FDFO FIRST DIGITAL FIBER OPTICS FIBER OPTICS 385-290-9299
JVWCD JORDAN VALLEY WATER C.D. CULINARY WATER 801-565-4300
CTLUT01 LUMEN/CENTURYLINK FBR/PHN MARKED BY USIC 800-778-9140
MOID MOUNT OLYMPUS I.D. SEWER 801-262-2904
MOID MOUNT OLYMPUS I.D. SEWER 801-262-2904
RMPSLD ROCKY MOUNTAIN POWER - SALT LAKE MAIN ELECTRIC MARKED BY USIC 800-778-9140
SLCOSL SALT LAKE COUNTY STREET LIGHTS ST LIGHTS - CITY & COUNTY Not available
SSLC SOUTH SALT LAKE CITY STORM DRAIN, SWR, CULINARY WTR 801-412-3210
SNI SYRINGA NETWORKS FBR & PHN MARKED BY RIGHT SIDE 801-637-4078
UDOTR2 UDOT REGION II FIBER OPTICS & TRAFFIC SIGNALS 801-887-3403
MCI VERIZON BUSINESS (MCI) FIBER MARKED BY STAKE CENTER 800-624-9675
ZAYOUT ZAYO FIBER SOLUTIONS FIBER MARKED BY STAKE CENTER 801-364-1063
View ticket info at:
https://urldefense.proofpoint.com/v2/url?u=https-3A__map.bluestakes.org_-3FTRG-3D88CmFjDjAqAj5jG-2DX&d=DwIDAw&c=euGZstcaTDllvimEN8b7jXrwqOf-
v5A_CdpgnVfiiMM&r=Z09QEQdNZvGCaYx7MVcY9fHEHsw_JsMsQBC1Lz7Rg9c&m=LpGGbJ0kQbnP7p6VFFNrlZz7r8Eu3Z2nHjPS2WqRWrkbLpjX1V9hnOTbrlVYpEgI&s=GbAJa0tA31oxeon6Kb08W8SaLlHRkxOVQbLVVsGJTm8&e=

Appendix C
South Salt Lake Permit Documentation

ENGINEERING APPLICATION

CHECKLIST PRIOR TO SUBMITTAL

1. Completed Application
2. Signed Acknowledgement of Terms & Conditions
3. Non-refundable $60 Deposit (Applied towards inspection fee)

Documents required by permit type

**INCOMPLETE APPLICATIONS WILL NOT BE ACCEPTED**

CHECKLIST PRIOR TO APPROVAL

1. Invoice payment
2. Infrastructure Agreement & Infrastructure Improvement Warranty signed
(If applicable to a bond)

Permit
Type
Liability
Insurance
(SSLC
certificate
holder)

BMP or
SWPPP
1 Acre>
Site
Plans Cost
Estimate
of
Project
Traffic
Control
Plan
Traffic
Control
Only
Required Required Required
ROW-
Excavation Required Required Required Required Required
Non-ROW
Utility
Work
Required Required Required Required
220 E Morris Ave
South Salt Lake, Utah 84115
[phone] ext.2
www.sslc.gov

PROJECT INFORMATION
PROPERTY OWNER
PROJECT OWNER TELEPHONE
EMAIL 24-HR EMERGENCY TELEPHONE
PROJECT ADDRESS CITY I STATE I ZIP
CLOSURE INFORMATION #OF
LANES
#OF
BLOCK
#OF
DAYS
SIDEWALK
LANE CLOSURE
LOCAL STREET FULL CLOSURE
ARTERIAL STREET FULL CLOSURE
CONTACT INFORMATION
PERMIT CONTACT TELEPHONE
EMAIL 24-HR EMERGENCY TELEPHONE
BUSINESS ADDRESS CITY STATE ZIP
GENERAL CONTRACTOR TELEPHONE
EMAIL I
STATE LICENSE # EXPIRATION DATE
SUB CONTRACTOR TELEPHONE
EMAIL I
STATE LICENSE# EXPIRATION DATE
SUB CONTRACTOR TELEPHONE
EMAIL
BUSINESS ADDRESS I CITY STATE ZIP
STATE LICENSE # EXPIRATION DATE
220 E Morris Ave
South Salt Lake, Utah 84115
[phone] ext.2
www.sslc.gov
Traffic Control Only ROW-Excavation Non-ROW Utility Work X ---------------------------------
Non-ROW No Utility Work
Mountain Crest Wasatch, LLC.
Mark Bond 801-328-2051
[e-mail]
647 West 3300 South South Salt Lake Utah 84119
NA
NA
NA
NA
NA
Blake B. Downey - Wasatch Environmental, Inc.435-760-8269
435-760-8269
Utah 84104
[e-mail]
2410 W. California Ave.Salt Lake City
DESCRIPTION OF WORK Wasatch plans to complete 4 shallow soil excavations to remove metals and petroleum impacted soil and dispose of the soil off-site. The soil will be direct loaded into dump trucks and
transported off-site for disposal (see the attached map for excavation locations and areas). Wasatch obtained (see attachment) a Treated Groundwater Discharge permit from the Utah
DWQ, as we will be extracting groundwater from EXC-4 to facilitate the soil excavation activities. The groundwater will be pumped into a 21,000-gallon frack tank and discharged as a batch
discharge. The the treated water will be run through a bag filter to remove sediments and then through a granular activated carbon vessel to remove any contaminants from the discharge.
Per the DWQ permit, prior to discharge, the water will be sampled to verify we meet the permit discharge requirements. Wasatch plans to discharge the treated groundwater to the storm
water drain depicted on the attached map. See the attached BMPs and fugitive dust plan for the excavation activities. All excavations will be backfilled and compacted upon completion of
the remediation activities. We will add inlet protections (straw waddles or filter pads) to the storm water drains located on-site and just south-west of the project.
Metro Group, Inc. - Devan Knight 801-328-2051
[e-mail]
SLC Business License - LIC2001-01011 State Reg. #671841-0142
------------------------------------ Work is going to be self completed no licensed contractor.
SLC Business Liense. - March 31, 2025
SOUTH SALT LAKE PUBLIC RIGHT OF WAY ACCESS TERMS AND CONDITIONS
Application is hereby made by the undersigned for a permit to work within the City right of way for the purpose designated
below. It is understood and agreed by the applicant that all necessary precautions for public safety will be installed and
maintained from the commencement to the conclusion of construction operations described by this permit. The applicant
shall indemnify and hold harmless the City of South Salt Lake from all liability, loss, damage, cost, or other expenses, arising
from any accident, injury, loss or damage to any person or property caused directly or indirectly by the acts, errors, or
omissions of applicant and its agents, servants, employees, or subcontractors. In addition, applicant agrees to the following
terms and conditions:
1.All work must be scheduled and coordinated with the City of South Salt Lake Engineering Department. All work
not inspected prior to backfill being placed, shall be re-excavated at the contractor's expense to allow for
inspection.
2.All work and clean up must be complete within 30 days from the start date of this permit unless a permit extension is
granted by South Salt Lake City Engineer, or the Engineer's authorized representative.
3.Curb, gutter, and sidewalk installation shall be in conformance with the 2017 Edition of the APWA Manual of
Standard Plans and Manual of Standard Specifications, South Salt Lake City engineering supplementary standards,
or South Salt Lake City Engineer, or the Engineer's authorized representative.
4.Asphalt trench repair shall be saw cut. Asphalt trench repairs require a T-patch extending at least 2 feet beyond the
edge of the trench, or as specified in the APWA Manual of Standard Plans and Specifications, South Salt Lake City
Engineering supplementary standards, South Salt Lake City Engineer, or the Engineer's authorized representative.
5.A minimum of 8" of road base is to be installed under pavement surfaces. A minimum of 6" of road base shall be
installed under curb, gutter, and sidewalk or as specified in the APWA Manual of Standard Plans and Specifications,
or as directed by South Salt Lake City Engineer or the Engineer's authorized representative.
6.Replacement asphalt shall match existing asphalt thickness plus 1 inch, but in no case be less than 4 inch thick. See
the latest edition of the APWA Manual of Standard Plans and Specifications for maximum pavement thickness.
7.On all new pavements, 5 years old or less, asphalt trench repairs shall be in conformance with South Salt Lake City
engineering supplementary standards, or South Salt Lake City Engineer, or the Engineer's authorized
representative.
8.Any road with existing overlay fabric shall be repaired as directed by South Salt Lake City Engineer, or the Engineer's
authorized representative.
9.All manholes and inlet boxes shall be core cut.
10.Storm drain and sewer line repairs shall be video inspected, and a copy of the video shall be given to the South Salt
Lake City Engineer, or the Engineer's authorized representative.
11.All contractors and their employees shall wear proper personal protective equipment at all times when working in the
public right of way.
12.Permit applicant shall provide Certificate of Liability Insurance with application.
•Liability insurance shall include: $1,000,000 each occurrence & $2,000,000 aggregate
13.The Fees paid for this permit do NOT include overtime costs for city inspectors. Applicant agrees to reimburse the
City of South Salt Lake for the following costs:
•Two-Hour minimum call out fee for all after hours, weekends, or emergency inspection service
•Additional time shall be charged at a rate of 1.5 times the inspector's hourly rate.
14.24-hour notice is required for all inspections. Call 801-483-6032, specify Engineering Inspection.
15.NO EXCAVATION WILL BE LEFT OPEN LONGER THAN 24 HOURS WITHOUT EXPRESS PERMISSION IN
WRITING FROM SOUTH SALT LAKE CITY ENGINEER, OR ENGINEER'S REPRESENTIVE.
16.ALL WORK MUST COMPLY WITH THE CITY OF SOUTH SALT LAKE STORM WATER MANAGEMENT PLAN. Call
the South Salt Lake Storm Water Division for storm water related questions at 801-483-6045
**I HAVE READ AND UNDERSTAND THE TERMS OF THIS PERMIT AND AGREE TO BE BOUND THERETO***
SIGNATURE OF APPLICANT:
NAME OF APPLICANT (PRINTED):_________________________________________Blake B. Downey
The use or reuse of this information is restricted to the referenced document unless otherwise authorized.
Wasatch Environmental Copyright 2006
Figure 1Site Map and Proposed Excavation Map
SOMMERS AUTO WRECKING WEI 2469-002G
1 inch is equal
to 50 feet
70
0

W
es
t
Proposed Excavation Area
EXC-2
(0.01 acres)
EXC-3
(0.01 acres)
EXC-1
(0.22 acres)
EXC-4
(0.20 acres)
Approximate Site Boundary
Equipment Storage
Area (0.07 acres)
3300 South
South Salt Lake
Storm Water Drain
06/11/2024
Trustco Insurance Agency
2735 East Parleys Way
Suite 305
Salt Lake City UT 84109-1666
Stephanie Ingalls
[phone] [phone]
[e-mail]
Wasatch Environmental Inc.
2410 West California Avenue
Salt Lake City UT 84104
Beazley Insurance Company, Inc.37540
Selective Insurance Company of America 12572
WCF Mutual Insurance Company 10033*
2024-
GL,PROF,POLL,BA,WC,X
A ENC000345906 06/24/2024 06/24/2025
1,000,000
100,000
10,000
1,000,000
2,000,000
2,000,000
Contractors Pollution
Liability
1mill/2mill
B S 2506648 06/24/2024 06/24/2025
1,000,000
Leased & Rented equip.175,000/500 ded.
A ENX000999202 06/24/2024 06/24/2025
4,000,000
4,000,000
C Y 1668944 04/01/2024 04/01/2025 1,000,000
1,000,000
1,000,000
A Professional Liability ENC000345906 06/24/2024 06/24/2025
Each Occurence 1,000,000
General Aggregate 3,000,000
deductible 5,000
See attached
Salt Lake City Corporation Engineering Division
P.O. Box 145506
Salt Lake City UT 84114-5506
SHOULD ANY OF THE ABOVE DESCRIBED POLICIES BE CANCELLED BEFORE
THE EXPIRATION DATE THEREOF, NOTICE WILL BE DELIVERED IN
ACCORDANCE WITH THE POLICY PROVISIONS.
INSURER(S) AFFORDING COVERAGE
INSURER F :
INSURER E :
INSURER D :
INSURER C :
INSURER B :
INSURER A :
NAIC #
NAME:CONTACT
(A/C, No):FAX
E-MAILADDRESS:
PRODUCER
(A/C, No, Ext):PHONE
INSURED
REVISION NUMBER:CERTIFICATE NUMBER:COVERAGES
IMPORTANT: If the certificate holder is an ADDITIONAL INSURED, the policy(ies) must have ADDITIONAL INSURED provisions or be endorsed.
If SUBROGATION IS WAIVED, subject to the terms and conditions of the policy, certain policies may require an endorsement. A statement on
this certificate does not confer rights to the certificate holder in lieu of such endorsement(s).
THIS CERTIFICATE IS ISSUED AS A MATTER OF INFORMATION ONLY AND CONFERS NO RIGHTS UPON THE CERTIFICATE HOLDER. THIS
CERTIFICATE DOES NOT AFFIRMATIVELY OR NEGATIVELY AMEND, EXTEND OR ALTER THE COVERAGE AFFORDED BY THE POLICIES
BELOW. THIS CERTIFICATE OF INSURANCE DOES NOT CONSTITUTE A CONTRACT BETWEEN THE ISSUING INSURER(S), AUTHORIZED
REPRESENTATIVE OR PRODUCER, AND THE CERTIFICATE HOLDER.
OTHER:
(Per accident)
(Ea accident)
$
$
N / A
SUBR
WVD
ADDL
INSD
THIS IS TO CERTIFY THAT THE POLICIES OF INSURANCE LISTED BELOW HAVE BEEN ISSUED TO THE INSURED NAMED ABOVE FOR THE POLICY PERIOD
INDICATED. NOTWITHSTANDING ANY REQUIREMENT, TERM OR CONDITION OF ANY CONTRACT OR OTHER DOCUMENT WITH RESPECT TO WHICH THIS
CERTIFICATE MAY BE ISSUED OR MAY PERTAIN, THE INSURANCE AFFORDED BY THE POLICIES DESCRIBED HEREIN IS SUBJECT TO ALL THE TERMS,
EXCLUSIONS AND CONDITIONS OF SUCH POLICIES. LIMITS SHOWN MAY HAVE BEEN REDUCED BY PAID CLAIMS.
$
$
$
$PROPERTY DAMAGE
BODILY INJURY (Per accident)
BODILY INJURY (Per person)
COMBINED SINGLE LIMIT
AUTOS ONLY
AUTOSAUTOS ONLY
NON-OWNED
SCHEDULEDOWNED
ANY AUTO
AUTOMOBILE LIABILITY
Y / N
WORKERS COMPENSATION
AND EMPLOYERS' LIABILITY
OFFICER/MEMBER EXCLUDED?
(Mandatory in NH)
DESCRIPTION OF OPERATIONS below
If yes, describe under
ANY PROPRIETOR/PARTNER/EXECUTIVE
$
$
$
E.L. DISEASE - POLICY LIMIT
E.L. DISEASE - EA EMPLOYEE
E.L. EACH ACCIDENT
EROTH-STATUTEPER
LIMITS(MM/DD/YYYY)POLICY EXP(MM/DD/YYYY)POLICY EFFPOLICY NUMBERTYPE OF INSURANCELTRINSR
DESCRIPTION OF OPERATIONS / LOCATIONS / VEHICLES (ACORD 101, Additional Remarks Schedule, may be attached if more space is required)
EXCESS LIAB
UMBRELLA LIAB $EACH OCCURRENCE
$AGGREGATE
$
OCCUR
CLAIMS-MADE
DED RETENTION $
$PRODUCTS - COMP/OP AGG
$GENERAL AGGREGATE
$PERSONAL & ADV INJURY
$MED EXP (Any one person)
$EACH OCCURRENCE
DAMAGE TO RENTED $PREMISES (Ea occurrence)
COMMERCIAL GENERAL LIABILITY
CLAIMS-MADE OCCUR
GEN'L AGGREGATE LIMIT APPLIES PER:
POLICY PRO-JECT LOC
CERTIFICATE OF LIABILITY INSURANCE DATE (MM/DD/YYYY)
CANCELLATION
AUTHORIZED REPRESENTATIVE
ACORD 25 (2016/03)
© 1988-2015 ACORD CORPORATION. All rights reserved.
CERTIFICATE HOLDER
The ACORD name and logo are registered marks of ACORD
HIRED
AUTOS ONLY
00020981
Trustco Insurance Agency
25 Certificate of Liability Insurance: Notes
Salt Lake City Corporation is listed as Additional Insured with respects to General Liability per endorsement CG2013 11/85.
Salt Lake City Corporation is listed as Additional Insured with respects to Business Auto Liability per endorsement CA 7809 04/24
Salt Lake City Corporation will be given a 30-day notice in the event of cancellation and 10-day notice for non-payment of premium for the referenced
insurance policies.
ACORD 101 (2008/01)
The ACORD name and logo are registered marks of ACORD
© 2008 ACORD CORPORATION. All rights reserved.
THIS ADDITIONAL REMARKS FORM IS A SCHEDULE TO ACORD FORM,
FORM NUMBER:FORM TITLE:
ADDITIONAL REMARKS
ADDITIONAL REMARKS SCHEDULE Page of
AGENCY CUSTOMER ID:
LOC #:
AGENCY
CARRIER NAIC CODE
POLICY NUMBER
NAMED INSURED
EFFECTIVE DATE:
Wasatch Environmental Inc.Trustco Insurance Agency
25 Certificate of Liability Insurance: Notes
The above referenced General Liability policy includes the following endorsements:CG2010 Blanket Additional Insured with Ongoing Operations, CG2001
Primary & Non-Contributory and CG2037 Blanket Additional Insured - Completed Operations CG2404 1093 Blanket Waiver of Subrogation & CGL160 Per
Project Aggregate
The above referenced Pollution policy includes the following endorsements: CPL271 & CPL275 Blanket Additional Insured, Products, Completed
Operations, Ongoing Operations & CPP279 Blanket Waiver of Subrogation
The above referenced Business Auto policy includes the following endorsements: CA7809 04/24 ElitePac Commercial Automobile Extension (Blanket
Additional Insured, Primary & Non-Contributory Coverage, Blanket Waiver of Subrogation
The above referenced Workers Compensation policy includes the following endorsements: WC430305 Blanket Waiver of Subrogation
The above referenced Excess Liability policy includes the following endorsement: EVX113 Excess Following Form Liability Insurance
ACORD 101 (2008/01)
The ACORD name and logo are registered marks of ACORD
© 2008 ACORD CORPORATION. All rights reserved.
THIS ADDITIONAL REMARKS FORM IS A SCHEDULE TO ACORD FORM,
FORM NUMBER:FORM TITLE:
ADDITIONAL REMARKS
ADDITIONAL REMARKS SCHEDULE Page of
AGENCY CUSTOMER ID:
LOC #:
AGENCY
CARRIER NAIC CODE
POLICY NUMBER
NAMED INSURED
EFFECTIVE DATE:

WASATCH ENVIRONMENTAL, INC.
ENVIRONMENTAL SCIENCE AND ENGINEERING

Wasatch Environmental, Inc. 1
FUGITIVE EMISSIONS MONITORING PLAN
FORMER SOMMERS AUTO WRECKING
647 WEST 3300 SOUTH
SOUTH SALT LAKE, UTAH

1. INTRODUCTION

This Fugitive Emissions Monitoring Plan (Plan) has been prepared for soil remediation activities at the
former Sommers Auto Wrecking property, an industrial property, consisting of 5.15 acres, located at 647
West 3300 South in South Salt Lake, Utah (Site). Heavy metal and petroleum hydrocarbon impacted soil
is located at the Site. These impacted soil will be excavated and disposed off-Site.

This Plan will be followed by the general contractor and all subcontractors during excavation, stockpiling,
on-Site relocation, and backfilling activities on the Site.

2. OBJECTIVES

The purpose of this Plan is to describe the fugitive dust control measures and Best Management
Practices (BMPs) that will be followed during soil excavation and backfilling activities to minimize the
generation of fugitive dust. Also described is the monitoring approach to evaluate effectiveness of the
dust control BMPs and to document those adjoining residents and workers involved with on-Site activities
are not exposed to fugitive dust, and that the State of Utah opacity limits are met.

Potential exposures to fugitive dust emissions by commercial/industrial properties in areas adjacent to the
Site and workers involved with impacted soil removal activities will be assessed using U.S. EPA Method 9
(Visual Determination of Opacity of Emissions from Stationary Sources) at the Site.

The equipment expected to be used during on-Site activities with the potential to generate fugitive dust
includes haul trucks, skidsters, front end loaders, water trucks, and excavators. A majority of this
equipment is not used on public roads so track-out is not expected to be an issue although it will be
monitored and prevented to the extent feasible. A temporary, stabilized gravel track-out pad will be in
place and steps will be taken to minimize track-out from equipment onto public roads.

By complying with the State of Utah Opacity limits, the National Ambient Air Quality Standards for
particulate matter, both particle sizes below 10 microns in diameter (PM10) and 2.5 microns in diameter
(PM2.5) will also be met. The daily limit for PM10 is 150 micrograms per cubic meter (ug/m3) and the daily
limit for PM2.5 is 35 ug/m3.

3. DUST CONTROL MEASURES/BEST MANAGEMENT PRACTICE

Attached to this Plan (as Appendix 1) is the Utah Division of Air Quality (DAQ) approved Fugitive Dust
Control Plan for the former Sommers Auto Wrecking project, which describes the construction BMPs to
minimize the generation of fugitive dust. These practices include the use of water to wet soils and haul
roads, and to form a crust on open soils. The Plan also discusses wetting stockpiles, maintaining low
drop heights when loading material, using gravel in lay-down areas, limiting vehicle speeds, and the
proper application of track-out controls. This Plan will be presented to the contractor and any
subcontractors during initial Site training activities. The Plan requires that all construction activities meet
opacity requirements in R307-309-5. It is Wasatch’s experience that wetting of soil greatly decreases any
dust generation.

FUGITIVE DUST CONTROL PLAN Former Sommers Auto Wrecking
Wasatch Environmental, Inc. 2

Also attached to this Plan (as Appendix 2) is a wind rose diagram of frequency of wind direction and
speed during November 2022. The diagram shows that the prevailing winds are generally expected to be
out of the south to southeast, or from the northwest. The month of November is representative of the
winds from late summer through the late fall.

It is Wasatch’s experience that heavy watering of stockpiles (if used) and exposed soil prior to ending
work before the weekend is effective in forming a “crust” on the soil which should reduce fugitive dust
generation. However, if strong winds are predicted during overnight hours or weekends, arrangement will
be made to provide additional watering.

4. DAILY MONITORING

Wasatch personnel will be on-Site during all soil removal and backfilling activities to screen soils using a
hand-held photoionization detector, collect confirmation soil samples for laboratory analysis, direct Health
and Safety meetings and training, and implement the fugitive dust control and monitoring procedures
described in this Plan.

Compliance with the Utah opacity limits (20% opacity at the generation source and 10% opacity at the
perimeter) will be assessed using U.S. EPA Method 9, modified to account for non-stationary sources.
For non-stationary sources, which would apply to vehicles on-Site, opacity readings are directed to a
point not less than one-half the vehicle length behind the vehicle and not less than one half the vehicle
height.

During soil remediation activities, Wasatch personnel trained as Visible Emission Observers will make
opacity observations at the point of generation and the down-wind property line, as well as at non-
stationary sources such as moving vehicles and/or equipment. These readings will be recorded on a
Visible Emissions Observation Form (Appendix 2), which includes weather conditions, wind speed and
direction, type of activity occurring on-Site, and position of observer relative to dust source. Opacity
readings will be made at least once daily, or as needed during peak work activities, or as weather
conditions require.

5. ACTION LIMITS

Utah opacity action limits will be used as action limits (20% opacity at the generation source and 10%
opacity at the perimeter) for this project.

Any concerns or indications that opacity action limits are being approached or exceeded will be
immediately addressed by aggressively applying additional BMPs, including, as warranted; pre-watering,
shifting the work area, curtailing certain types of work, or shutting down work activities.

When the wind speeds exceed 25 miles per hour, Rule 307-309-5 (3) exempts the opacity limits as long
as the operator continues to implement the approved fugitive dust control plan and administers at least
one of the following control methods: pre-event watering, hourly watering, shifting work areas, or ceases
or reduces dust producing operations.

6. REPORTING

Wasatch will consult frequently (at least weekly) with Utah VCP to discuss, address, and work to remedy
any fugitive dust control issues, including responding to resident complaints, re-evaluating, and modifying
dust control procedures, and other related problems that may arise.

FUGITIVE DUST CONTROL PLAN Former Sommers Auto Wrecking
Wasatch Environmental, Inc. 3

A summary of the dust control measures, copies of the completed daily Air Quality Data Forms and any
corrective actions will be included in the Remediation Action Implementation Report.

Sincerely,

WASATCH ENVIRONMENTAL, INC.

Blake B. Downey, P.G.
Senior Project Hydrogeologist

APPEDNDICES

Appendix 1 – DEQ Fugitive Dust Control Plan
Appendix 2 – Daily Air Monitoring Form and Wind Rose Diagram

F ugitive Dust
8/14/2023 2:30:47 PM
Introduction
Please complete the following information in order to create a Fugitive D ust Application for your
pro ject.  You will have a chance to review the plan prior to nal s ubmission.
Introduction
A Fu gitive Dust Con trol Plan is requ ired if you r project is 1/4 acre or larger an d located in
Cache, Box Elder, Weber, Davis, Salt Lake, Tooele or Utah Cou nty. Other areas and
con dition s are option al.  Please complete the form to assess your project.
Project Location
Projec t Loc ation
A Fu gitive Dust Con trol Plan is requ ired if you r project is 1/4 acre or larger an d located in
Cache, Box Elder, Weber, Davis, Salt Lake, Tooele or Utah Cou nty. Other areas and
con dition s are option al.
Select th e Coun ty where you r project will be located :Salt Lake
Utah Administrative Code (UAC) 307-309-6 re quire s that any person owning or ope rating
a source of fugitive dust within PM10 and PM2.5 non-attainment and maintenance plan
are as on cle ared land grea te r than 1/4 acre in size m ust submit a completed Fugitive Dust
Control Plan. The DAQ Tempora ry Relocation Form re quire s the submission of a Fugitive
Dust Control Plan Permit Num ber for a ll temporary re location proje cts.
Is th is project a temporary relocation project?:
Yes
No
N on-A ttainment Dust Tutorial
W hat is Fugitive D ust?
Fugitive dust is dust that is stirr ed up, creating an air quality pro blem. It is made up of ne
particles called particulate matter. It is a health concern because it ir r itates eyes and nas al tissue
and seriously impacts the r espir ator y system.
x
Fugitive dust may come from gravel o per ations,
construction or demolition activities, land clear ing and
exposed sur faces, r oadways, and mining activities.
Tracko ut fr om muddy work areas also create fugitive
dust when the mud dries.
How We Measu re Compliance-Opac ity
Opacity is the
amount of light
that is blo cked
by something
else such as
smoke or a
tinted window.
The percentage
of opacity can
pro vide a measur e of the par ticulate matter in the air .
Opacity is meas ur ed as a percentage - 0% means that all light passes thr ough; 100% means that
no light can pass through. The more particles pr esent, the higher the opacity percentage.
Utah Fugitive Dust Ru le R307-309-5
Non -a tta inm e nt D u st Ru le
Acknowledgements::
I acknowledge that Utah regulation R307-309-5(1)(a) pro hibits fugitive dust to exceed 10% opacity
at the pro per ty bo undary;
I acknowledge that Utah regulation R307-309-5(1)(b) prohibits fugitive dust to exceed 20% opacity
on site;
I acknowledge that Utah regulation R307-309-5(3) exempts the opacity requirements abo ve, ONLY
when wind speed exceeds 25 miles per hour AND fugitive dust contro ls ar e maintained. The
online fugitive dust contr ol plan r equir es selection of appropriate contr ol measures that must be
implemented for this exemption to apply; and
I acknowledge that failure to comply with fugitive dust rules may r esult in compliance action and
penalties up to $10,000 per violation/day.
Applicant Inform ation
Applican t Type::Pr ime Contractor
Plan Certicate Number:5056048D87
x
x
x
x
Name:blake downey
Mailing Address
Mailin g Address - Address Line 1:2410 west California Ave.
Mailin g Address - Address Line 2:
Mailin g Address - City:salt lake city
Mailin g Address - State:Utah
Mailin g Address - Zip:84104
Email:bd@wasatch-enviro nmental.com
Ph one:[phone]
Project Informa tion
Project Name:Former Sommers Auto Wr ecking
Project End Date:12/31/23
Pr oject L ocation
Address Lin e 1:647 West 3300 South
Address Lin e 2:
City:So uth Salt Lake
State:Utah
Zip:84119
Site Direction s:The Site is lo cated o n the southeast corner of the 3300 South and 700 West
inter section.
County:Salt Lake
Acreage:5.2
Calcu lated Acreage:5.2
La titude/L ongitude Verication
For Ma nu a l La titu d e a nd Lon gitu de in p u t: 
Ma ke su r e to in clu de a t lea st 6 d igits a fter the d e cim al a n d it m u st fa ll w ith in the
sta te of Uta h .
E xa m p le 40.404976 or 40.404976232
Latitude (Decimals Only) :40.698397
Lon gitu de (Decimals Only) :-111.910764
Map Ver ic ation
Copy the following URL into your br owser so you can verify on a map that the pr oject latitude and
longitude you pr ovided ar e co rrect.
Map Calcu lation :https://www.google.com/maps/place/40.698397,-111.910764
Latitu de/Lon gitu de verication :
The above Latitude and Longitude have been veried.
Point of Contact
Point of Contact for du st c ontrol matters and to wh om a COMPLIANCE ACTION
sh ou ld be sen t if n ecessary.
Name:blake downey
Compan y:Wasatch Environmental
Addr ess
Address Lin e 1:2410 west Califor nia Ave.
Address Lin e 2:
City:salt lake city
State:Utah
Zip:84104
Ph one nu mber:[phone]
Cell n umber:
Dust Suppressants
Do you plan on using chemical dust su ppressing or stabilizin g agents?:
Yes
No
Best Manag em ent Practices (BMP) Checklist
Best Man agemen t Practices (BMP) Ch ecklist Instru ctions
Place a check mark next to every activity th at will be con ducted on th is site.  
For each checked activity, complete the corresponding control measures/best management practices (BMP)
selection page.  When completed, we will email the entire plan to you. 
x
x
Fu gitive Du st Plan Nu mber:FC51A011EF
Select all that apply:
01. Backlling area previously excavated or trenched.
02. Blasting so il and rock - drilling and blasting.
03. Clearing for site pr eparation and vacant land cleanup.
04. Clearing forms, foundations, slab clear ing and cleaning of for ms , foundations and slabs
prior to pour ing concrete.
05. Crushing o f constr uctio n and demolition debr is, rock and soil.
06. Cut and ll soils for site gr ade pr eparation.
07. Demolitio n - Implosive demolition of a structure, using explosives.
08. Demolitio n - mechanical/manual demolitio n o f walls, stucco , concrete, freestanding
str uctures, buildings and o ther str uctur es.
09. Disturbed so il throughout pr oject including between s tructures. THIS ACTIV ITY MUST BE
SELECTED FOR ALL PROJECTS.
10. Disturbed land - long term stabilization and erosion contr ol of large tracts of distur bed
land that will not have continuing activity for mo re than 30 days.
11. Hauling mater ials.
12. P aving/subgr ade preparation fo r paving streets, par king lots, etc.
13. Sawing/cutting mater ial, concrete, asphalt, block or pipe.
14. Screening of rock, soil or cons truction debris.
15. Staging ar eas, equipment stor age, vehicle parking lo ts, and material stor age ar eas.
16. Stockpiles materials (storage), other soils, rock or debris, for future use or export.
17. Tailings piles, ponds and erosion contr ol.
18. Trackout, Pr evention and cleanup of mud, silt and soil tracked out onto paved roads. (THIS
ACTIV ITY MUST BE SELECTED FOR ALL PROJECTS.)
19. Trac - unpaved r outes and par king, constr uctio n related trac on unpaved interior
and/or access r oads and unpaved employee/wo rker parking ar eas.
20. Trenching with track or wheel mounted excavator, shovel, backhoe or trencher .
21. Truck loading with mater ials including constr uction and demolition debr is, rock and soil.
BMP - 09 Disturbed soil throughout project including between
structures.
GENERAL REQUIREMENT: ALL ACTIVITIES MUST MEET OP ACITY REQUIREMENTS IN R307-309-5
MAKE AT LEAST ONE SELECTION FROM EACH SECTION.
x
x
x
x
x
x
x
Limit disturbance of soils where possible.:
09-01. Limit disturbance of s oils with the use o f fencing, bar r iers, barricades, and/or wind
barrier s.
09-02. Limit vehicle mileage and reduce speed.
Stabilize and maintain stability of all disturbed soil throu ghou t con struction site.:
09-03. Apply water to stabiliz e disturbed so ils . Soil mo isture must be maintained such that soils
can be wor ked without gener ating fugitive dust.
09-04. Apply and maintain a chemical stabilizer.
09-05. Use wind breaks.
09-06. Apply cover (natur al or synthetic).
BMP - 11 Ha uling ma terials.
GENERAL REQUIREMENT: ALL ACTIVITIES MUST MEET OP ACITY REQUIREMENTS IN R307-309-5
MAKE AT LEAST ONE SELECTION FROM EACH SECTION.
Limit visible du st opacity from veh icu lar operations.:
11-01. Apply and maintain water/chemical suppr essant to operational areas and haul
routes.
11-02. Limit vehicle mileage and speed.
Stabilize materials during transport on site.:
11-03. Use tarps or other suitable enclosures on haul trucks .
11-04. Apply water prior to trans port.
Clean wh eels an d u ndercarriage of h au l tru cks prior to leavin g con struction site.:
11-05. Clean wheels.
11-06. Sweep or water haul r oad.
BMP - 15 Staging areas, equipment stora ge, vehicle pa rking
lots, and ma teria l storage areas.
GENERAL REQUIREMENT: ALL ACTIVITIES MUST MEET OP ACITY REQUIREMENTS IN R307-309-5
MAKE AT LEAST ONE SELECTION FROM EACH SECTION.
x
x
x
x
x
x
Limit visible du st opacity from veh icu lar operations.:
15-01. Limit vehicle mileage and speed limit.
15-02. Apply water on all vehicle trac ar eas in the staging ar eas and unpaved access
routes.
Stabilize stagin g area soils du rin g u se.:
15-03. Pre-water and maintain surface soils in a stabiliz ed condition.
15-04. Apply and maintain a chemical stabilizer to surface s oils.
Stabilize stagin g area soils at project completion .:
15-05. Apply a chemical stabilizer.
15-06. Apply scr eened or washed aggr egate.
15-07. Use wind breaks.
15-08. Pave.
15-09. Completed project will cover s taging area with buildings, paving, and/or landscaping.
15-10. Apply water to form adequate cr ust and pr event acces s .
BMP - 16 Stockpiles materials (storage), other soils, rock or
debris, for future use or export.
GENERAL REQUIREMENT: ALL ACTIVITIES MUST MEET OP ACITY REQUIREMENTS IN R307-309-5
MAKE AT LEAST ONE SELECTION FROM EACH SECTION.
Stabilize su rface soils where support equipmen t an d veh icles will operate.:
16-01. Pre-water and maintain surface soils in a stabiliz ed condition.
16-02. Apply and maintain a chemical stabilizer on s ur face soils.
16-03. Pave area.
Stabilize stockpile materials du rin g h andling.:
16-04. Remove material from the downwind side of the stockpile, when safe to do so.
16-05. Reduce height.
16-06. Create wind scr een
x
x
x
x
x
Stabilize stockpiles after h andling.:
16-07. Water stockpiles to for m a crust immediately.
16-08. Apply and maintain a chemical stabilizer to all outer sur faces of the stockpiles.
16-09. Pro vide and maintain wind barrier s on 3 sides of the pile.
16-10. Apply a cover (natural o r synthetic)
16-11. Wind s creen.
16-12. Avoid steep sides to pr event material slo ughing.
16-13. Reduce height.
BMP - 18 Tra ckout, Prevention a nd clea nup of mud, silt a nd
soil tra cked out onto pa ved roa ds.
GENERAL REQUIREMENT: ALL ACTIVITIES MUST MEET OP ACITY REQUIREMENTS IN R307-309-5
MAKE AT LEAST ONE SELECTION FROM EACH SECTION.
Prevent dust from trackou t.:
18-01. Clean tr ackout at the end of the work shift fr om paved sur faces to maintain dust co ntrol
18-02. Maintain dust contr ol during wo rking hours and clean tracko ut fr om paved sur faces at
the end of the wor k shift/day.
18-03. Install gravel pad(s), clean, well-gr aded gravel or cr ushed rock. Minimum dimensions
must be 30 feet wide by 3 inches deep, and, at minimum, 50' o r the length of the longest haul
tr uck, whichever is greater. Re-screen, wash or apply additional rock in gravel pad to maintain
eectivenes s .
18-04. Install wheel shaker s. Clean wheel shaker s o n a r egular basis to maintain eectiveness.
18-05. Install wheel washers. Maintain wheel was her s o n a r egular basis to maintain
eectivenes s .
18-06. Motoriz ed vehicles will only operate on paved sur faces.
18-07. Install cattle guard before paved road entrance.
All exiting trac mu st be rou ted over selected trackou t con trol device(s).:
18-08. Clearly establish and enforce tr ac patterns to route tr ac over selected tr ackout contr ol
device(s).
18-09. Limit site accessibility to ro utes with trackout contro l devices in place by installing
eective barr iers on unprotected routes.
BMP - 20 Trenching with track or wheel mounted exca vator,
shovel, backhoe or trencher.
GENERAL REQUIREMENT: ALL ACTIVITIES MUST MEET OP ACITY REQUIREMENTS IN R307-309-5
x
x
x
x
x
MAKE AT LEAST ONE SELECTION FROM EACH SECTION.
Presoak soils prior to trench in g activities.:
20-01. Pre-water surface.
Stabilize su rface soils where trench in g equipment, su pport equ ipmen t an d vehicles will
operate.:
20-02. Pre-water and maintain surface soils in a stabiliz ed condition.
20-03. Apply and maintain a chemical stabilizer to surface s oils.
20-04. Limit mileage and speed.
Stabilize soils after trenching.:
20-05. Apply and maintain water on excavated soil.
20-06. Apply and maintain chemical stabilizer on excavated soil.
BMP - 21 Truck loa ding with materials including construction
and demolition debris, rock a nd soil.
GENERAL REQUIREMENT: ALL ACTIVITIES MUST MEET OP ACITY REQUIREMENTS IN R307-309-5
MAKE AT LEAST ONE SELECTION FROM EACH SECTION.
Apply and maintain a ch emical stabilizer on surface soils wh ere loaders, support equipmen t
and vehicles will operate. :
21-01. Pre-water and maintain surface soils in a stabiliz ed condition wher e loader s , s uppo rt
equipment and vehicles will operate.
21-02. Apply and maintain a chemical stabilizer on s ur face soils wher e loaders, support
equipment and vehicles will operate.
21-03. Empty loader bucket slowly and keep loader bucket close to the truck to minimiz e the dro p
height while dumping.
Reviewing Your Pla n
Please carefully review yo ur plan befo re submitting it. Once the plan has
been submitted, it CANNOT be edited.
BEFO RE you submit your plan, if you ne ed to m ake cha nges, navigate back to those
sections via the left navigation or the Previous button to complete those cha nges.
Whe n you are satisfied, submit your plan.
The plan will be available to download in the My Forms section, under the Done
tab.
x
x
x
x
By s ubmitting this plan I agree to the following terms :
A. I am authorized, on be half of the individual or compa ny liste d in Se ction 1, as
Applicant, to apply for a Fugitive Dust Control Plan and to com m it to a ll of the terms and
conditions of the re que ste d pla n.
B. Construction a ctivities will be limited to lands that the applicant e ithe r owns or is
authorize d to use for construction activitie s.
C. The applica nt a cce pts re sponsibility for assuring that all contractors, subcontractors, and
all othe r pe rsons on the construction site covered by this plan, comply with the terms and
conditions of the Fugitive Dust Control Plan.
D. I unde rstand that any false m ate rial state m ent, re presentation or certification made in
this application may invalidate the plan or ca use me to be subject to e nforcement action
pursuant to Utah Code Ann. 19-2-115.
E. Failure to comply with fugitive dust rules m ay result in compliance action and penalties
up to $10,000 pe r violation/day.
Conrmation of terms:
My plan is r eady to be submitted.
Fr equently As ked Questions
Division of Air Quality
Utah Depar tment of Environmental Quality
Feedback
Div isio n of Air Quality
Address: 195 North 1950 West
P.O. Box 144820
Salt Lake City, UT 84114-482
Contact Phone: [phone]
Contact Fax: [phone]
Frequently Asked Questions
Fr equently As ked Questions
Division of Air Quality
Utah Depar tment of Environmental Quality
Feedback
x
Div isio n of Air Quality
Address: 195 North 1950 West
P.O. Box 144820
Salt Lake City, UT 84114-482
Contact Phone: [phone]
Contact Fax: [phone]
Former Sommers Auto Wrecking
Dust Control Form
VISIBLE EMISSION OBSERVATION FORM
Site Name
Address
City State Zip
Process Equipment Operating Mode
Control Equipment Operating Mode
Describe Emission Point

Height of Emission Point Height Relative to Observer

Start End
Distance to Emission Point

Start End
Direction to Emission Point

Start End
Vertical Angle to Observation Pt.
Start End
Direction to Observation Point
Start End
Describe Emissions

Start End
Emission Color

Start End
If Water Droplet Plume (Circle)
Attached Detached N/A
Point In The Plume At Which Opacity Was Determined

Start End
Describe Plume Background

Start End
Background Color

Start End
Sky Condition

Start End
Wind Speed

Start End
Wind Direction

Start End
Ambient Temp

Start End
Relative Humidity %

Additional Information

Continue on reverse side
Observation Date Start Time End Time
Sec Min 0 15 30 45 Comments
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30

Observer’s Name (Print)
Observer’s Signature Date
Organization
Certified by Date

Visible Emission Observation Location Map

Additional Information

Project No.: 2469-002GEnvironmental Science and Engineering
November 2022 Wind Rose Diagram
Former Sommers Auto Wrecking
South Salt Lake, Utah
Date: 8/14/23 Figure 1
Page 1 of 8
UPDES General Permit For
Treated Groundwater and Surface
Water
NOI
Notice of Intent (NOI)
for Coverage Under the
UPDES General Permit for Treated Groundwater and Surface Water
UPDES Permit No. UTG790000
Submission of this Notice of Intent constitutes notice that the party identified in Part II. of this form intends to be authorized
by UPDES General Permit No. UTG790000, issued for discharges of treated water to surface waters in the State of Utah.
Coverage of this permit obligates such dischargers to comply with the terms and conditions of the permit.
PLEASE PROVIDE ALL REQUIRED INFORMATION
You must print or type legibly; forms that are not legible, incomplete, or unsigned will be returned. You must maintain a
copy of the completed NOI form for your records.
PART I. (NOTE: THIS SECTION FOR DIVISION OF WATER QUALITY USE ONLY. Skip to Part II.)
THIS SECTION FOR DIVISION OF WATER QUALITY USE ONLY
Coverage Number:UTG79-
COVERAGE DATES://20 TO //20
RECEIVING WATER:CLASSIFICATION:
ADDITIONAL MONITORING AND/OR EFFLUENT LIMITATIONS:
DIVISION PERMIT OF COVERAGE ISSUANCE:
DATE://20 SIGNATURE:
Once coverage is assigned discharge monitoring reports will be generated and provided to the operator.
PART II. CONTACT INFORMATION (used for permit correspondence)
Organization Name:
Contact Name:Title:
Phone Number:Email:
Mailing Address:Street (PO Box):
City:State:Zip:
Owner/Manager Name:
Phone Number:Email:
Legal Status of Owner/Operator:
Wasatch Environmental, Inc.
Blake Downey V.P.
435-760-8269 [e-mail]
2410 W. California Ave.
Salt Lake City Utah 84104
Mark Bond
Legal Citizen of the U.S.A.
[e-mail]801-301-1146
0107
07 14 24 07 14 25
Golf of the Round Pond via Storm drain Category 3
Barium Copper Zinc
Arsenic
7 12 24
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 2 of 8
PART III. PROJECT SITE LOCATION
Project Lead Name:Project Lead Phone:
Project Site Name:
Project Street/Location:
City:County:State:UTAH Zip:
Project Site Phone:
Project latitude and longitude location in degree decimal.
Latitude Longitude
PART IV. PROJECT DESCRIPTION
Description of cleanup site, including a description of the source(s) of contamination and the extent of contamination
and any additional contamination anticipated in the local groundwater from other possible sources:
PART V. MAP
Attach a topographical map of the area extending to at least 1 mile beyond the property boundaries. The map must show the
outline of the facility, the location of each of its existing and proposed intake and discharge structures, each of its waste
treatment, storage, or disposal facilities, and discharge locations. Include all springs, rivers, and other surface water bodies in
the map.
Map Attached
PART VI. PROJECT DATES
Filing your permit will grant you one year of coverage from the filing date regardless of the project duration outlined below.
If you project ends early, you must file a Notice of Termination (NOT).
Project Start Date://20
Project Completion Date://20
Notes:
Blake Downey 435-760-8269
Former Sommers Auto
647 West 3300 South
South Salt Lake Salt Lake 84119
801-301-1146
40.698807 -111.910399
This site is a former automotive salvage wrecking yard that had above ground storage tanks that contained gasoline and
diesel. The tanks had a release of fuel, and lead and arsenic have been detected in the soils as well. Groundwater flows
to the northwest, but the impacts appear to be located on the southwest corner of the property. Wasatch plans to complete
on-site remediation which will include dewatering a soil excavation into frac tanks to be aerated then discharged through
a bag filter and granular activated carbon vessel prior to remove residual contaminants before discharge into the storm
water system.
X
07 15 24
09 30 24 **This is an estimated date range and may vary.
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 3 of 8
PART VII. DISCHARGE LOCATION(S)
List the Latitude and Longitude of the Discharge Point(s) in degree decimal with the Receiving Water.
Outfall No.Latitude Longitude Receiving Surface Waters (Name)
Are any of the discharge points located in the Colorado River Basin?Yes No
Does the receiving water designated uses include Class 1C drinking water as defined by R317-2-
13?Yes No
Class 1C waters are “Protected for domestic purposes with prior treatment by treatment processes as required by the
Utah Division of Drinking Water”.
Is the project located on tribal lands?Yes No
If the facility is located on Tribal Lands the permittee must contact EPA Region VIII except for facilities on the
Navajo Reservation or the Goshute Reservation, for which the permittee must contact EPA Region IX.
Does the discharge flow into a storm drain before entering the receiving water body?Yes No
Be Advised: Discharges to storm drains must be approved by the storm drain authority/owner.
Is the project part of the Utah Voluntary Cleanup Program (VCP)?Yes No
Description of Discharge location and conveyance system to live water:
PART VIII. INFLUENT AND EFFLUENT CONCENTRATIONS
Complete attached Table A and list any additional pollutants (not included in Table A) with influent and/or effluent
concentrations here:


X
X
1
2 (backup)40.699686 -111.910179
40.698257 -111.911111 The ponds at Golf the Round
The ponds at Golf the Round
X
Treated groundwater would be pumped to a storm drain located just west of the southwest corner of the project site.
According to South Salt Lake Public Works drawings of the storm sewer drians and lines, this discharge point flows to the
north and outfalls into the ponds located at the Golf the Round golf course.
TPH-DRO (Average (3 samples) 7.63 mg/L for influent)
TPH-GRO (Average (3 samples) 13.57 mg/L for influent)
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 4 of 8
PART VIII. INFLUENT AND EFFLUENT CONCENTRATIONS continued
Discharge IS to Class 1C Water:
1. In addition to completing Table A, influent sampling including total toxic organics (TTO results must be attached.
See attached Table B for list of TTO constituents. No permits for discharge to Class 1C Waters will be issued prior
to influent sampling being conducted and results received.
2. An analysis of alternative disposal methods of the treated groundwater must be attached. This analysis must include
an economic comparison of the alternative disposal methods. If no other disposal methods are feasible the analysis
must demonstrated the consideration of other methods such as trucking and/or discharge to a treatment facility.
3.
Discharge is NOT to Class 1C Water:
1. In addition to completing Table A, influent sampling including total toxic organics OR a report documenting why
influent sampling is not needed for this project and an estimation of anticipated influent constituents concentrations.
2. In accordance with Part I.D. the permittee may petition Total Petroleum Hydrocarbon (TPH-GRO and TPH-DRO)
analyses may be substituted for the TTO analyses. If approved maximum daily effluent limitations of 1.0 mg/LTPH-
GRO and TPH-DRO will be substituted for the TTO effluent limitation.
PART IX. DESCRIPTION OF TREATMENT SYSTEM
Description of the current or proposed treatment system, including discharge flow rate (attach a flow diagram):
FLOW DIAGRAM ATTACHED
PART X. CERTIFICATION AND SIGNATURE
I certify under penalty of law that this submission was prepared under my direction or supervision in accordance with
a system designed to assure that qualified personnel properly gather and evaluate the information submitted. Based on
my inquiry of the person or persons who manage the system, or those person(s) directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate, and complete. I am
aware that there are significant penalties for submitted false information, including the possibility of fine and
imprisonment for knowing violations. I further certify that the applicant has sufficient title, right or interest in the
property where the proposed activity occurs.
PRINT Signatory
Authority Signature Title Date
X
Groundwater would be pumped from the excavation into two 21,000 gallon frac tanks. The groundwater would be aerated
within the frac tanks and then pumped through a bag filter unit to remove sediments, and then through a granular activated
carbon vessel to remove any remaining contaminants. Then the treated groundwater would be discharged through the
South Salt Lake storm sewer system.
Blake B. Downey Vice President 6-24-24
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 5 of 8
PART XI. ADDITIONAL APPLICATIONS AND APPROVALS
1. You may need to file for a temporary application to appropriate water rights form the Division of Water
Rights. Call 801.583.7240 for more information.
2. You may need to obtain approval from the Division of Air Quality if any air stripping equipment is to be
employed at the cleanup site. Call 801.536.4000 for more information.
The Division of Water Quality may request addition information.
Important:
The UPDES Permit Application, must be signed as follows: (Refer to Part IV.G. Signatory Requirements, of the General
Permit.)
1) For a corporation, a responsible corporate officer shall sign the NOT, a responsible corporate officer means:
a. A President, secretary, treasurer, or vice-president of the corporation in charge of a principal business function, or
any other person who performs similar policy- or decision-making functions for the corporation; or
b. The manager of one or more manufacturing, production, or operating facilities, if
i. The manager is authorized to make management decisions that govern the operation of the regulated facility,
including having the explicit or implicit duty of making major capital investment recommendations, and
initiating and directing other comprehensive measures to assure long term environmental compliance with
environmental statutes and regulations:
ii. The manager can ensure that the necessary systems are established or actions taken to gather complete and
accurate information for permit application requirements; and
iii. Authority to sign documents has been assigned or delegated to the manager in accordance with corporate
procedures.
2) For a partnership of sole proprietorship, the general partner or the proprietor, respectively; or
3) For a municipality, state or other public agency, either a principal executive officer or ranking elected official shall sign
the application; in this subsection, a principal executive officer of any agency means;
a. The chief executive officer of the agency; or
b. A senior executive officer having responsibility for the overall operations of a principal geographic unit or division
of the agency.
Where to File the UPDES Permit Application form:
Please submit the original form with signature via the DWQ Electronic Documents Submission Portal:
https://deq.utah.gov/water-quality/water-quality-electronic-submissions
You can also send by mail or hand deliver to the below address. Remember to retain a copy for your records.
Division of Water Quality
Department of Environmental Quality
195 North 1950 West
PO Box 144870
Salt Lake City, UT 84114-4870
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 6 of 8
TABLE A
Analysis of Treatment System Influent and Effluent
You must report concentrations for each pollutant listed. Please refer to Part I.D. and Part I.E. of the permit or
NOI to determine if actual influent values are required or if estimated values will be accepted.
Are influent values:Estimated Or Actual
Are effluent values:Estimated Or Actual
Influent Effluent
Parameters Avg
(mg/L)
Max
(mg/L)
Number of
Samples
Avg
(mg/L)
Max
(mg/L)
Number of
Samples
pH (range in standard units)
Total Suspended Solids
Total Dissolved Solids
Total Lead
Oil & Grease
Benzene
Toluene
Ethylbenzene
Xylenes
Naphthalene
MTBE
TTO’s
(attach full list if required)
Given this is a fuel release from an AST we request to sample for TPH-GRO and
TPH-DRO instead of TTO, with an effluent limit of <1.0 mg/L.
X
XX
6.9 7.2 Estimated 7.0 7.5 Est.
<0.00200 <0.00200 3 <0.00200 <0.00200 Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.<70 <70
<1,200 <1,200
Est.
Est.800 900
65 70
<10 <10
<0.005 <0.005
<0.2 <0.2
<0.7 <0.7
<0.1 <0.1
<0.1 <0.1
<0.1 <0.1
14.24.79 3
2.910.975 3
10.73.59 3
0.609 30.251
0.0247 30.0144
0.888 30.297
28.685.54
See attached data report, only samples GP-14, GP-15, and GP-16 apply.
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 7 of 8
TABLE B
Metals Detection to Determine Required Monitoring
Effluent Characteristics Results (mg/L)Effluent Limitations (mg/L)
Arsenic 0.01 / 0.10
Barium 1.0
Beryllium 0.0004
Cadmium 0.026
Chromium 0.05 / 0.10
Copper 0.003
Mercury 0.002
Selenium 0.05
Silver 0.05
Zinc 0.04
0.307
0.332
Not sampled for
Not sampled for
Not sampled for
<0.00200
<0.00200
<0.0000900
<0.0400
<0.000700
Max Detection
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 8 of 8
TABLE C
Total Toxic Organic List
(These are the parameters that shall be analyzed for initially determining the total toxic organic (TTO) concentration of the wastewater)
Volatile Organic Compounds
Acrolein
Acrylonitrile
Benzene
Bromoform
Carbon Tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-Chloroethylvinyl Ether
Chloroform
Dichlorobromomethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethylene
1,2-Dichloropropane
1,3-Dichloropropylene
Ethylbenzene
Methyl Bromide
Methyl Chloride
Methylene Chloride
1,1,2,2-Tetrachloroethane
Tetrachloroethylene
Toluene
1,2-Cis,Trans- Dichloroethylene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethylene
Vinyl Chloride
Semi-Volatile Organic
Compounds
2-Chlorophenol
2,4-Dichlorophenol
2,4-Dimethylphenol
4,6-Dinitro-O-Cresol
2,4-Dinitrophenol
2-Nitrophenol
4-Nitrophenol
P-Chloro-M-Cresol
Pentachlorophenol
Phenol
2,4,6-Trichlorophenol
Acenaphthene
Acenaphthylene
Anthracene
Benzidine
Benzo(A)Anthracene
Benzo(A)Pyrene
3,4-Benzofluoranthene
Benzo(Ghi)Perylene
Benzo(K)Fluoranthene
Bis(2-Chloroethoxy)Methane
Bis(2-Chloroethyl)Ether
Bis(2-Chloroisopropyl)Ether
Bis (2-Ethylhexyl)Phthalate
4-Bromophenyl Phenyl Ether
Butylbenzyl Phthalate
2-Chloronaphthalene
Ether
4-Chlorophenyl Phenyl
Chrysene
Dibenzo(A,H)Anthracene
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
3,3′-Dichlorobenzidine
Diethyl Phthalate
Dimethyl Phthalate
Di-N-Butyl Phthalate
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Di-N-Octyl Phthalate
1,2-Diphenylhydrazine (As Azobenzene)
Fluroranthene
Fluorene
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachloroethane
Indeno(1,2,3-Cd)Pyrene
Isophorone
Napthalene
Nitrobenzene
N-Nitrosodimethylamine
N-Nitrosodi-N-Propylamine
N-Nitrosodiphenylamine
Phenanthrene
Pyrene
1,2,4-Trichlorobenzene
Pesticides and PCBs
Aldrin
Alpha-Bhc
Beta-Bhc
Gamma-Bhc
Delta-Bhc
Chlordane
4,4′-Ddt
4,4′-Dde
4,4′-Ddd
Dieldrin
Alpha-Endosulfan
Beta-Endosulfan
Endosulfan Sulfate
Endrin
Endrin Aldehyde
Heptachlor
Heptachlor Epoxide
Pcb-1242
Pcb-1254
Pcb-1221
Pcb-1232
Pcb-1248
Pcb-1260
Pcb-1016
Toxaphene
FIGURE
1
DRAWING DATEPROJECT NO.
Environmental Science and Engineering
Arrieta Property
Grange Property
Topographic Map of Facility
2469-002H June 24, 2024
Former Sommers Auto
647 West 3300 South
South Salt Lake, Utah
Scale: 1-inch equals
approximately 770 feet
Approximate Facility Boundary
Excavation and Dewatering Area
Groundwater Treatment Area
Discharge Area
FIGURE
2
DRAWING DATEPROJECT NO.
Environmental Science and Engineering
Proposed Soil Excavation Area
Remediation Process Map
2469-002H June 24, 2024
Scale: 1-inch equals
approximately 80 feet
Dump Truck Haul Pathway
Proposed Frack-Tank Location
and Area of Groundwater Treatment
Approximate Site Boundary
3200 South
3300 South
Filter Unit and
GAC Vessel
Groundwater Treatment Flow Path
Storm Drain (Discharge Location)
Proposed Track-Out Pad
Former Sommers Auto
647 West 3300 South
South Salt Lake, Utah
Backup Storm Drain
(Discharge Location)

195 North 1950 West • Salt Lake City, UT
Mailing Address: P.O. Box 144870 • Salt Lake City, UT 84114-4870
Telephone [phone] • Fax [phone] TDD [phone]
www.deq.utah.gov
Printed on 100% recycled paper
State of Utah

Department of
Environmental Quality

Kimberly D. Shelley
Executive Director

DIVISION OF WATER QUALITY
John Mackey, P.E.
Interim Director

SPENCER J. COX
Governor

DEIDRE HENDERSON
Lieutenant Governor
July 16, 2024

VIA EMAIL
READ RECEIPT REQUESTED

Blake Downey
Vice President
Wasatch Environmental, Inc.
2410 West California Avenue
Salt Lake City, Utah, 84104

Subject: UPDES General Permit Coverage No. UTG790107
Former Sommers Auto, Salt Lake City, Utah

Dear Mr. Downey:

Enclosed is a signed copy of the Utah Pollutant Discharge Elimination System (UPDES) General
Permit Notice of Intent (NOI), which combined with this letter, authorizes discharges for the facility
referenced above. Coverage under the Treated Groundwater and Surface Water General Permit for
this facility is referred to as UPDES permit number UTG790107. The conditions and requirements
of the permit will be effective for one year beginning July 16, 2024. For reference, a copy of the
general permit is available at: https://deq.utah.gov/water-quality/current-permits-and-forms-updes-
permitting-program#general-treated-gw.
After reviewing your NOI and associated information, it was determined that effluent monitoring
and limits will be required as described in section I.E of the Treated Groundwater and Surface Water
General Permit. Effluent monitoring will also be required for Arsenic, Barium, Copper, and Zinc.
The Division of Water Quality (DWQ) approves the request to monitor for TPH-GRO and TPH-
DRO in lieu of the Total Toxic Organics (TTO) monitoring requirement. Prior to the first discharge
event, the facility must submit the required sampling analysis in section I.E., and the additional
required metals from a representative sample of treated effluent water. The initial monitoring shall
be sent via email to [e-mail]. After the facility has provided the initial monitoring results
and has received the DWQ approval, the facility is authorized to discharge.
Page 2
UTG790107
Former Sommers Auto
Monitoring and Limit requirements for Permit No. UTG790107 are as follows:
The permit requires that monitoring results be summarized and reported on a Discharge Monitoring
Report (DMR). The DMR shall be submitted electronically monthly the Environmental Protection
Agency’s (EPA) electronic reporting system: NetDMR https://npdes-ereporting.epa.gov/net-
netdmr. The DMR is due by the 28th day of each month for the previous month’s discharge
activity. When discharging activities cease, please notify the Division by submitting a Notice of
Termination form, which can also be obtained at: https://deq.utah.gov/water-quality/current-
permits-and-forms-updes-permitting-program#general
UPDES General Permit Coverage for the Discharge of Treated Groundwater is for 12 months or
less. Within 6 months of permit issuance, please evaluate your discharge timeline. If dewatering
discharges are expected to extend greater than 12 months from the issuance date, an individual
permit will need to be obtained. Individual permits require 6 months for issuance. Please keep DWQ
informed of your project status.
A fee schedule was included in the Utah Department of Environmental Quality Budget
appropriation request at the direction of the Legislature and in accordance with Utah Code annotated
19-1-201. The fee schedule, as approved by the legislature, includes a fee for the General Permit
for Treated Groundwater and Surface Water of $ 601.00 per year (see attached invoice). Please
submit payment within 30 days of permit issuance to:
Effluent Characteristics Effluent Limitations a Monitoring Requirement
Daily
Minimum
Daily
Maximum
Average
Weekly d
Average
Monthly
d
Measurement
requirement
Sample
Type
Flow, million gallons per day (mgd) 1 2/Month e Measured
pH, standard units (SU) 6.5 9.0 2/Month e Measured
Total Suspended Solids (TSS), mg/L 70 35 25 Monthly Grab
Total Dissolved Solids (TDS), mg/L 1,200 Monthly Grab
Total Recoverable Lead, mg/L 0.005 Monthly Grab
Oil & Grease, mg/L h 10 Monthly Grab
Benzene, mg/L 0.005 2/Month e Grab
BTEX, mg/L i 0.1 2/Month e Grab
MTBE, mg/L 0.2 2/Month e Grab
Naphthalene, mg/L 0.7 Monthly Grab
TPH- GRO, mg/L l 1.0 Monthly Grab
TPH-DRO, mg/L l 1.0 Monthly Grab
Arsenic, mg/L 0.10 Monthly Grab
Barium, mg/L 1.0 Monthly Grab
Copper, mg/L 0.003 Monthly Grab
Zinc, mg/L 0.04 Monthly Grab
Page 3
UTG790107
Former Sommers Auto

Department of Environmental Quality
Division of Water Quality
Attn: Susan Woeppel
PO Box 144870
Salt Lake City, Utah 84114-4870

Payment may also be made online via the Payment Portal at https://deq.utah.gov/general/payment-
portal Water Quality Shopping Cart by selecting Invoice Payment. Please be sure to include the
invoice number with either method of remittance.

Please keep DWQ informed of your project status, especially during discharging events for
coordination of potential future inspections. If you have any questions with regards to this matter,
please contact Linsey Shafer at [phone] or at [e-mail].

Sincerely.

Linsey Shafer
Permit Writer
Utah Division of Water Quality

Enclosures: 1. Signed NOI for UTG790107 (DWQ-2024-0055235)
2. Invoice # 257-4 (DWQ-2024-005347)

Cc: Via Email

Mark Bond, Owner, Former Sommers Auto Remediation Site
Corby Talbot, Division Manager, South Salt Lake
Dennis Pay, City Engineer, South Salt Lake
Ron Lund, Environmental Director, Salt Lake County Public Health
Baylie Nusink, Environmental Scientist, Division of Water Quality

DWQ-2024-005236

The use or reuse of this information is restricted to the referenced document unless otherwise authorized.
Wasatch Environmental Copyright 2006
Figure 1Site Map and Proposed Excavation Map
SOMMERS AUTO WRECKING WEI 2469-002G
1 inch is equal
to 50 feet
70
0

W
es
t
Proposed Excavation Area
EXC-2
(0.01 acres)
EXC-3
(0.01 acres)
EXC-1
(0.22 acres)
EXC-4
(0.20 acres)
Approximate Site Boundary
Equipment Storage
Area (0.07 acres)
3300 South
South Salt Lake
Storm Water Drain
Former Sommers Auto Wrecking
Dust Control Form
VISIBLE EMISSION OBSERVATION FORM
Site Name
Address
City State Zip
Process Equipment Operating Mode
Control Equipment Operating Mode
Describe Emission Point

Height of Emission Point Height Relative to Observer

Start End
Distance to Emission Point

Start End
Direction to Emission Point

Start End
Vertical Angle to Observation Pt.
Start End
Direction to Observation Point
Start End
Describe Emissions

Start End
Emission Color

Start End
If Water Droplet Plume (Circle)
Attached Detached N/A
Point In The Plume At Which Opacity Was Determined

Start End
Describe Plume Background

Start End
Background Color

Start End
Sky Condition

Start End
Wind Speed

Start End
Wind Direction

Start End
Ambient Temp

Start End
Relative Humidity %

Additional Information

Continue on reverse side
Observation Date Start Time End Time
Sec Min 0 15 30 45 Comments
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30

Observer’s Name (Print)
Observer’s Signature Date
Organization
Certified by Date

Visible Emission Observation Location Map

Additional Information

Project No.: 2469-002GEnvironmental Science and Engineering
November 2022 Wind Rose Diagram
Former Sommers Auto Wrecking
South Salt Lake, Utah
Date: 8/14/23 Figure 1
Page 1 of 8
UPDES General Permit For
Treated Groundwater and Surface
Water
NOI
Notice of Intent (NOI)
for Coverage Under the
UPDES General Permit for Treated Groundwater and Surface Water
UPDES Permit No. UTG790000
Submission of this Notice of Intent constitutes notice that the party identified in Part II. of this form intends to be authorized
by UPDES General Permit No. UTG790000, issued for discharges of treated water to surface waters in the State of Utah.
Coverage of this permit obligates such dischargers to comply with the terms and conditions of the permit.
PLEASE PROVIDE ALL REQUIRED INFORMATION
You must print or type legibly; forms that are not legible, incomplete, or unsigned will be returned. You must maintain a
copy of the completed NOI form for your records.
PART I. (NOTE: THIS SECTION FOR DIVISION OF WATER QUALITY USE ONLY. Skip to Part II.)
THIS SECTION FOR DIVISION OF WATER QUALITY USE ONLY
Coverage Number:UTG79-
COVERAGE DATES://20 TO //20
RECEIVING WATER:CLASSIFICATION:
ADDITIONAL MONITORING AND/OR EFFLUENT LIMITATIONS:
DIVISION PERMIT OF COVERAGE ISSUANCE:
DATE://20 SIGNATURE:
Once coverage is assigned discharge monitoring reports will be generated and provided to the operator.
PART II. CONTACT INFORMATION (used for permit correspondence)
Organization Name:
Contact Name:Title:
Phone Number:Email:
Mailing Address:Street (PO Box):
City:State:Zip:
Owner/Manager Name:
Phone Number:Email:
Legal Status of Owner/Operator:
Wasatch Environmental, Inc.
Blake Downey V.P.
435-760-8269 [e-mail]
2410 W. California Ave.
Salt Lake City Utah 84104
Mark Bond
Legal Citizen of the U.S.A.
[e-mail]801-301-1146
0107
07 14 24 07 14 25
Golf of the Round Pond via Storm drain Category 3
Barium Copper Zinc
Arsenic
7 12 24
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 2 of 8
PART III. PROJECT SITE LOCATION
Project Lead Name:Project Lead Phone:
Project Site Name:
Project Street/Location:
City:County:State:UTAH Zip:
Project Site Phone:
Project latitude and longitude location in degree decimal.
Latitude Longitude
PART IV. PROJECT DESCRIPTION
Description of cleanup site, including a description of the source(s) of contamination and the extent of contamination
and any additional contamination anticipated in the local groundwater from other possible sources:
PART V. MAP
Attach a topographical map of the area extending to at least 1 mile beyond the property boundaries. The map must show the
outline of the facility, the location of each of its existing and proposed intake and discharge structures, each of its waste
treatment, storage, or disposal facilities, and discharge locations. Include all springs, rivers, and other surface water bodies in
the map.
Map Attached
PART VI. PROJECT DATES
Filing your permit will grant you one year of coverage from the filing date regardless of the project duration outlined below.
If you project ends early, you must file a Notice of Termination (NOT).
Project Start Date://20
Project Completion Date://20
Notes:
Blake Downey 435-760-8269
Former Sommers Auto
647 West 3300 South
South Salt Lake Salt Lake 84119
801-301-1146
40.698807 -111.910399
This site is a former automotive salvage wrecking yard that had above ground storage tanks that contained gasoline and
diesel. The tanks had a release of fuel, and lead and arsenic have been detected in the soils as well. Groundwater flows
to the northwest, but the impacts appear to be located on the southwest corner of the property. Wasatch plans to complete
on-site remediation which will include dewatering a soil excavation into frac tanks to be aerated then discharged through
a bag filter and granular activated carbon vessel prior to remove residual contaminants before discharge into the storm
water system.
X
07 15 24
09 30 24 **This is an estimated date range and may vary.
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 3 of 8
PART VII. DISCHARGE LOCATION(S)
List the Latitude and Longitude of the Discharge Point(s) in degree decimal with the Receiving Water.
Outfall No.Latitude Longitude Receiving Surface Waters (Name)
Are any of the discharge points located in the Colorado River Basin?Yes No
Does the receiving water designated uses include Class 1C drinking water as defined by R317-2-
13?Yes No
Class 1C waters are “Protected for domestic purposes with prior treatment by treatment processes as required by the
Utah Division of Drinking Water”.
Is the project located on tribal lands?Yes No
If the facility is located on Tribal Lands the permittee must contact EPA Region VIII except for facilities on the
Navajo Reservation or the Goshute Reservation, for which the permittee must contact EPA Region IX.
Does the discharge flow into a storm drain before entering the receiving water body?Yes No
Be Advised: Discharges to storm drains must be approved by the storm drain authority/owner.
Is the project part of the Utah Voluntary Cleanup Program (VCP)?Yes No
Description of Discharge location and conveyance system to live water:
PART VIII. INFLUENT AND EFFLUENT CONCENTRATIONS
Complete attached Table A and list any additional pollutants (not included in Table A) with influent and/or effluent
concentrations here:


X
X
1
2 (backup)40.699686 -111.910179
40.698257 -111.911111 The ponds at Golf the Round
The ponds at Golf the Round
X
Treated groundwater would be pumped to a storm drain located just west of the southwest corner of the project site.
According to South Salt Lake Public Works drawings of the storm sewer drians and lines, this discharge point flows to the
north and outfalls into the ponds located at the Golf the Round golf course.
TPH-DRO (Average (3 samples) 7.63 mg/L for influent)
TPH-GRO (Average (3 samples) 13.57 mg/L for influent)
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 4 of 8
PART VIII. INFLUENT AND EFFLUENT CONCENTRATIONS continued
Discharge IS to Class 1C Water:
1. In addition to completing Table A, influent sampling including total toxic organics (TTO results must be attached.
See attached Table B for list of TTO constituents. No permits for discharge to Class 1C Waters will be issued prior
to influent sampling being conducted and results received.
2. An analysis of alternative disposal methods of the treated groundwater must be attached. This analysis must include
an economic comparison of the alternative disposal methods. If no other disposal methods are feasible the analysis
must demonstrated the consideration of other methods such as trucking and/or discharge to a treatment facility.
3.
Discharge is NOT to Class 1C Water:
1. In addition to completing Table A, influent sampling including total toxic organics OR a report documenting why
influent sampling is not needed for this project and an estimation of anticipated influent constituents concentrations.
2. In accordance with Part I.D. the permittee may petition Total Petroleum Hydrocarbon (TPH-GRO and TPH-DRO)
analyses may be substituted for the TTO analyses. If approved maximum daily effluent limitations of 1.0 mg/LTPH-
GRO and TPH-DRO will be substituted for the TTO effluent limitation.
PART IX. DESCRIPTION OF TREATMENT SYSTEM
Description of the current or proposed treatment system, including discharge flow rate (attach a flow diagram):
FLOW DIAGRAM ATTACHED
PART X. CERTIFICATION AND SIGNATURE
I certify under penalty of law that this submission was prepared under my direction or supervision in accordance with
a system designed to assure that qualified personnel properly gather and evaluate the information submitted. Based on
my inquiry of the person or persons who manage the system, or those person(s) directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate, and complete. I am
aware that there are significant penalties for submitted false information, including the possibility of fine and
imprisonment for knowing violations. I further certify that the applicant has sufficient title, right or interest in the
property where the proposed activity occurs.
PRINT Signatory
Authority Signature Title Date
X
Groundwater would be pumped from the excavation into two 21,000 gallon frac tanks. The groundwater would be aerated
within the frac tanks and then pumped through a bag filter unit to remove sediments, and then through a granular activated
carbon vessel to remove any remaining contaminants. Then the treated groundwater would be discharged through the
South Salt Lake storm sewer system.
Blake B. Downey Vice President 6-24-24
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 5 of 8
PART XI. ADDITIONAL APPLICATIONS AND APPROVALS
1. You may need to file for a temporary application to appropriate water rights form the Division of Water
Rights. Call 801.583.7240 for more information.
2. You may need to obtain approval from the Division of Air Quality if any air stripping equipment is to be
employed at the cleanup site. Call 801.536.4000 for more information.
The Division of Water Quality may request addition information.
Important:
The UPDES Permit Application, must be signed as follows: (Refer to Part IV.G. Signatory Requirements, of the General
Permit.)
1) For a corporation, a responsible corporate officer shall sign the NOT, a responsible corporate officer means:
a. A President, secretary, treasurer, or vice-president of the corporation in charge of a principal business function, or
any other person who performs similar policy- or decision-making functions for the corporation; or
b. The manager of one or more manufacturing, production, or operating facilities, if
i. The manager is authorized to make management decisions that govern the operation of the regulated facility,
including having the explicit or implicit duty of making major capital investment recommendations, and
initiating and directing other comprehensive measures to assure long term environmental compliance with
environmental statutes and regulations:
ii. The manager can ensure that the necessary systems are established or actions taken to gather complete and
accurate information for permit application requirements; and
iii. Authority to sign documents has been assigned or delegated to the manager in accordance with corporate
procedures.
2) For a partnership of sole proprietorship, the general partner or the proprietor, respectively; or
3) For a municipality, state or other public agency, either a principal executive officer or ranking elected official shall sign
the application; in this subsection, a principal executive officer of any agency means;
a. The chief executive officer of the agency; or
b. A senior executive officer having responsibility for the overall operations of a principal geographic unit or division
of the agency.
Where to File the UPDES Permit Application form:
Please submit the original form with signature via the DWQ Electronic Documents Submission Portal:
https://deq.utah.gov/water-quality/water-quality-electronic-submissions
You can also send by mail or hand deliver to the below address. Remember to retain a copy for your records.
Division of Water Quality
Department of Environmental Quality
195 North 1950 West
PO Box 144870
Salt Lake City, UT 84114-4870
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 6 of 8
TABLE A
Analysis of Treatment System Influent and Effluent
You must report concentrations for each pollutant listed. Please refer to Part I.D. and Part I.E. of the permit or
NOI to determine if actual influent values are required or if estimated values will be accepted.
Are influent values:Estimated Or Actual
Are effluent values:Estimated Or Actual
Influent Effluent
Parameters Avg
(mg/L)
Max
(mg/L)
Number of
Samples
Avg
(mg/L)
Max
(mg/L)
Number of
Samples
pH (range in standard units)
Total Suspended Solids
Total Dissolved Solids
Total Lead
Oil & Grease
Benzene
Toluene
Ethylbenzene
Xylenes
Naphthalene
MTBE
TTO’s
(attach full list if required)
Given this is a fuel release from an AST we request to sample for TPH-GRO and
TPH-DRO instead of TTO, with an effluent limit of <1.0 mg/L.
X
XX
6.9 7.2 Estimated 7.0 7.5 Est.
<0.00200 <0.00200 3 <0.00200 <0.00200 Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.<70 <70
<1,200 <1,200
Est.
Est.800 900
65 70
<10 <10
<0.005 <0.005
<0.2 <0.2
<0.7 <0.7
<0.1 <0.1
<0.1 <0.1
<0.1 <0.1
14.24.79 3
2.910.975 3
10.73.59 3
0.609 30.251
0.0247 30.0144
0.888 30.297
28.685.54
See attached data report, only samples GP-14, GP-15, and GP-16 apply.
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 7 of 8
TABLE B
Metals Detection to Determine Required Monitoring
Effluent Characteristics Results (mg/L)Effluent Limitations (mg/L)
Arsenic 0.01 / 0.10
Barium 1.0
Beryllium 0.0004
Cadmium 0.026
Chromium 0.05 / 0.10
Copper 0.003
Mercury 0.002
Selenium 0.05
Silver 0.05
Zinc 0.04
0.307
0.332
Not sampled for
Not sampled for
Not sampled for
<0.00200
<0.00200
<0.0000900
<0.0400
<0.000700
Max Detection
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 8 of 8
TABLE C
Total Toxic Organic List
(These are the parameters that shall be analyzed for initially determining the total toxic organic (TTO) concentration of the wastewater)
Volatile Organic Compounds
Acrolein
Acrylonitrile
Benzene
Bromoform
Carbon Tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-Chloroethylvinyl Ether
Chloroform
Dichlorobromomethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethylene
1,2-Dichloropropane
1,3-Dichloropropylene
Ethylbenzene
Methyl Bromide
Methyl Chloride
Methylene Chloride
1,1,2,2-Tetrachloroethane
Tetrachloroethylene
Toluene
1,2-Cis,Trans- Dichloroethylene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethylene
Vinyl Chloride
Semi-Volatile Organic
Compounds
2-Chlorophenol
2,4-Dichlorophenol
2,4-Dimethylphenol
4,6-Dinitro-O-Cresol
2,4-Dinitrophenol
2-Nitrophenol
4-Nitrophenol
P-Chloro-M-Cresol
Pentachlorophenol
Phenol
2,4,6-Trichlorophenol
Acenaphthene
Acenaphthylene
Anthracene
Benzidine
Benzo(A)Anthracene
Benzo(A)Pyrene
3,4-Benzofluoranthene
Benzo(Ghi)Perylene
Benzo(K)Fluoranthene
Bis(2-Chloroethoxy)Methane
Bis(2-Chloroethyl)Ether
Bis(2-Chloroisopropyl)Ether
Bis (2-Ethylhexyl)Phthalate
4-Bromophenyl Phenyl Ether
Butylbenzyl Phthalate
2-Chloronaphthalene
Ether
4-Chlorophenyl Phenyl
Chrysene
Dibenzo(A,H)Anthracene
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
3,3′-Dichlorobenzidine
Diethyl Phthalate
Dimethyl Phthalate
Di-N-Butyl Phthalate
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Di-N-Octyl Phthalate
1,2-Diphenylhydrazine (As Azobenzene)
Fluroranthene
Fluorene
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachloroethane
Indeno(1,2,3-Cd)Pyrene
Isophorone
Napthalene
Nitrobenzene
N-Nitrosodimethylamine
N-Nitrosodi-N-Propylamine
N-Nitrosodiphenylamine
Phenanthrene
Pyrene
1,2,4-Trichlorobenzene
Pesticides and PCBs
Aldrin
Alpha-Bhc
Beta-Bhc
Gamma-Bhc
Delta-Bhc
Chlordane
4,4′-Ddt
4,4′-Dde
4,4′-Ddd
Dieldrin
Alpha-Endosulfan
Beta-Endosulfan
Endosulfan Sulfate
Endrin
Endrin Aldehyde
Heptachlor
Heptachlor Epoxide
Pcb-1242
Pcb-1254
Pcb-1221
Pcb-1232
Pcb-1248
Pcb-1260
Pcb-1016
Toxaphene
FIGURE
1
DRAWING DATEPROJECT NO.
Environmental Science and Engineering
Arrieta Property
Grange Property
Topographic Map of Facility
2469-002H June 24, 2024
Former Sommers Auto
647 West 3300 South
South Salt Lake, Utah
Scale: 1-inch equals
approximately 770 feet
Approximate Facility Boundary
Excavation and Dewatering Area
Groundwater Treatment Area
Discharge Area
FIGURE
2
DRAWING DATEPROJECT NO.
Environmental Science and Engineering
Proposed Soil Excavation Area
Remediation Process Map
2469-002H June 24, 2024
Scale: 1-inch equals
approximately 80 feet
Dump Truck Haul Pathway
Proposed Frack-Tank Location
and Area of Groundwater Treatment
Approximate Site Boundary
3200 South
3300 South
Filter Unit and
GAC Vessel
Groundwater Treatment Flow Path
Storm Drain (Discharge Location)
Proposed Track-Out Pad
Former Sommers Auto
647 West 3300 South
South Salt Lake, Utah
Backup Storm Drain
(Discharge Location)

195 North 1950 West • Salt Lake City, UT
Mailing Address: P.O. Box 144870 • Salt Lake City, UT 84114-4870
Telephone [phone] • Fax [phone] TDD [phone]
www.deq.utah.gov
Printed on 100% recycled paper
State of Utah

Department of
Environmental Quality

Kimberly D. Shelley
Executive Director

DIVISION OF WATER QUALITY
John Mackey, P.E.
Interim Director

SPENCER J. COX
Governor

DEIDRE HENDERSON
Lieutenant Governor
July 16, 2024

VIA EMAIL
READ RECEIPT REQUESTED

Blake Downey
Vice President
Wasatch Environmental, Inc.
2410 West California Avenue
Salt Lake City, Utah, 84104

Subject: UPDES General Permit Coverage No. UTG790107
Former Sommers Auto, Salt Lake City, Utah

Dear Mr. Downey:

Enclosed is a signed copy of the Utah Pollutant Discharge Elimination System (UPDES) General
Permit Notice of Intent (NOI), which combined with this letter, authorizes discharges for the facility
referenced above. Coverage under the Treated Groundwater and Surface Water General Permit for
this facility is referred to as UPDES permit number UTG790107. The conditions and requirements
of the permit will be effective for one year beginning July 16, 2024. For reference, a copy of the
general permit is available at: https://deq.utah.gov/water-quality/current-permits-and-forms-updes-
permitting-program#general-treated-gw.
After reviewing your NOI and associated information, it was determined that effluent monitoring
and limits will be required as described in section I.E of the Treated Groundwater and Surface Water
General Permit. Effluent monitoring will also be required for Arsenic, Barium, Copper, and Zinc.
The Division of Water Quality (DWQ) approves the request to monitor for TPH-GRO and TPH-
DRO in lieu of the Total Toxic Organics (TTO) monitoring requirement. Prior to the first discharge
event, the facility must submit the required sampling analysis in section I.E., and the additional
required metals from a representative sample of treated effluent water. The initial monitoring shall
be sent via email to [e-mail]. After the facility has provided the initial monitoring results
and has received the DWQ approval, the facility is authorized to discharge.
Page 2
UTG790107
Former Sommers Auto
Monitoring and Limit requirements for Permit No. UTG790107 are as follows:
The permit requires that monitoring results be summarized and reported on a Discharge Monitoring
Report (DMR). The DMR shall be submitted electronically monthly the Environmental Protection
Agency’s (EPA) electronic reporting system: NetDMR https://npdes-ereporting.epa.gov/net-
netdmr. The DMR is due by the 28th day of each month for the previous month’s discharge
activity. When discharging activities cease, please notify the Division by submitting a Notice of
Termination form, which can also be obtained at: https://deq.utah.gov/water-quality/current-
permits-and-forms-updes-permitting-program#general
UPDES General Permit Coverage for the Discharge of Treated Groundwater is for 12 months or
less. Within 6 months of permit issuance, please evaluate your discharge timeline. If dewatering
discharges are expected to extend greater than 12 months from the issuance date, an individual
permit will need to be obtained. Individual permits require 6 months for issuance. Please keep DWQ
informed of your project status.
A fee schedule was included in the Utah Department of Environmental Quality Budget
appropriation request at the direction of the Legislature and in accordance with Utah Code annotated
19-1-201. The fee schedule, as approved by the legislature, includes a fee for the General Permit
for Treated Groundwater and Surface Water of $ 601.00 per year (see attached invoice). Please
submit payment within 30 days of permit issuance to:
Effluent Characteristics Effluent Limitations a Monitoring Requirement
Daily
Minimum
Daily
Maximum
Average
Weekly d
Average
Monthly
d
Measurement
requirement
Sample
Type
Flow, million gallons per day (mgd) 1 2/Month e Measured
pH, standard units (SU) 6.5 9.0 2/Month e Measured
Total Suspended Solids (TSS), mg/L 70 35 25 Monthly Grab
Total Dissolved Solids (TDS), mg/L 1,200 Monthly Grab
Total Recoverable Lead, mg/L 0.005 Monthly Grab
Oil & Grease, mg/L h 10 Monthly Grab
Benzene, mg/L 0.005 2/Month e Grab
BTEX, mg/L i 0.1 2/Month e Grab
MTBE, mg/L 0.2 2/Month e Grab
Naphthalene, mg/L 0.7 Monthly Grab
TPH- GRO, mg/L l 1.0 Monthly Grab
TPH-DRO, mg/L l 1.0 Monthly Grab
Arsenic, mg/L 0.10 Monthly Grab
Barium, mg/L 1.0 Monthly Grab
Copper, mg/L 0.003 Monthly Grab
Zinc, mg/L 0.04 Monthly Grab
Page 3
UTG790107
Former Sommers Auto

Department of Environmental Quality
Division of Water Quality
Attn: Susan Woeppel
PO Box 144870
Salt Lake City, Utah 84114-4870

Payment may also be made online via the Payment Portal at https://deq.utah.gov/general/payment-
portal Water Quality Shopping Cart by selecting Invoice Payment. Please be sure to include the
invoice number with either method of remittance.

Please keep DWQ informed of your project status, especially during discharging events for
coordination of potential future inspections. If you have any questions with regards to this matter,
please contact Linsey Shafer at [phone] or at [e-mail].

Sincerely.

Linsey Shafer
Permit Writer
Utah Division of Water Quality

Enclosures: 1. Signed NOI for UTG790107 (DWQ-2024-0055235)
2. Invoice # 257-4 (DWQ-2024-005347)

Cc: Via Email

Mark Bond, Owner, Former Sommers Auto Remediation Site
Corby Talbot, Division Manager, South Salt Lake
Dennis Pay, City Engineer, South Salt Lake
Ron Lund, Environmental Director, Salt Lake County Public Health
Baylie Nusink, Environmental Scientist, Division of Water Quality

DWQ-2024-005236

Appendix D
DWQ Treated Groundwater Discharge Permit and Documentation

Page 1 of 8
UPDES General Permit For
Treated Groundwater and Surface
Water
NOI
Notice of Intent (NOI)
for Coverage Under the
UPDES General Permit for Treated Groundwater and Surface Water
UPDES Permit No. UTG790000
Submission of this Notice of Intent constitutes notice that the party identified in Part II. of this form intends to be authorized
by UPDES General Permit No. UTG790000, issued for discharges of treated water to surface waters in the State of Utah.
Coverage of this permit obligates such dischargers to comply with the terms and conditions of the permit.
PLEASE PROVIDE ALL REQUIRED INFORMATION
You must print or type legibly; forms that are not legible, incomplete, or unsigned will be returned. You must maintain a
copy of the completed NOI form for your records.
PART I. (NOTE: THIS SECTION FOR DIVISION OF WATER QUALITY USE ONLY. Skip to Part II.)
THIS SECTION FOR DIVISION OF WATER QUALITY USE ONLY
Coverage Number:UTG79-
COVERAGE DATES://20 TO //20
RECEIVING WATER:CLASSIFICATION:
ADDITIONAL MONITORING AND/OR EFFLUENT LIMITATIONS:
DIVISION PERMIT OF COVERAGE ISSUANCE:
DATE://20 SIGNATURE:
Once coverage is assigned discharge monitoring reports will be generated and provided to the operator.
PART II. CONTACT INFORMATION (used for permit correspondence)
Organization Name:
Contact Name:Title:
Phone Number:Email:
Mailing Address:Street (PO Box):
City:State:Zip:
Owner/Manager Name:
Phone Number:Email:
Legal Status of Owner/Operator:
Wasatch Environmental, Inc.
Blake Downey V.P.
435-760-8269 [e-mail]
2410 W. California Ave.
Salt Lake City Utah 84104
Mark Bond
Legal Citizen of the U.S.A.
[e-mail]801-301-1146
0107
07 14 24 07 14 25
Golf of the Round Pond via Storm drain Category 3
Barium Copper Zinc
Arsenic
7 12 24
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 2 of 8
PART III. PROJECT SITE LOCATION
Project Lead Name:Project Lead Phone:
Project Site Name:
Project Street/Location:
City:County:State:UTAH Zip:
Project Site Phone:
Project latitude and longitude location in degree decimal.
Latitude Longitude
PART IV. PROJECT DESCRIPTION
Description of cleanup site, including a description of the source(s) of contamination and the extent of contamination
and any additional contamination anticipated in the local groundwater from other possible sources:
PART V. MAP
Attach a topographical map of the area extending to at least 1 mile beyond the property boundaries. The map must show the
outline of the facility, the location of each of its existing and proposed intake and discharge structures, each of its waste
treatment, storage, or disposal facilities, and discharge locations. Include all springs, rivers, and other surface water bodies in
the map.
Map Attached
PART VI. PROJECT DATES
Filing your permit will grant you one year of coverage from the filing date regardless of the project duration outlined below.
If you project ends early, you must file a Notice of Termination (NOT).
Project Start Date://20
Project Completion Date://20
Notes:
Blake Downey 435-760-8269
Former Sommers Auto
647 West 3300 South
South Salt Lake Salt Lake 84119
801-301-1146
40.698807 -111.910399
This site is a former automotive salvage wrecking yard that had above ground storage tanks that contained gasoline and
diesel. The tanks had a release of fuel, and lead and arsenic have been detected in the soils as well. Groundwater flows
to the northwest, but the impacts appear to be located on the southwest corner of the property. Wasatch plans to complete
on-site remediation which will include dewatering a soil excavation into frac tanks to be aerated then discharged through
a bag filter and granular activated carbon vessel prior to remove residual contaminants before discharge into the storm
water system.
X
07 15 24
09 30 24 **This is an estimated date range and may vary.
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 3 of 8
PART VII. DISCHARGE LOCATION(S)
List the Latitude and Longitude of the Discharge Point(s) in degree decimal with the Receiving Water.
Outfall No.Latitude Longitude Receiving Surface Waters (Name)
Are any of the discharge points located in the Colorado River Basin?Yes No
Does the receiving water designated uses include Class 1C drinking water as defined by R317-2-
13?Yes No
Class 1C waters are “Protected for domestic purposes with prior treatment by treatment processes as required by the
Utah Division of Drinking Water”.
Is the project located on tribal lands?Yes No
If the facility is located on Tribal Lands the permittee must contact EPA Region VIII except for facilities on the
Navajo Reservation or the Goshute Reservation, for which the permittee must contact EPA Region IX.
Does the discharge flow into a storm drain before entering the receiving water body?Yes No
Be Advised: Discharges to storm drains must be approved by the storm drain authority/owner.
Is the project part of the Utah Voluntary Cleanup Program (VCP)?Yes No
Description of Discharge location and conveyance system to live water:
PART VIII. INFLUENT AND EFFLUENT CONCENTRATIONS
Complete attached Table A and list any additional pollutants (not included in Table A) with influent and/or effluent
concentrations here:


X
X
1
2 (backup)40.699686 -111.910179
40.698257 -111.911111 The ponds at Golf the Round
The ponds at Golf the Round
X
Treated groundwater would be pumped to a storm drain located just west of the southwest corner of the project site.
According to South Salt Lake Public Works drawings of the storm sewer drians and lines, this discharge point flows to the
north and outfalls into the ponds located at the Golf the Round golf course.
TPH-DRO (Average (3 samples) 7.63 mg/L for influent)
TPH-GRO (Average (3 samples) 13.57 mg/L for influent)
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 4 of 8
PART VIII. INFLUENT AND EFFLUENT CONCENTRATIONS continued
Discharge IS to Class 1C Water:
1. In addition to completing Table A, influent sampling including total toxic organics (TTO results must be attached.
See attached Table B for list of TTO constituents. No permits for discharge to Class 1C Waters will be issued prior
to influent sampling being conducted and results received.
2. An analysis of alternative disposal methods of the treated groundwater must be attached. This analysis must include
an economic comparison of the alternative disposal methods. If no other disposal methods are feasible the analysis
must demonstrated the consideration of other methods such as trucking and/or discharge to a treatment facility.
3.
Discharge is NOT to Class 1C Water:
1. In addition to completing Table A, influent sampling including total toxic organics OR a report documenting why
influent sampling is not needed for this project and an estimation of anticipated influent constituents concentrations.
2. In accordance with Part I.D. the permittee may petition Total Petroleum Hydrocarbon (TPH-GRO and TPH-DRO)
analyses may be substituted for the TTO analyses. If approved maximum daily effluent limitations of 1.0 mg/LTPH-
GRO and TPH-DRO will be substituted for the TTO effluent limitation.
PART IX. DESCRIPTION OF TREATMENT SYSTEM
Description of the current or proposed treatment system, including discharge flow rate (attach a flow diagram):
FLOW DIAGRAM ATTACHED
PART X. CERTIFICATION AND SIGNATURE
I certify under penalty of law that this submission was prepared under my direction or supervision in accordance with
a system designed to assure that qualified personnel properly gather and evaluate the information submitted. Based on
my inquiry of the person or persons who manage the system, or those person(s) directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate, and complete. I am
aware that there are significant penalties for submitted false information, including the possibility of fine and
imprisonment for knowing violations. I further certify that the applicant has sufficient title, right or interest in the
property where the proposed activity occurs.
PRINT Signatory
Authority Signature Title Date
X
Groundwater would be pumped from the excavation into two 21,000 gallon frac tanks. The groundwater would be aerated
within the frac tanks and then pumped through a bag filter unit to remove sediments, and then through a granular activated
carbon vessel to remove any remaining contaminants. Then the treated groundwater would be discharged through the
South Salt Lake storm sewer system.
Blake B. Downey Vice President 6-24-24
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 5 of 8
PART XI. ADDITIONAL APPLICATIONS AND APPROVALS
1. You may need to file for a temporary application to appropriate water rights form the Division of Water
Rights. Call 801.583.7240 for more information.
2. You may need to obtain approval from the Division of Air Quality if any air stripping equipment is to be
employed at the cleanup site. Call 801.536.4000 for more information.
The Division of Water Quality may request addition information.
Important:
The UPDES Permit Application, must be signed as follows: (Refer to Part IV.G. Signatory Requirements, of the General
Permit.)
1) For a corporation, a responsible corporate officer shall sign the NOT, a responsible corporate officer means:
a. A President, secretary, treasurer, or vice-president of the corporation in charge of a principal business function, or
any other person who performs similar policy- or decision-making functions for the corporation; or
b. The manager of one or more manufacturing, production, or operating facilities, if
i. The manager is authorized to make management decisions that govern the operation of the regulated facility,
including having the explicit or implicit duty of making major capital investment recommendations, and
initiating and directing other comprehensive measures to assure long term environmental compliance with
environmental statutes and regulations:
ii. The manager can ensure that the necessary systems are established or actions taken to gather complete and
accurate information for permit application requirements; and
iii. Authority to sign documents has been assigned or delegated to the manager in accordance with corporate
procedures.
2) For a partnership of sole proprietorship, the general partner or the proprietor, respectively; or
3) For a municipality, state or other public agency, either a principal executive officer or ranking elected official shall sign
the application; in this subsection, a principal executive officer of any agency means;
a. The chief executive officer of the agency; or
b. A senior executive officer having responsibility for the overall operations of a principal geographic unit or division
of the agency.
Where to File the UPDES Permit Application form:
Please submit the original form with signature via the DWQ Electronic Documents Submission Portal:
https://deq.utah.gov/water-quality/water-quality-electronic-submissions
You can also send by mail or hand deliver to the below address. Remember to retain a copy for your records.
Division of Water Quality
Department of Environmental Quality
195 North 1950 West
PO Box 144870
Salt Lake City, UT 84114-4870
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 6 of 8
TABLE A
Analysis of Treatment System Influent and Effluent
You must report concentrations for each pollutant listed. Please refer to Part I.D. and Part I.E. of the permit or
NOI to determine if actual influent values are required or if estimated values will be accepted.
Are influent values:Estimated Or Actual
Are effluent values:Estimated Or Actual
Influent Effluent
Parameters Avg
(mg/L)
Max
(mg/L)
Number of
Samples
Avg
(mg/L)
Max
(mg/L)
Number of
Samples
pH (range in standard units)
Total Suspended Solids
Total Dissolved Solids
Total Lead
Oil & Grease
Benzene
Toluene
Ethylbenzene
Xylenes
Naphthalene
MTBE
TTO’s
(attach full list if required)
Given this is a fuel release from an AST we request to sample for TPH-GRO and
TPH-DRO instead of TTO, with an effluent limit of <1.0 mg/L.
X
XX
6.9 7.2 Estimated 7.0 7.5 Est.
<0.00200 <0.00200 3 <0.00200 <0.00200 Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.
Est.<70 <70
<1,200 <1,200
Est.
Est.800 900
65 70
<10 <10
<0.005 <0.005
<0.2 <0.2
<0.7 <0.7
<0.1 <0.1
<0.1 <0.1
<0.1 <0.1
14.24.79 3
2.910.975 3
10.73.59 3
0.609 30.251
0.0247 30.0144
0.888 30.297
28.685.54
See attached data report, only samples GP-14, GP-15, and GP-16 apply.
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 7 of 8
TABLE B
Metals Detection to Determine Required Monitoring
Effluent Characteristics Results (mg/L)Effluent Limitations (mg/L)
Arsenic 0.01 / 0.10
Barium 1.0
Beryllium 0.0004
Cadmium 0.026
Chromium 0.05 / 0.10
Copper 0.003
Mercury 0.002
Selenium 0.05
Silver 0.05
Zinc 0.04
0.307
0.332
Not sampled for
Not sampled for
Not sampled for
<0.00200
<0.00200
<0.0000900
<0.0400
<0.000700
Max Detection
NOI
UPDES General Permit For
Treated Groundwater and Surface Water
Page 8 of 8
TABLE C
Total Toxic Organic List
(These are the parameters that shall be analyzed for initially determining the total toxic organic (TTO) concentration of the wastewater)
Volatile Organic Compounds
Acrolein
Acrylonitrile
Benzene
Bromoform
Carbon Tetrachloride
Chlorobenzene
Chlorodibromomethane
Chloroethane
2-Chloroethylvinyl Ether
Chloroform
Dichlorobromomethane
1,1-Dichloroethane
1,2-Dichloroethane
1,1-Dichloroethylene
1,2-Dichloropropane
1,3-Dichloropropylene
Ethylbenzene
Methyl Bromide
Methyl Chloride
Methylene Chloride
1,1,2,2-Tetrachloroethane
Tetrachloroethylene
Toluene
1,2-Cis,Trans- Dichloroethylene
1,1,1-Trichloroethane
1,1,2-Trichloroethane
Trichloroethylene
Vinyl Chloride
Semi-Volatile Organic
Compounds
2-Chlorophenol
2,4-Dichlorophenol
2,4-Dimethylphenol
4,6-Dinitro-O-Cresol
2,4-Dinitrophenol
2-Nitrophenol
4-Nitrophenol
P-Chloro-M-Cresol
Pentachlorophenol
Phenol
2,4,6-Trichlorophenol
Acenaphthene
Acenaphthylene
Anthracene
Benzidine
Benzo(A)Anthracene
Benzo(A)Pyrene
3,4-Benzofluoranthene
Benzo(Ghi)Perylene
Benzo(K)Fluoranthene
Bis(2-Chloroethoxy)Methane
Bis(2-Chloroethyl)Ether
Bis(2-Chloroisopropyl)Ether
Bis (2-Ethylhexyl)Phthalate
4-Bromophenyl Phenyl Ether
Butylbenzyl Phthalate
2-Chloronaphthalene
Ether
4-Chlorophenyl Phenyl
Chrysene
Dibenzo(A,H)Anthracene
1,2-Dichlorobenzene
1,3-Dichlorobenzene
1,4-Dichlorobenzene
3,3′-Dichlorobenzidine
Diethyl Phthalate
Dimethyl Phthalate
Di-N-Butyl Phthalate
2,4-Dinitrotoluene
2,6-Dinitrotoluene
Di-N-Octyl Phthalate
1,2-Diphenylhydrazine (As Azobenzene)
Fluroranthene
Fluorene
Hexachlorobenzene
Hexachlorobutadiene
Hexachlorocyclopentadiene
Hexachloroethane
Indeno(1,2,3-Cd)Pyrene
Isophorone
Napthalene
Nitrobenzene
N-Nitrosodimethylamine
N-Nitrosodi-N-Propylamine
N-Nitrosodiphenylamine
Phenanthrene
Pyrene
1,2,4-Trichlorobenzene
Pesticides and PCBs
Aldrin
Alpha-Bhc
Beta-Bhc
Gamma-Bhc
Delta-Bhc
Chlordane
4,4′-Ddt
4,4′-Dde
4,4′-Ddd
Dieldrin
Alpha-Endosulfan
Beta-Endosulfan
Endosulfan Sulfate
Endrin
Endrin Aldehyde
Heptachlor
Heptachlor Epoxide
Pcb-1242
Pcb-1254
Pcb-1221
Pcb-1232
Pcb-1248
Pcb-1260
Pcb-1016
Toxaphene
FIGURE
1
DRAWING DATEPROJECT NO.
Environmental Science and Engineering
Arrieta Property
Grange Property
Topographic Map of Facility
2469-002H June 24, 2024
Former Sommers Auto
647 West 3300 South
South Salt Lake, Utah
Scale: 1-inch equals
approximately 770 feet
Approximate Facility Boundary
Excavation and Dewatering Area
Groundwater Treatment Area
Discharge Area
FIGURE
2
DRAWING DATEPROJECT NO.
Environmental Science and Engineering
Proposed Soil Excavation Area
Remediation Process Map
2469-002H June 24, 2024
Scale: 1-inch equals
approximately 80 feet
Dump Truck Haul Pathway
Proposed Frack-Tank Location
and Area of Groundwater Treatment
Approximate Site Boundary
3200 South
3300 South
Filter Unit and
GAC Vessel
Groundwater Treatment Flow Path
Storm Drain (Discharge Location)
Proposed Track-Out Pad
Former Sommers Auto
647 West 3300 South
South Salt Lake, Utah
Backup Storm Drain
(Discharge Location)

195 North 1950 West • Salt Lake City, UT
Mailing Address: P.O. Box 144870 • Salt Lake City, UT 84114-4870
Telephone [phone] • Fax [phone] TDD [phone]
www.deq.utah.gov
Printed on 100% recycled paper
State of Utah

Department of
Environmental Quality

Kimberly D. Shelley
Executive Director

DIVISION OF WATER QUALITY
John Mackey, P.E.
Interim Director

SPENCER J. COX
Governor

DEIDRE HENDERSON
Lieutenant Governor
July 16, 2024

VIA EMAIL
READ RECEIPT REQUESTED

Blake Downey
Vice President
Wasatch Environmental, Inc.
2410 West California Avenue
Salt Lake City, Utah, 84104

Subject: UPDES General Permit Coverage No. UTG790107
Former Sommers Auto, Salt Lake City, Utah

Dear Mr. Downey:

Enclosed is a signed copy of the Utah Pollutant Discharge Elimination System (UPDES) General
Permit Notice of Intent (NOI), which combined with this letter, authorizes discharges for the facility
referenced above. Coverage under the Treated Groundwater and Surface Water General Permit for
this facility is referred to as UPDES permit number UTG790107. The conditions and requirements
of the permit will be effective for one year beginning July 16, 2024. For reference, a copy of the
general permit is available at: https://deq.utah.gov/water-quality/current-permits-and-forms-updes-
permitting-program#general-treated-gw.
After reviewing your NOI and associated information, it was determined that effluent monitoring
and limits will be required as described in section I.E of the Treated Groundwater and Surface Water
General Permit. Effluent monitoring will also be required for Arsenic, Barium, Copper, and Zinc.
The Division of Water Quality (DWQ) approves the request to monitor for TPH-GRO and TPH-
DRO in lieu of the Total Toxic Organics (TTO) monitoring requirement. Prior to the first discharge
event, the facility must submit the required sampling analysis in section I.E., and the additional
required metals from a representative sample of treated effluent water. The initial monitoring shall
be sent via email to [e-mail]. After the facility has provided the initial monitoring results
and has received the DWQ approval, the facility is authorized to discharge.
Page 2
UTG790107
Former Sommers Auto
Monitoring and Limit requirements for Permit No. UTG790107 are as follows:
The permit requires that monitoring results be summarized and reported on a Discharge Monitoring
Report (DMR). The DMR shall be submitted electronically monthly the Environmental Protection
Agency’s (EPA) electronic reporting system: NetDMR https://npdes-ereporting.epa.gov/net-
netdmr. The DMR is due by the 28th day of each month for the previous month’s discharge
activity. When discharging activities cease, please notify the Division by submitting a Notice of
Termination form, which can also be obtained at: https://deq.utah.gov/water-quality/current-
permits-and-forms-updes-permitting-program#general
UPDES General Permit Coverage for the Discharge of Treated Groundwater is for 12 months or
less. Within 6 months of permit issuance, please evaluate your discharge timeline. If dewatering
discharges are expected to extend greater than 12 months from the issuance date, an individual
permit will need to be obtained. Individual permits require 6 months for issuance. Please keep DWQ
informed of your project status.
A fee schedule was included in the Utah Department of Environmental Quality Budget
appropriation request at the direction of the Legislature and in accordance with Utah Code annotated
19-1-201. The fee schedule, as approved by the legislature, includes a fee for the General Permit
for Treated Groundwater and Surface Water of $ 601.00 per year (see attached invoice). Please
submit payment within 30 days of permit issuance to:
Effluent Characteristics Effluent Limitations a Monitoring Requirement
Daily
Minimum
Daily
Maximum
Average
Weekly d
Average
Monthly
d
Measurement
requirement
Sample
Type
Flow, million gallons per day (mgd) 1 2/Month e Measured
pH, standard units (SU) 6.5 9.0 2/Month e Measured
Total Suspended Solids (TSS), mg/L 70 35 25 Monthly Grab
Total Dissolved Solids (TDS), mg/L 1,200 Monthly Grab
Total Recoverable Lead, mg/L 0.005 Monthly Grab
Oil & Grease, mg/L h 10 Monthly Grab
Benzene, mg/L 0.005 2/Month e Grab
BTEX, mg/L i 0.1 2/Month e Grab
MTBE, mg/L 0.2 2/Month e Grab
Naphthalene, mg/L 0.7 Monthly Grab
TPH- GRO, mg/L l 1.0 Monthly Grab
TPH-DRO, mg/L l 1.0 Monthly Grab
Arsenic, mg/L 0.10 Monthly Grab
Barium, mg/L 1.0 Monthly Grab
Copper, mg/L 0.003 Monthly Grab
Zinc, mg/L 0.04 Monthly Grab
Page 3
UTG790107
Former Sommers Auto

Department of Environmental Quality
Division of Water Quality
Attn: Susan Woeppel
PO Box 144870
Salt Lake City, Utah 84114-4870

Payment may also be made online via the Payment Portal at https://deq.utah.gov/general/payment-
portal Water Quality Shopping Cart by selecting Invoice Payment. Please be sure to include the
invoice number with either method of remittance.

Please keep DWQ informed of your project status, especially during discharging events for
coordination of potential future inspections. If you have any questions with regards to this matter,
please contact Linsey Shafer at [phone] or at [e-mail].

Sincerely.

Linsey Shafer
Permit Writer
Utah Division of Water Quality

Enclosures: 1. Signed NOI for UTG790107 (DWQ-2024-0055235)
2. Invoice # 257-4 (DWQ-2024-005347)

Cc: Via Email

Mark Bond, Owner, Former Sommers Auto Remediation Site
Corby Talbot, Division Manager, South Salt Lake
Dennis Pay, City Engineer, South Salt Lake
Ron Lund, Environmental Director, Salt Lake County Public Health
Baylie Nusink, Environmental Scientist, Division of Water Quality

DWQ-2024-005236

Notice of Termination (NOT) for Coverage Under the UPDES General Permit for Treated
Groundwater, UPDES Permit No.UTG790000.

NOT
Submission of this NOT constitutes notice that the operator/facility identified in section I of this form is no longer
covered under the UPDES General Permit for Treated Groundwater, UPDES Permit No.UTG790000.
I. Facility/Operator Information
UPDES Permit No.UTG790000 Coverage No. UTG79 .
Name and location of facility (Include County name) __________________________________________
_____________________________________________________________________________________________
Facility mailing address (if different from physical address) ___________________________________________
_____________________________________________________________________________________________
Telephone Number __________________________ Name of Operator ________________________________
II. Reason for the Termination of Permit Coverage
Reason for permit termination (attach additional sheets if necessary)_____________________________________
____________________________________________________________________________________________
III. Certification
I certify under penalty of law that all construction dewatering and/or hydrostatic testing operations at the above
facility that were authorized by the UPDES General Permit for Treated Groundwater, UPDES Permit
No.UTG790000 have been eliminated or that I am no longer the operator of the facility. I understand that by
submitting the Notice of Termination, I am no longer covered under the general permit. I also understand that the
submittal of this notice of termination does not release an operator from liability for any violations of this permit or
the Water Quality Act.
Name (print) _____________________________________ Title ________________________________________
Signature ________________________________________ Date(mm/dd/yy) ______/_______/_________
Where to File the NOT Form:
Division of Water Quality
195 North 1950 West
P.O. Box 144870
Salt Lake City, UT 84114-4870
0107
Former Sommers Auto
647 West 3300 South, South Salt Lake, Utah
Same
801-301-1146 Mark Bond/Devan Knight
This was a one time batch discharge that
is completed and no additional water will be generated.
Blake B. Downey Vice President
09 27 2024

Appendix E
SLCHD Notice Documentation

Appendix F
Public Notice

Public Notice
30-Day Comment Period
Former Sommers Auto Wrecking Project

Mountain Crest Wasatch, LLC, has prepared a Remedial Action Plan (RAP) to address
heavy metal and petroleum hydrocarbon impacts to soil and groundwater at the former
Sommers Auto Wrecking property located at approximately 647 West 3300 South in
South Salt Lake, Utah. The current property owner has entered into an agreement with
the Utah Department of Environmental Quality (UDEQ), Division of Environmental
Response and Remediation’s (DERR’s) Voluntary Cleanup Program (VCP) to remediate
the impacted soil and groundwater to agreed upon cleanup levels to allow industrial use
of the property. During excavation work associated with the impacted soils and
groundwater, access to the site will be controlled and fugitive dust mitigated to ensure
the safety of workers and the community. It is anticipated that work will start in April
2024. Site remedial activities that disturb impacted soils and groundwater are
anticipated to take approximately four weeks to complete. The RAP will describe
procedures to manage impacted soil and groundwater that will be disturbed during the
remedial activities. All VCP documents including the RAP may be viewed online at
http://eqedocs.utah.gov, and at the Utah DEQ/DERR offices at the address below. The
Public Comment period will commence on December 20, 2023, and comments will be
received through January 20, 2023. Please send written comments, either by mail or
email to:

Mr. Lincoln Grevengoed, Project Manager
Voluntary Cleanup/Brownfields Section
Division of Environmental Response and Remediation
Utah Department of Environmental Quality
P. O. Box 144840
195 North 1950 West, 1st Floor
Salt Lake City, Utah 84114-4840
[e-mail]
[phone]
The use or reuse of this information is restricted to the referenced document unless otherwise authorized.
Wasatch Environmental Copyright 2006
FORMER SOMMERS AUTO WRECKING WEI 2469-002H
Figure 1 Public Notice Map
Approximate
Location of Site
Parcel where public notice was delivered to each occupant at the parcel.
1
Blake Downey
From:[e-mail]
Sent:Friday, December 15, 2023 10:53 AM
To:Blake Downey
Subject:[EXTERNAL] Thank you for placing your order with us.
Attachments:SLT00255250.pdf; SLT00255250.txt
THANK YOU for your ad submission!
This is your confirmation that your order has been submitted. Below are the details of your transaction. Please save this confirmation for your records.
Notes
Proof and Receipt for the Cost of $134.60 for Ad number SLT0025525 Thank you
Job Details
Order Number:
SLT0025525
Classification:
Public Meeting/Hearing Notices
Package:
Legals
Order Cost:
$134.60
Payment Type:
Visa
Account Details
BLAKE DOWNEY
2410 W CALIFORNIA AVE
SALT LAKE CITY, UT 84104
801-972-8400
[e-mail]
WASATCH ENVIRONMENTAL, INC.
Credit Card - Visa ************2545
Schedule for ad number SLT00255250
Wed Dec 20, 2023
The Salt Lake Tribune E-Edition
All Zones
The Salt Lake Tribune Legals
All Zones
2

Appendix G
Photographic Log

Photo 1 – Excavating test pits for soil
sampling
Photo 2 – Test pitting cont.
Photo 3 – Test pitting cont.Photo 4 – Test pitting cont.
Photo 5 – Removal of concrete from the area
of excavation EXC-4 Photo 6 – Excavator loading haul trucks with
concrete for disposal
Photo 7 – Area of EXC-4 after concrete
removal and prior to soil excavation, looking
west
Photo 8 – Excavating petroleum-impacted soil
from EXC-4
Photo 9 – Loading haul truck with petroleum-
impacted soil for disposal
Photo 10 – Beginning excavation EXC-4,
looking southwest
Photo 11 – Excavation of EXC-4, looking west Photo 12 – Petroleum impacted groundwater
within EXC-4, free-product observed on the
groundwater surface
Photo 13 – Absorbent pads placed within EXC-
4, used to clean up free-product on
groundwater surface
Photo 14 – Dewatering EXC-4 using a sump
pump and 2” diameter water hose
Photo 15 – Impacted groundwater from EXC-4
being pumped into frac tank
Photo 16 – PVC constructed aeration system
within the frac tank
Photo 17 – Operating the aeration system
within the frac tank Photo 18 – Frac tanks used during the
dewatering/treatment process
Photo 19 – Excavating the north wall of EXC-4 Photo 20 – Completed excavation of EXC-4,
looking south
Photo 21 – Frac tank water running through
the GAC filtration system prior to discharge
Photo 22 – Petroleum saturated absorbent
pads removed from EXC-4 for disposal
Photo 23 – Excavating lead-impacted soil from
EXC -2
Photo 24 – Loading haul truck with lead-
impacted soil for disposal
Photo 25 – Excavating lead-impacted soil from
EXC -3 Photo 26 – Completed excavation of EXC-3,
looking southeast
Photo 27 – Removal of concrete from the area
of excavation EXC-1
Photo 28 – Area of EXC-1 after concrete
removal and prior to soil excavation, looking
north
Photo 29 – EXC-1 after backfilling and
compaction, looking south
Photo 30 – EXC-2 after backfilling and
compaction, looking north
Photo 31 – EXC-3 after backfilling and
compaction, looking north
Photo 32 – EXC-4 after backfilling and
compaction, looking south
Photo 33 – Geoprobe drill rig setting up for
installation of monitoring well MW-6
Photo 34 – Monitoring well MW-6 surface
completion
Photo 35 – Drilling/installing monitoring well
MW-7
Photo 36 – Monitoring well MW-7 surface
completion

Appendix H
Monitoring Well Construction Logs

BORING NO.: MW-6
Sommers Auto Wrecking
670 West 3300 South
South Salt Lake, Utah
12” Flush Mount
Well Vault set in
Concrete
2” PVC
0.5’ to 5’
Hydrated
Medium
Bentonite
1’ to 2.5’
10/20
Silica Sand
2.5’-15’
3” PVC
Foot
Well Screen
5’ to 15’
End of Boring
REFERENCE ELEVATION: Ground Surface
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
DRILL RIG: Geoprobe7822 DT
TOTAL DEPTH: 15’
DESCRIPTION AND CLASSIFICATION
Description and Remarks Color
Soil
Type Consist.De
p
t
h

(
f
e
e
t
)
Sa
m
p
l
e
r
Bl
o
w
s
/
F
o
o
t
PI
D

(
p
p
m
)
Wat
e
r

L
e
v
e
l
Well
Construction
WELL LOG
Environmental Science and Engineering
0.1
0.1
0.1
0.1
0.1
0.1
DEPTH TO GROUNDWATER: 6’
DATE DRILLED: October 14, 2024
LOGGED BY: Jake Scott, P.G.
PROJECT NO.: 2469-002H

Brown SW
Clay: With trace fine to coarse-grained sand, traced fine
to coarse-grained sub-angular gravel,medium plasticity,
saturated at 12’
Medium
Dense
Tan
Grades to:
Clay: trace fine to coarse-grained sand, medium plasticity
StiffCL
Gravelly Sand (Engineered Fill): fine to coarse-grained,
fine to medium-grained sub-angular gravel, some silt,
moist
DEPTH TO GROUNDWATER: 6’
BORING NO.: MW-7
Sommers Auto Wrecking
670 West 3300 South
South Salt Lake, Utah
12” Flush Mount
Well Vault set in
Concrete
2” PVC
0.5’ to 5’
Hydrated
Medium
Bentonite
1’ to 2.5’
10/20
Silica Sand
2.5’-15’
3” PVC
Foot
Well Screen
5’ to 15’
End of Boring

Brown CL
REFERENCE ELEVATION: Ground Surface
Clay: With trace fine to coarse-grained sand, traced fine
to coarse-grained sub-angular gravel,medium plasticity,
saturated at 12’
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
DATE DRILLED: October 14, 2024
LOGGED BY: Jake Scott, P.G.
DRILL RIG: Geoprobe7822 DT
TOTAL DEPTH: 15’
DESCRIPTION AND CLASSIFICATION
Description and Remarks Color
Soil
Type Consist.De
p
t
h

(
f
e
e
t
)
Sa
m
p
l
e
r
Bl
o
w
s
/
F
o
o
t
PI
D

(
p
p
m
)
Wat
e
r

L
e
v
e
l
Well
Construction
WELL LOG
PROJECT NO.: 2469-002HEnvironmental Science and Engineering
Medium
Stiff
Tan
Grades to:
Clay: trace fine to coarse-grained sand, medium plasticity
StiffCL
0.1
0.1
0.1
0.1
0.1
Clay (fill): With some fine to coarse-grained sand,
some fine to coarse-grained sub-angular gravel, moist
0’-5’ Small Recovery

Appendix I
Waste Disposal Documentation

The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24F1419
Project: Former Sommers Auto Wrecking
6/28/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 47
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24F1419-01 TP - 1 (2'-3')
24F1419-02 TP - 2 ( 5'-6')
24F1419-03 TP - 3 ( 2'-3')
24F1419-04 TP - 4 ( 2'-3')
24F1419-05 TP - 5 ( 4'-5')
24F1419-06 TP - 6 ( 4'-5')
24F1419-07 TP - 60 ( 4'-5')
24F1419-08 DU-1
24F1419-09 DU-2
24F1419-10 DU-10
24F1419-11 Test Pit WCS
24F1419-12 EXC 1-3 WCS
24F1419-13 Trip Blank
24F1419-14 Equipment Blank
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
Page 2 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 1 (2'-3')
Lab ID: 24F1419-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 9:10
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800081.7Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.29 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.29 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.29 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.29 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDEthylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDNaphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.24 EPA 8270E/35700.53C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/357011.2C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/35702.46C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/357014.3C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.24 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 3 of 46Page 3 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 2 ( 5'-6')
Lab ID: 24F1419-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 10:25
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800079.9Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B3.63C5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B13.2C7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B5.85C9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B13.0C9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030B0.75Benzene
mg/kg dry MS-Low6/18/246/18/240.03 EPA 8260D/5030B0.18Ethylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030B1.88Naphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030B0.36Xylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.75 EPA 8270E/35702.91C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.75 EPA 8270E/35701330C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.75 EPA 8270E/357081.9C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.75 EPA 8270E/357044.7C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.75 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.75 EPA 8270E/35705.14Total C12-C22 PAH
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/35703.44Phenanthrene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 4 of 46Page 4 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 3 ( 2'-3')
Lab ID: 24F1419-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 11:10
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800091.4Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/242.10 EPA 8260D/5030B5.08C5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/242.10 EPA 8260D/5030B6.93C7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/242.10 EPA 8260D/5030B3.64C9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/242.10 EPA 8260D/5030B29.3C9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.08 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.21 EPA 8260D/5030B2.48Ethylbenzene
mg/kg dry 6/18/246/18/240.21 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.21 EPA 8260D/5030B0.81Naphthalene
mg/kg dry 6/18/246/18/240.21 EPA 8260D/5030B5.28Toluene
mg/kg dry 6/18/246/18/240.63 EPA 8260D/5030B17.0Xylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/357026.8C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/3570859C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/3570320C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/35701400C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 5 of 46Page 5 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 4 ( 2'-3')
Lab ID: 24F1419-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 11:35
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800074.0Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.32 EPA 8260D/5030B1.04C5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.32 EPA 8260D/5030B3.49C7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.32 EPA 8260D/5030B1.51C9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.32 EPA 8260D/5030B13.6C9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030B0.10Benzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030B0.73Ethylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030B0.44Naphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030B0.14Toluene
mg/kg dry 6/18/246/18/240.10 EPA 8260D/5030B3.50Xylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/245.40 EPA 8270E/357011.2C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570530C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570112C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570588C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 6 of 46Page 6 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 5 ( 4'-5')
Lab ID: 24F1419-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 11:50
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800078.1Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDEthylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDNaphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.26 EPA 8270E/35700.65C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/357020.6C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/35707.11C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/357028.6C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.26 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 7 of 46Page 7 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 6 ( 4'-5')
Lab ID: 24F1419-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:05
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800075.6Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDEthylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDNaphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.26 EPA 8270E/35700.67C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/357013.7C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/35701.66C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/357012.1C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.26 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 8 of 46Page 8 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 60 ( 4'-5')
Lab ID: 24F1419-07Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:10
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800082.4Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDEthylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDNaphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.24 EPA 8270E/35700.57C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/357013.7C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/35707.07C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/357031.8C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.24 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 9 of 46Page 9 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: DU-1
Lab ID: 24F1419-08Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 13:20
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800099.8Total Solids
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/244.00 EPA 8270E/35705.11C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570149C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/357044.5C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570262C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 10 of 46Page 10 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: DU-2
Lab ID: 24F1419-09Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 13:00
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800098.6Total Solids
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/244.00 EPA 8270E/35705.96C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570223C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570644C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/35702270C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 11 of 46Page 11 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: DU-10
Lab ID: 24F1419-10Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 13:25
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF8000100Total Solids
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/244.00 EPA 8270E/35705.79C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570167C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570121C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570695C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 12 of 46Page 12 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Test Pit WCS
Lab ID: 24F1419-11Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:45
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
°F 6/25/246/25/2480.0 EPA 1010MOD>200Flashpoint
mg/kg dry 6/19/246/19/24308EPA 1664BModNDOil & Grease (HEM)
%6/19/246/19/240.1 EPA 1311/1311NDPercent Pass
pH Units 6/19/24 10:356/19/24 8:590.1 EPA 9040C/9045D10.5pH
%6/19/246/18/240.1 CTF800080.9Total Solids
Metals
mg/kg dry 6/20/246/19/241.05 EPA 6010D/3050B15.2Arsenic, Total
mg/kg dry 6/20/246/19/240.210 EPA 6010D/3050B129Barium, Total
mg/kg dry 6/20/246/19/240.105 EPA 6010D/3050B0.536Cadmium, Total
mg/kg dry 6/20/246/19/240.105 EPA 6010D/3050B9.37Chromium, Total
mg/kg dry 6/20/246/19/242.10 EPA 6010D/3050B171Lead, Total
mg/kg dry 6/19/246/19/240.017 EPA 7471A0.075Mercury, Total
mg/kg dry 6/20/246/19/241.26 EPA 6010D/3050BNDSelenium, Total
mg/kg dry 6/20/246/19/240.105 EPA 6010D/3050BNDSilver, Total
TCLP Metals
mg/L 6/28/246/28/240.20 EPA 6010D/3010A0.42Lead, TCLP
Volatile Organic Compounds
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,1,1-Trichloroethane
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,1,2-Trichloroethane
mg/kg dry J-LOW-L6/18/246/18/240.28 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,1-Dichloroethene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,2-Dichlorobenzene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,2-Dichloroethane
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,4-Dichlorobenzene
mg/kg dry J-LOW-C6/18/246/18/240.56 EPA 8260D/5030BND2-Nitropropane
mg/kg dry 6/18/246/18/245.62 EPA 8260D/5030BNDAcetone
mg/kg dry 6/18/246/18/240.11 EPA 8260D/5030B0.12Benzene
mg/kg dry J-LOW-L6/18/246/18/240.56 EPA 8260D/5030BNDCarbon Disulfide
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDCarbon Tetrachloride
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDChlorobenzene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDChloroform
mg/kg dry MS-Low6/18/246/18/242.81 EPA 8260D/5030BNDCyclohexanone
mg/kg dry 6/18/246/18/240.56 EPA 8260D/5030BNDEthyl Acetate
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDEthyl Ether
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B0.43Ethylbenzene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDHexachlorobutadiene
mg/kg dry 6/18/246/18/245.62 EPA 8260D/5030BNDIsobutanol
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 13 of 46Page 13 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Test Pit WCS (cont.)
Lab ID: 24F1419-11Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:45
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
mg/kg dry 6/18/246/18/240.56 EPA 8260D/5030BNDMethyl Ethyl Ketone
mg/kg dry 6/18/246/18/241.40 EPA 8260D/5030BNDMethyl Isobutyl Ketone
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDMethylene Chloride
mg/kg dry 6/18/246/18/2414.0 EPA 8260D/5030BNDn-Butyl Alcohol
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDTetrachloroethene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDTrichloroethene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDTrichlorofluoromethane
mg/kg dry 6/18/246/18/240.22 EPA 8260D/5030BNDVinyl Chloride
mg/kg dry 6/18/246/18/240.84 EPA 8260D/5030B2.32Xylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 14 of 46Page 14 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: EXC 1-3 WCS
Lab ID: 24F1419-12Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:30
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800096.0Total Solids
Metals
mg/kg dry 6/20/246/19/244.57 EPA 6010D/3050B10.3Arsenic, Total
mg/kg dry 6/20/246/19/244.57 EPA 6010D/3050B274Lead, Total
TCLP Metals
mg/L 6/20/246/20/240.50 EPA 6010D/3010ANDArsenic, TCLP
mg/L 6/20/246/20/240.20 EPA 6010D/3010A1.27Lead, TCLP
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 15 of 46Page 15 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24F1419-13Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 8:00
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 6/19/246/19/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L 6/19/246/19/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 6/19/246/19/2420.0 EPA 8260D/5030BNDAcetone
ug/L 6/19/246/19/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 6/19/246/19/240.4 EPA 8260D/5030BNDBenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030B10.7Bromodichloromethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDBromoform
ug/L 6/19/246/19/242.0 EPA 8260D/5030BNDBromomethane
ug/L 6/19/246/19/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 16 of 46Page 16 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24F1419-13Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 8:00
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDChloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030B40.2Chloroform
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDChloromethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L 6/19/246/19/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 6/19/246/19/241.0 EPA 8260D/5030B2.2Dibromochloromethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDDibromomethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 6/19/246/19/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 6/19/246/19/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 6/19/246/19/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 6/19/246/19/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L J-LOW-L6/19/246/19/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDNaphthalene
ug/L 6/19/246/19/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDStyrene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDToluene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 6/19/246/19/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 6/19/246/19/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 17 of 46Page 17 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Equipment Blank
Lab ID: 24F1419-14Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:20
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
BETX Compounds
mg/L 6/19/246/19/240.125 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/L 6/19/246/19/240.125 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/L 6/19/246/19/240.125 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/L 6/19/246/19/240.125 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/L 6/19/246/19/240.005 EPA 8260D/5030BNDBenzene
mg/L 6/19/246/19/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L 6/19/246/19/240.012 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 6/19/246/19/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 6/19/246/19/240.012 EPA 8260D/5030BNDToluene
mg/L 6/19/246/19/240.038 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
ug/L 6/20/246/20/2410EPA 8270E/351154C11-12 Aliphatic hydrocarbons
ug/L 6/20/246/20/2410EPA 8270E/3511655C13-C16 Aliphatic hydrocarbons
ug/L 6/20/246/20/2410EPA 8270E/351160C17-C21 Aliphatic hydrocarbons
ug/L 6/20/246/20/2410EPA 8270E/3511596C22-C35 Aliphatic hydrocarbons
ug/L 6/20/246/20/2410EPA 8270E/3511NDC11-C13 Alkyl Naphthalenes
ug/L 6/20/246/20/2410EPA 8270E/3511NDTotal C12-C22 PAH
ug/L 6/20/246/20/2410EPA 8270E/3511NDAcenaphthene
ug/L 6/20/246/20/2410EPA 8270E/3511NDAcenaphthylene
ug/L 6/20/246/20/2410EPA 8270E/3511NDAnthracene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (a) anthracene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (a) pyrene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (b) fluoranthene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (g,h,i) perylene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (k) fluoranthene
ug/L 6/20/246/20/2410EPA 8270E/3511NDChrysene
ug/L 6/20/246/20/2410EPA 8270E/3511NDDibenzo (a,h) anthracene
ug/L 6/20/246/20/2410EPA 8270E/3511NDFluoranthene
ug/L 6/20/246/20/2410EPA 8270E/3511NDFluorene
ug/L 6/20/246/20/2410EPA 8270E/3511NDIndeno (1,2,3-cd) pyrene
ug/L 6/20/246/20/2410EPA 8270E/3511NDPhenanthrene
ug/L 6/20/246/20/2410EPA 8270E/3511NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 18 of 46Page 18 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-C = Estimated low due to low recovery of CCV
J-LOW-L = Estimated low due to low recovery of LCS
MS-Low = Estimated low due to Matrix Spike recovery.
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 19 of 46Page 19 of 47
Page 20 of 47
Page 21 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYF0795-DUP1 QC Source Sample: 24F1419-02Batch: BYF0795
Date Prepared: 06/18/2024 Date Analyzed: 06/19/2024
Total Solids 1.24 20 80.9 79.9 0.1 1.00
QC Sample ID: BYF0795-DUP2 QC Source Sample: 24F1419-11Batch: BYF0795
Date Prepared: 06/18/2024 Date Analyzed: 06/19/2024
Total Solids 1.83 20 82.4 80.9 0.1 1.00
QC Sample ID: BYF0795-DUP3 QC Source Sample: 24F1419-12Batch: BYF0795
Date Prepared: 06/18/2024 Date Analyzed: 06/19/2024
Total Solids 2.04 20 94.1 96.0 0.1 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 22 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - EPA 1010MOD
QC Sample ID: BYF1146-DUP1 QC Source Sample: 24F1419-11Batch: BYF1146
Date Prepared: 06/25/2024 Date Analyzed: 06/25/2024
Flashpoint 0.00 200 >200 >200 80.0 1.00
Z-01 - >200
Reference - EPA 1010MOD
QC Sample ID: BYF1146-SRM1 Batch: BYF1146
Date Prepared: 06/25/2024 Date Analyzed: 06/25/2024
Flashpoint 98.4 96.06 - 103.7 125 127 80.0 1.00
QC Sample ID: BYF1146-SRM2 Batch: BYF1146
Date Prepared: 06/25/2024 Date Analyzed: 06/25/2024
Flashpoint 100 96.06 - 103.7 127 127 80.0 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 23 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 1311
QC Sample ID: BYF0886-BLK1 Batch: BYF0886
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Percent Pass ND 0.1 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 24 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
QC Sample ID: BYF0896-DUP1 QC Source Sample: 24F1419-11Batch: BYF0896
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Oil & Grease (HEM)200 ND 185 307 1.00
Blank - EPA 1664BMod
QC Sample ID: BYF0896-BLK1 Batch: BYF0896
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Oil & Grease (HEM)ND 250 1.00
LCS - EPA 1664BMod
QC Sample ID: BYF0896-BS1 Batch: BYF0896
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Oil & Grease (HEM)96.5 78 - 114 1930 2000 250 1.00
LCS Dup - EPA 1664BMod
QC Sample ID: BYF0896-BSD1 Batch: BYF0896
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Oil & Grease (HEM)94.5 2.09 78 - 114 18 1890 2000 250 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 25 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6010D
QC Sample ID: BYF0847-BLK1 Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total ND 5.00 1.00
Barium, Total ND 0.500 1.00
Cadmium, Total ND 0.500 1.00
Chromium, Total ND 0.500 1.00
Lead, Total ND 5.00 1.00
Selenium, Total ND 3.00 1.00
Silver, Total ND 0.500 1.00
QC Sample ID: BYF0954-BLK1 Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP ND 0.50 1.00
Lead, TCLP ND 0.20 1.00
QC Sample ID: BYF0954-BLK2 Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP ND 0.50 1.00
Lead, TCLP ND 0.20 1.00
QC Sample ID: BYF1385-BLK1 Batch: BYF1385
Date Prepared: 06/28/2024 Date Analyzed: 06/28/2024
Lead, TCLP ND 0.20 1.00
LCS - EPA 6010D
QC Sample ID: BYF0847-BS1 Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total 105 85 - 115 210 200 5.00 1.00
Barium, Total 101 85 - 115 25.2 24.9 0.500 1.00
Cadmium, Total 107 85 - 115 213 200 0.500 1.00
Chromium, Total 103 85 - 115 206 200 0.500 1.00
Lead, Total 102 85 - 115 205 200 5.00 1.00
Selenium, Total 82.8 85 - 115 166 200 3.00 1.00
NR - No analyte requiring this QC element is included in this analytical bracket.
Silver, Total 104 85 - 115 10.3 9.95 0.500 1.00
QC Sample ID: BYF0954-BS1 Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP 118 85 - 115 2.36 2.00 0.50 1.00
QM-11 - The Laboratory Control Sample recovery was outside acceptance limits. The analytical batch was accepted based on
the recovery of the Method Spike.
Lead, TCLP 106 85 - 115 2.11 2.00 0.20 1.00
QC Sample ID: BYF1385-BS1 Batch: BYF1385
Date Prepared: 06/28/2024 Date Analyzed: 06/28/2024
Lead, TCLP 99.5 85 - 115 1.99 2.00 0.20 1.00
Matrix Spike - EPA 6010D
QC Sample ID: BYF0847-MS2 QC Source Sample: 24F1419-11Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total 81.6 75 - 125 72.4 15.2 70.1 1.75 1.00
Barium, Total 81.3 75 - 125 136 129 8.72 0.175 1.00
Cadmium, Total 78.4 75 - 125 55.5 0.536 70.1 0.175 1.00
Chromium, Total 85.8 75 - 125 69.5 9.37 70.1 0.175 1.00
Lead, Total 72.8 75 - 125 222 171 70.1 1.75 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 26 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 6010D (cont.)
QC Sample ID: BYF0847-MS2 QC Source Sample: 24F1419-11Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Selenium, Total 67.8 75 - 125 47.5 ND 70.1 1.05 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Silver, Total 95.9 75 - 125 3.34 ND 3.49 0.175 1.00
QC Sample ID: BYF0954-MS1 QC Source Sample: 24F1419-12Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP 89.4 75 - 125 2.07 0.28 2.00 0.50 1.00
Lead, TCLP 111 75 - 125 3.50 1.27 2.00 0.20 1.00
QC Sample ID: BYF1385-MS1 QC Source Sample: 24F1419-11Batch: BYF1385
Date Prepared: 06/28/2024 Date Analyzed: 06/28/2024
Lead, TCLP 103 75 - 125 2.48 0.42 2.00 0.20 1.00
Matrix Spike Dup - EPA 6010D
QC Sample ID: BYF0847-MSD2 QC Source Sample: 24F1419-11Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total 83.6 3.39 75 - 125 20 74.9 15.2 71.4 1.78 1.00
Barium, Total 44.6 2.33 75 - 125 20 133 129 8.88 0.178 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Cadmium, Total 81.3 5.41 75 - 125 25 58.5 0.536 71.4 0.178 1.00
Chromium, Total 92.0 7.69 75 - 125 20 75.0 9.37 71.4 0.178 1.00
Lead, Total 108 11.2 75 - 125 20 248 171 71.4 1.78 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Selenium, Total 68.5 2.90 75 - 125 20 48.9 ND 71.4 1.07 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Silver, Total 95.8 1.74 75 - 125 20 3.40 ND 3.55 0.178 1.00
QC Sample ID: BYF0954-MSD1 QC Source Sample: 24F1419-12Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP 92.4 2.90 75 - 125 20 2.13 0.28 2.00 0.50 1.00
Lead, TCLP 105 4.03 75 - 125 20 3.36 1.27 2.00 0.20 1.00
QC Sample ID: BYF1385-MSD1 QC Source Sample: 24F1419-11Batch: BYF1385
Date Prepared: 06/28/2024 Date Analyzed: 06/28/2024
Lead, TCLP 99.7 2.37 75 - 125 20 2.42 0.42 2.00 0.20 1.00
Reference - EPA 6010D
QC Sample ID: BYF0847-SRM1 Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total 83.6 60.07 - 111.31 237 283 10.8 1.00
Barium, Total 94.7 67.8 - 113.2 309 326 1.08 1.00
Cadmium, Total 93.3 65.97 - 109.6 89.4 95.8 1.08 1.00
Chromium, Total 91.5 62.34 - 115.9 219 239 1.08 1.00
Lead, Total 92.0 67.62 - 117.14 193 210 10.8 1.00
CtF WO#: 24F1419
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QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Reference - EPA 6010D (cont.)
QC Sample ID: BYF0847-SRM1 Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Selenium, Total 84.4 67.26 - 126.33 237 281 6.47 1.00
Silver, Total 91.5 65.78 - 119.83 75.7 82.7 1.08 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 28 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 7471A
QC Sample ID: BYF0833-BLK1 Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total ND 0.030 1.00
Duplicate - EPA 7471A
QC Sample ID: BYF0833-DUP1 QC Source Sample: 24F1419-11Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total 17.2 20 0.089 0.075 0.017 1.00
Matrix Spike - EPA 7471A
QC Sample ID: BYF0833-MS1 QC Source Sample: 24F1419-11Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total 139 70 - 130 1.24 0.075 0.839 0.030 1.00
QM-010 - The MS recovery was outside acceptance limits but passed Duplicate Spike acceptance limits. The batch was
accepted based on the acceptability of the MSD as the batch Spike.
Matrix Spike Dup - EPA 7471A
QC Sample ID: BYF0833-MSD1 QC Source Sample: 24F1419-11Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total 101 19.1 70 - 130 20 1.02 0.075 0.944 0.034 1.00
Reference - EPA 7471A
QC Sample ID: BYF0833-SRM1 Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total 57.8 54.636 - 127.27 6.36 11.0 0.688 10.00
CtF WO#: 24F1419
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QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYF0810-BLK1 Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane ND 0.001 1.00
1,1,2-Trichloroethane ND 0.001 1.00
1,1,2-Trichlorotrifluoroethane ND 0.001 1.00
1,1-Dichloroethene ND 0.001 1.00
1,2-Dichlorobenzene ND 0.001 1.00
1,2-Dichloroethane ND 0.001 1.00
1,4-Dichlorobenzene ND 0.001 1.00
2-Nitropropane ND 0.002 1.00
Acetone ND 0.02 1.00
Benzene ND 0.0004 1.00
C5-C6 Aliphatic hydrocarbons ND 0.01 1.00
C7-C8 Aliphatic hydrocarbons ND 0.01 1.00
C9-C10 Aliphatic hydrocarbons ND 0.01 1.00
C9-C10 Alkyl Benzenes ND 0.01 1.00
Carbon Disulfide ND 0.002 1.00
Carbon Tetrachloride ND 0.001 1.00
Chlorobenzene ND 0.001 1.00
Chloroform ND 0.001 1.00
Cyclohexanone ND 0.01 1.00
Ethyl Acetate ND 0.002 1.00
Ethyl Ether ND 0.001 1.00
Ethylbenzene ND 0.001 1.00
Hexachlorobutadiene ND 0.001 1.00
Isobutanol ND 0.02 1.00
Methyl Ethyl Ketone ND 0.002 1.00
Methyl Isobutyl Ketone ND 0.005 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.001 1.00
Methylene Chloride ND 0.001 1.00
Naphthalene ND 0.001 1.00
n-Butyl Alcohol ND 0.05 1.00
Tetrachloroethene ND 0.001 1.00
Toluene ND 0.001 1.00
Trichloroethene ND 0.001 1.00
Trichlorofluoromethane ND 0.001 1.00
Vinyl Chloride ND 0.0008 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYF0881-BLK1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
CtF WO#: 24F1419
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QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYF0881-BLK1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.0004 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
C5-C6 Aliphatic hydrocarbons ND 0.010 1.00
C7-C8 Aliphatic hydrocarbons ND 0.010 1.00
C9-C10 Aliphatic hydrocarbons ND 0.010 1.00
C9-C10 Alkyl Benzenes ND 0.010 1.00
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 0.001 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.001 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 0.001 1.00
n-Butyl Alcohol ND 50.0 1.00
CtF WO#: 24F1419
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QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYF0881-BLK1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 0.001 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYF0810-BS1 Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 88.4 70 - 130 0.009 0.0100 0.001 1.00
1,1,2-Trichloroethane 98.0 70 - 130 0.01 0.0100 0.001 1.00
1,1,2-Trichlorotrifluoroethane 52.9 70 - 130 0.005 0.0100 0.001 1.00
J-LOW-L - Estimated low due to low recovery of LCS
1,1-Dichloroethene 78.9 70 - 130 0.008 0.0100 0.001 1.00
1,2-Dichlorobenzene 110 70 - 130 0.01 0.0100 0.001 1.00
1,2-Dichloroethane 97.4 70 - 130 0.01 0.0100 0.001 1.00
1,4-Dichlorobenzene 114 70 - 130 0.01 0.0100 0.001 1.00
2-Nitropropane 49.4 70 - 130 0.01 0.0300 0.002 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Acetone 97.3 70 - 130 0.1 0.100 0.02 1.00
Benzene 94.2 70 - 130 0.009 0.0100 0.0004 1.00
Carbon Disulfide 41.4 70 - 130 0.004 0.0100 0.002 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Carbon Tetrachloride 80.2 70 - 130 0.008 0.0100 0.001 1.00
Chlorobenzene 97.7 70 - 130 0.01 0.0100 0.001 1.00
Chloroform 92.4 70 - 130 0.009 0.0100 0.001 1.00
Cyclohexanone 137 70 - 130 0.1 0.100 0.01 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Acetate 90.1 70 - 130 0.02 0.0200 0.002 1.00
Ethyl Ether 89.8 70 - 130 0.009 0.0100 0.001 1.00
Ethylbenzene 94.3 70 - 130 0.009 0.0100 0.001 1.00
Hexachlorobutadiene 101 70 - 130 0.01 0.0100 0.001 1.00
Isobutanol 95.6 70 - 130 0.2 0.200 0.02 1.00
Methyl Ethyl Ketone 95.6 70 - 130 0.01 0.0100 0.002 1.00
Methyl Isobutyl Ketone 113 70 - 130 0.01 0.0100 0.005 1.00
Methylene Chloride 88.7 70 - 130 0.009 0.0100 0.001 1.00
n-Butyl Alcohol 100 70 - 130 0.1 0.100 0.05 1.00
Tetrachloroethene 93.2 70 - 130 0.009 0.0100 0.001 1.00
Toluene 89.2 70 - 130 0.009 0.0100 0.001 1.00
Trichloroethene 97.4 70 - 130 0.01 0.0100 0.001 1.00
Trichlorofluoromethane 78.5 70 - 130 0.008 0.0100 0.001 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 32 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYF0810-BS1 Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
Vinyl Chloride 116 70 - 130 0.01 0.0100 0.0008 1.00
Xylenes, total 95.4 70 - 130 0.03 0.0300 0.003 1.00
QC Sample ID: BYF0881-BS1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
1,1,1,2-Tetrachloroethane 107 70 - 130 10.7 10.0 1.0 1.00
1,1,1-Trichloroethane 99.7 70 - 130 9.97 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 116 70 - 130 11.6 10.0 1.0 1.00
1,1,2-Trichloroethane 104 70 - 130 10.4 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 98.5 70 - 130 9.85 10.0 1.0 1.00
1,1-Dichloroethane 74.8 70 - 130 7.48 10.0 1.0 1.00
1,1-Dichloroethene 98.8 70 - 130 9.88 10.0 1.0 1.00
1,1-Dichloropropene 101 70 - 130 10.1 10.0 1.0 1.00
1,2,3-Trichlorobenzene 118 70 - 130 11.8 10.0 1.0 1.00
1,2,3-Trichloropropane 113 70 - 130 11.3 10.0 1.0 1.00
1,2,4-Trichlorobenzene 122 70 - 130 12.2 10.0 1.0 1.00
1,2,4-Trimethylbenzene 113 70 - 130 11.3 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 113 70 - 130 11.3 10.0 1.0 1.00
1,2-Dibromoethane (EDB)107 70 - 130 10.7 10.0 1.0 1.00
1,2-Dichlorobenzene 114 70 - 130 11.4 10.0 1.0 1.00
1,2-Dichloroethane 96.2 70 - 130 9.62 10.0 1.0 1.00
1,2-Dichloropropane 99.2 70 - 130 9.92 10.0 1.0 1.00
1,3,5-Trimethylbenzene 113 70 - 130 11.3 10.0 1.0 1.00
1,3-Dichlorobenzene 115 70 - 130 11.5 10.0 1.0 1.00
1,3-Dichloropropane 102 70 - 130 10.2 10.0 1.0 1.00
1,4-Dichlorobenzene 113 70 - 130 11.3 10.0 1.0 1.00
2,2-Dichloropropane 84.8 70 - 130 8.48 10.0 1.0 1.00
2-Chlorotoluene 108 70 - 130 10.8 10.0 1.0 1.00
2-Hexanone 113 70 - 130 11.3 10.0 10.0 1.00
2-Nitropropane 70.2 70 - 130 21.0 30.0 2.0 1.00
4-Chlorotoluene 109 70 - 130 10.9 10.0 1.0 1.00
Acetone 92.9 70 - 130 92.9 100 20.0 1.00
Acrylonitrile 91.3 70 - 130 45.6 50.0 5.0 1.00
Benzene 102 70 - 130 0.010 0.0100 0.0004 1.00
Bromobenzene 108 70 - 130 10.8 10.0 1.0 1.00
Bromochloromethane 95.4 70 - 130 9.54 10.0 1.0 1.00
Bromodichloromethane 101 70 - 130 10.1 10.0 1.0 1.00
Bromoform 110 70 - 130 11.0 10.0 1.0 1.00
Bromomethane 77.2 70 - 130 7.72 10.0 2.0 1.00
Carbon Disulfide 80.2 70 - 130 8.02 10.0 2.0 1.00
Carbon Tetrachloride 105 70 - 130 10.5 10.0 1.0 1.00
Chlorobenzene 104 70 - 130 10.4 10.0 1.0 1.00
Chloroethane 89.3 70 - 130 8.93 10.0 1.0 1.00
Chloroform 95.5 70 - 130 9.55 10.0 1.0 1.00
Chloromethane 79.2 70 - 130 7.92 10.0 1.0 1.00
cis-1,2-Dichloroethene 97.1 70 - 130 9.71 10.0 1.0 1.00
cis-1,3-Dichloropropene 104 70 - 130 10.4 10.0 1.0 1.00
Cyclohexanone 336 70 - 130 336 100 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Dibromochloromethane 107 70 - 130 10.7 10.0 1.0 1.00
Dibromomethane 108 70 - 130 10.8 10.0 1.0 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 33 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYF0881-BS1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Dichlorodifluoromethane 78.4 70 - 130 7.84 10.0 1.0 1.00
Ethyl Acetate 93.8 70 - 130 18.8 20.0 2.0 1.00
Ethyl Ether 89.1 70 - 130 8.91 10.0 1.0 1.00
Ethylbenzene 105 70 - 130 10.5 10.0 1.0 1.00
Hexachlorobutadiene 116 70 - 130 11.6 10.0 1.0 1.00
Isobutanol 88.8 70 - 130 178 200 20.0 1.00
Isopropylbenzene 112 70 - 130 11.2 10.0 1.0 1.00
Methyl Ethyl Ketone 117 70 - 130 11.7 10.0 2.0 1.00
Methyl Isobutyl Ketone 97.5 70 - 130 9.75 10.0 5.0 1.00
Methylene Chloride 90.6 70 - 130 9.06 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)65.9 70 - 130 6.59 10.0 0.6 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 118 70 - 130 11.8 10.0 1.0 1.00
n-Butyl Alcohol 93.3 70 - 130 93.3 100 50.0 1.00
n-Butylbenzene 118 70 - 130 11.8 10.0 1.0 1.00
n-Propyl Benzene 111 70 - 130 11.1 10.0 1.0 1.00
Pentachloroethane 112 70 - 130 11.2 10.0 1.0 1.00
p-Isopropyltoluene 117 70 - 130 11.7 10.0 1.0 1.00
sec-Butyl Benzene 115 70 - 130 11.5 10.0 1.0 1.00
Styrene 111 70 - 130 11.1 10.0 1.0 1.00
tert-Butylbenzene 115 70 - 130 11.5 10.0 1.0 1.00
Tetrachloroethene 98.2 70 - 130 9.82 10.0 1.0 1.00
Toluene 100 70 - 130 0.010 0.0100 0.001 1.00
trans-1,2-Dichloroethene 95.3 70 - 130 9.53 10.0 1.0 1.00
trans-1,3-Dichloropropene 104 70 - 130 10.4 10.0 1.0 1.00
Trichloroethene 102 70 - 130 10.2 10.0 1.0 1.00
Trichlorofluoromethane 95.2 70 - 130 9.52 10.0 1.0 1.00
Vinyl Chloride 93.2 70 - 130 9.32 10.0 0.8 1.00
Xylenes, total 109 70 - 130 32.8 30.0 3.0 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYF0810-MS1 QC Source Sample: 24F1419-02Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 86.9 70 - 130 0.2 ND 0.282 0.03 1.00
1,1,2-Trichloroethane 125 70 - 130 0.4 ND 0.282 0.03 1.00
1,1,2-Trichlorotrifluoroethane 55.5 70 - 130 0.2 ND 0.282 0.03 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1-Dichloroethene 78.7 70 - 130 0.2 ND 0.282 0.03 1.00
1,2-Dichlorobenzene 99.9 70 - 130 0.3 ND 0.282 0.03 1.00
1,2-Dichloroethane 102 70 - 130 0.3 ND 0.282 0.03 1.00
1,4-Dichlorobenzene 108 70 - 130 0.3 ND 0.282 0.03 1.00
2-Nitropropane 120 70 - 130 1 ND 0.845 0.06 1.00
Acetone 118 70 - 130 3 ND 2.82 0.56 1.00
Benzene -30.0 70 - 130 0.67 0.75 0.282 0.01 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Disulfide 40.8 70 - 130 0.1 ND 0.282 0.06 1.00
CtF WO#: 24F1419
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QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYF0810-MS1 QC Source Sample: 24F1419-02Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Tetrachloride 82.4 70 - 130 0.2 ND 0.282 0.03 1.00
Chlorobenzene 93.2 70 - 130 0.3 ND 0.282 0.03 1.00
Chloroform 94.3 70 - 130 0.3 ND 0.282 0.03 1.00
Cyclohexanone 62.2 70 - 130 2 ND 2.82 0.28 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Ethyl Acetate 306 70 - 130 2 ND 0.563 0.06 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Ether 89.7 70 - 130 0.3 ND 0.282 0.03 1.00
Ethylbenzene 39.1 70 - 130 0.3 0.2 0.282 0.03 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Hexachlorobutadiene 38.7 70 - 130 0.1 ND 0.282 0.03 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Isobutanol 189 70 - 130 11 ND 5.63 0.56 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Methyl Ethyl Ketone 105 70 - 130 0.3 ND 0.282 0.06 1.00
Methyl Isobutyl Ketone 101 70 - 130 0.3 ND 0.282 0.14 1.00
Methylene Chloride 90.4 70 - 130 0.3 ND 0.282 0.03 1.00
n-Butyl Alcohol 245 70 - 130 7 ND 2.82 1.41 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Tetrachloroethene 156 70 - 130 0.4 ND 0.282 0.03 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Toluene 91.3 70 - 130 0.26 ND 0.282 0.03 1.00
Trichloroethene 75.5 70 - 130 0.2 ND 0.282 0.03 1.00
Trichlorofluoromethane 84.1 70 - 130 0.2 ND 0.282 0.03 1.00
Vinyl Chloride 118 70 - 130 0.3 ND 0.282 0.02 1.00
Xylenes, total 53.3 70 - 130 0.8 0.4 0.845 0.08 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
QC Sample ID: BYF0810-MS2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 55.5 70 - 130 1 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1,2-Trichloroethane 92.2 70 - 130 2 ND 2.21 0.22 1.00
1,1,2-Trichlorotrifluoroethane 32.3 70 - 130 0.7 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1-Dichloroethene 48.5 70 - 130 1 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,2-Dichlorobenzene 86.3 70 - 130 2 ND 2.21 0.22 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 35 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYF0810-MS2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,2-Dichloroethane 84.6 70 - 130 2 ND 2.21 0.22 1.00
1,4-Dichlorobenzene 80.4 70 - 130 2 ND 2.21 0.22 1.00
2-Nitropropane 29.4 70 - 130 2 ND 6.62 0.44 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Acetone 94.5 70 - 130 21 ND 22.1 4.41 1.00
Benzene 76.2 70 - 130 1.80 0.12 2.21 0.09 1.00
Carbon Disulfide 26.1 70 - 130 0.6 ND 2.21 0.44 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Tetrachloride 50.2 70 - 130 1 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Chlorobenzene 76.4 70 - 130 2 ND 2.21 0.22 1.00
Chloroform 68.2 70 - 130 2 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Cyclohexanone 24.0 70 - 130 5 ND 22.1 2.21 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Ethyl Acetate 91.1 70 - 130 4 ND 4.41 0.44 1.00
Ethyl Ether 79.3 70 - 130 2 ND 2.21 0.22 1.00
Ethylbenzene 73.1 70 - 130 2 0.4 2.21 0.22 1.00
Hexachlorobutadiene 39.7 70 - 130 0.9 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Isobutanol 31.1 70 - 130 14 ND 44.1 4.41 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Methyl Ethyl Ketone 114 70 - 130 3 ND 2.21 0.44 1.00
Methyl Isobutyl Ketone 103 70 - 130 2 ND 2.21 1.10 1.00
Methylene Chloride 69.8 70 - 130 2 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
n-Butyl Alcohol 119 70 - 130 26 ND 22.1 11.0 1.00
Tetrachloroethene 120 70 - 130 3 ND 2.21 0.22 1.00
Toluene 84.1 70 - 130 1.86 ND 2.21 0.22 1.00
Trichloroethene 134 70 - 130 3 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Trichlorofluoromethane 43.7 70 - 130 1 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Vinyl Chloride 63.2 70 - 130 1 ND 2.21 0.18 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 36 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYF0810-MS2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Xylenes, total 77.7 70 - 130 7 2 6.62 0.66 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYF0810-MSD1 QC Source Sample: 24F1419-02Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 80.8 13.7 70 - 130 20 0.3 ND 0.347 0.03 1.00
1,1,2-Trichloroethane 111 9.50 70 - 130 20 0.4 ND 0.347 0.03 1.00
1,1,2-Trichlorotrifluoroethane 51.4 13.3 70 - 130 20 0.2 ND 0.347 0.03 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1-Dichloroethene 74.2 15.1 70 - 130 20 0.3 ND 0.347 0.03 1.00
1,2-Dichlorobenzene 102 22.7 70 - 130 20 0.4 ND 0.347 0.03 1.00
RPD-01 - RPD between MS and MSD is outside established limits. Data is acceptable based on MS and MSD being within
acceptable recovery limits.
1,2-Dichloroethane 91.2 9.38 70 - 130 20 0.3 ND 0.347 0.03 1.00
1,4-Dichlorobenzene 94.8 7.84 70 - 130 20 0.3 ND 0.347 0.03 1.00
2-Nitropropane 88.8 9.41 70 - 130 20 0.9 ND 1.04 0.07 1.00
Acetone 110 13.8 70 - 130 20 4 ND 3.47 0.69 1.00
Benzene -31.2 3.61 70 - 130 20 0.65 0.75 0.347 0.01 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Disulfide 39.3 17.2 70 - 130 20 0.1 ND 0.347 0.07 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Tetrachloride 72.7 8.44 70 - 130 20 0.3 ND 0.347 0.03 1.00
Chlorobenzene 86.5 13.5 70 - 130 20 0.3 ND 0.347 0.03 1.00
Chloroform 86.3 12.1 70 - 130 20 0.3 ND 0.347 0.03 1.00
Cyclohexanone 76.1 40.5 70 - 130 20 3 ND 3.47 0.35 1.00
RPD-MSOut - The RPD between MS and MSD is outside established control limits.
Ethyl Acetate 228 8.53 70 - 130 20 2 ND 0.695 0.07 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Ether 88.3 19.3 70 - 130 20 0.3 ND 0.347 0.03 1.00
Ethylbenzene 60.3 29.1 70 - 130 20 0.4 0.2 0.347 0.03 1.00
RPD-MSOut - The RPD between MS and MSD is outside established control limits.
Hexachlorobutadiene 40.2 24.6 70 - 130 20 0.1 ND 0.347 0.03 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Isobutanol 151 1.49 70 - 130 20 10 ND 6.95 0.69 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Methyl Ethyl Ketone 83.1 2.70 70 - 130 20 0.3 ND 0.347 0.07 1.00
Methyl Isobutyl Ketone 92.5 11.8 70 - 130 20 0.3 ND 0.347 0.17 1.00
Methylene Chloride 85.1 14.9 70 - 130 20 0.3 ND 0.347 0.03 1.00
n-Butyl Alcohol 170 15.6 70 - 130 20 6 ND 3.47 1.74 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
CtF WO#: 24F1419
www.ChemtechFord.com Page 37 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYF0810-MSD1 QC Source Sample: 24F1419-02Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
Tetrachloroethene 149 15.9 70 - 130 20 0.5 ND 0.347 0.03 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Toluene 82.9 11.3 70 - 130 20 0.29 ND 0.347 0.03 1.00
Trichloroethene 105 53.0 70 - 130 20 0.4 ND 0.347 0.03 1.00
RPD-01 - RPD between MS and MSD is outside established limits. Data is acceptable based on MS and MSD being within
acceptable recovery limits.
Trichlorofluoromethane 77.5 12.8 70 - 130 20 0.3 ND 0.347 0.03 1.00
Vinyl Chloride 111 14.6 70 - 130 20 0.4 ND 0.347 0.03 1.00
Xylenes, total 75.4 34.2 70 - 130 20 1 0.4 1.04 0.10 1.00
RPD-MSOut - The RPD between MS and MSD is outside established control limits.
QC Sample ID: BYF0810-MSD2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 52.8 10.4 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1,2-Trichloroethane 90.1 13.1 70 - 130 20 2 ND 2.57 0.26 1.00
1,1,2-Trichlorotrifluoroethane 28.9 4.29 70 - 130 20 0.7 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1-Dichloroethene 44.2 6.13 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,2-Dichlorobenzene 84.7 13.5 70 - 130 20 2 ND 2.57 0.26 1.00
1,2-Dichloroethane 81.7 11.9 70 - 130 20 2 ND 2.57 0.26 1.00
1,4-Dichlorobenzene 72.3 4.80 70 - 130 20 2 ND 2.57 0.26 1.00
2-Nitropropane 26.7 5.78 70 - 130 20 2 ND 7.72 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Acetone 91.9 12.5 70 - 130 20 24 ND 25.7 5.15 1.00
Benzene 73.5 11.1 70 - 130 20 2.01 0.12 2.57 0.10 1.00
Carbon Disulfide 23.3 4.07 70 - 130 20 0.6 ND 2.57 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Tetrachloride 46.7 8.18 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Chlorobenzene 72.6 10.3 70 - 130 20 2 ND 2.57 0.26 1.00
Chloroform 65.3 11.1 70 - 130 20 2 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Cyclohexanone 26.2 24.1 70 - 130 20 7 ND 25.7 2.57 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Ethyl Acetate 82.8 5.87 70 - 130 20 4 ND 5.15 0.51 1.00
Ethyl Ether 77.6 13.2 70 - 130 20 2 ND 2.57 0.26 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 38 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYF0810-MSD2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
Ethylbenzene 73.9 13.3 70 - 130 20 2 0.4 2.57 0.26 1.00
Hexachlorobutadiene 39.5 14.9 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Isobutanol 24.1 10.1 70 - 130 20 12 ND 51.5 5.15 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Methyl Ethyl Ketone 115 16.0 70 - 130 20 3 ND 2.57 0.51 1.00
Methyl Isobutyl Ketone 97.9 10.3 70 - 130 20 3 ND 2.57 1.29 1.00
Methylene Chloride 66.8 11.0 70 - 130 20 2 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
n-Butyl Alcohol 113 10.4 70 - 130 20 29 ND 25.7 12.9 1.00
Tetrachloroethene 120 15.2 70 - 130 20 3 ND 2.57 0.26 1.00
Toluene 80.1 10.5 70 - 130 20 2.06 ND 2.57 0.26 1.00
Trichloroethene 139 19.2 70 - 130 20 4 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Trichlorofluoromethane 40.2 7.06 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Vinyl Chloride 57.7 6.31 70 - 130 20 1 ND 2.57 0.21 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Xylenes, total 89.4 21.1 70 - 130 20 9 2 7.72 0.77 1.00
RPD-01 - RPD between MS and MSD is outside established limits. Data is acceptable based on MS and MSD being within
acceptable recovery limits.
CtF WO#: 24F1419
www.ChemtechFord.com Page 39 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8270E
QC Sample ID: BYF0957-BLK1 Batch: BYF0957
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Acenaphthene ND 10 1.00
Acenaphthylene ND 10 1.00
Anthracene ND 10 1.00
Benzo (a) anthracene ND 10 1.00
Benzo (a) pyrene ND 10 1.00
Benzo (b) fluoranthene ND 10 1.00
Benzo (g,h,i) perylene ND 10 1.00
Benzo (k) fluoranthene ND 10 1.00
C11-12 Aliphatic hydrocarbons ND 10 1.00
C11-C13 Alkyl Naphthalenes ND 10 1.00
C13-C16 Aliphatic hydrocarbons ND 10 1.00
C17-C21 Aliphatic hydrocarbons ND 10 1.00
C22-C35 Aliphatic hydrocarbons ND 10 1.00
Chrysene ND 10 1.00
Dibenzo (a,h) anthracene ND 10 1.00
Fluoranthene ND 10 1.00
Fluorene ND 10 1.00
Indeno (1,2,3-cd) pyrene ND 10 1.00
Phenanthrene ND 10 1.00
Pyrene ND 10 1.00
Total C12-C22 PAH ND 10 1.00
QC Sample ID: BYF0957-BLK2 Batch: BYF0957
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Acenaphthene ND 10 1.00
Acenaphthylene ND 10 1.00
Anthracene ND 10 1.00
Benzo (a) anthracene ND 10 1.00
Benzo (a) pyrene ND 10 1.00
Benzo (b) fluoranthene ND 10 1.00
Benzo (g,h,i) perylene ND 10 1.00
Benzo (k) fluoranthene ND 10 1.00
C11-12 Aliphatic hydrocarbons ND 10 1.00
C11-C13 Alkyl Naphthalenes ND 10 1.00
C13-C16 Aliphatic hydrocarbons ND 10 1.00
C17-C21 Aliphatic hydrocarbons ND 10 1.00
C22-C35 Aliphatic hydrocarbons ND 10 1.00
Chrysene ND 10 1.00
Dibenzo (a,h) anthracene ND 10 1.00
Fluoranthene ND 10 1.00
Fluorene ND 10 1.00
Indeno (1,2,3-cd) pyrene ND 10 1.00
Phenanthrene ND 10 1.00
Pyrene ND 10 1.00
Total C12-C22 PAH ND 10 1.00
QC Sample ID: BYF1007-BLK1 Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Acenaphthene ND 0.40 1.00
Acenaphthylene ND 0.40 1.00
Anthracene ND 0.40 1.00
Benzo (a) anthracene ND 0.40 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 40 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8270E (cont.)
QC Sample ID: BYF1007-BLK1 Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Benzo (a) pyrene ND 0.40 1.00
Benzo (b) fluoranthene ND 0.40 1.00
Benzo (g,h,i) perylene ND 0.40 1.00
Benzo (k) fluoranthene ND 0.40 1.00
Chrysene ND 0.40 1.00
Fluoranthene ND 0.40 1.00
Fluorene ND 0.40 1.00
Indeno (1,2,3-cd) pyrene ND 0.40 1.00
Phenanthrene ND 0.40 1.00
Pyrene ND 0.40 1.00
LCS - EPA 8270E
QC Sample ID: BYF0957-BS1 Batch: BYF0957
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Acenaphthene 89.4 65 - 135 45 50.0 10 1.00
Acenaphthylene 96.2 65 - 135 48 50.0 10 1.00
Anthracene 95.5 65 - 135 48 50.0 10 1.00
Benzo (a) anthracene 99.3 65 - 135 50 50.0 10 1.00
Benzo (a) pyrene 108 65 - 135 54 50.0 10 1.00
Benzo (b) fluoranthene 104 65 - 135 52 50.0 10 1.00
Benzo (g,h,i) perylene 113 65 - 135 56 50.0 10 1.00
Benzo (k) fluoranthene 95.6 65 - 135 48 50.0 10 1.00
Chrysene 129 65 - 135 64 50.0 10 1.00
Dibenzo (a,h) anthracene 111 65 - 135 56 50.0 10 1.00
Fluoranthene 104 65 - 135 52 50.0 10 1.00
Fluorene 88.4 65 - 135 44 50.0 10 1.00
Indeno (1,2,3-cd) pyrene 114 65 - 135 57 50.0 10 1.00
Phenanthrene 100 65 - 135 50 50.0 10 1.00
Pyrene 103 65 - 135 51 50.0 10 1.00
QC Sample ID: BYF1007-BS1 Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Acenaphthene 68.9 47 - 145 0.5 0.667 0.40 1.00
Acenaphthylene 74.6 65 - 135 0.5 0.667 0.40 1.00
Anthracene 80.3 65 - 135 0.5 0.667 0.40 1.00
Benzo (a) anthracene 92.6 65 - 135 0.6 0.667 0.40 1.00
Benzo (a) pyrene 103 65 - 135 0.7 0.667 0.40 1.00
Benzo (b) fluoranthene 101 65 - 135 0.7 0.667 0.40 1.00
Benzo (g,h,i) perylene 106 65 - 135 0.7 0.667 0.40 1.00
Benzo (k) fluoranthene 99.8 65 - 135 0.7 0.667 0.40 1.00
Chrysene 120 65 - 135 0.8 0.667 0.40 1.00
Fluoranthene 99.9 65 - 135 0.7 0.667 0.40 1.00
Fluorene 67.4 65 - 135 0.4 0.667 0.40 1.00
Indeno (1,2,3-cd) pyrene 109 65 - 135 0.7 0.667 0.40 1.00
Phenanthrene 82.3 65 - 135 0.5 0.667 0.40 1.00
Pyrene 90.2 33 - 130 0.6 0.667 0.40 1.00
Matrix Spike - EPA 8270E
QC Sample ID: BYF1007-MS1 QC Source Sample: 24F1419-02Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Acenaphthene 75.4 47 - 145 2 ND 2.50 1.50 1.00
Acenaphthylene 80.0 50 - 150 2 ND 2.50 1.50 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 41 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8270E (cont.)
QC Sample ID: BYF1007-MS1 QC Source Sample: 24F1419-02Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Anthracene 84.1 50 - 150 2 ND 2.50 1.50 1.00
Benzo (a) anthracene 88.5 50 - 150 2 ND 2.50 1.50 1.00
Benzo (a) pyrene 97.9 50 - 150 2 ND 2.50 1.50 1.00
Benzo (b) fluoranthene 94.7 50 - 150 2 ND 2.50 1.50 1.00
Benzo (g,h,i) perylene 99.1 50 - 150 2 ND 2.50 1.50 1.00
Benzo (k) fluoranthene 92.8 50 - 150 2 ND 2.50 1.50 1.00
Chrysene 111 50 - 150 3 ND 2.50 1.50 1.00
Fluoranthene 109 50 - 150 3 ND 2.50 1.50 1.00
Fluorene 46.3 50 - 150 2 1 2.50 1.50 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Indeno (1,2,3-cd) pyrene 101 50 - 150 3 ND 2.50 1.50 1.00
Phenanthrene 44.8 50 - 150 5 3 2.50 1.50 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Pyrene 79.2 33 - 130 2 ND 2.50 1.50 1.00
Matrix Spike Dup - EPA 8270E
QC Sample ID: BYF1007-MSD1 QC Source Sample: 24F1419-02Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Acenaphthene 77.5 2.78 47 - 145 200 2 ND 2.50 1.50 1.00
Acenaphthylene 71.5 11.2 50 - 150 200 2 ND 2.50 1.50 1.00
Anthracene 88.2 4.75 50 - 150 200 2 ND 2.50 1.50 1.00
Benzo (a) anthracene 92.5 4.38 50 - 150 200 2 ND 2.50 1.50 1.00
Benzo (a) pyrene 102 3.86 50 - 150 200 3 ND 2.50 1.50 1.00
Benzo (b) fluoranthene 100 5.49 50 - 150 200 3 ND 2.50 1.50 1.00
Benzo (g,h,i) perylene 109 9.56 50 - 150 200 3 ND 2.50 1.50 1.00
Benzo (k) fluoranthene 91.4 1.57 50 - 150 200 2 ND 2.50 1.50 1.00
Chrysene 117 5.07 50 - 150 200 3 ND 2.50 1.50 1.00
Fluoranthene 105 3.27 50 - 150 200 3 ND 2.50 1.50 1.00
Fluorene 52.1 6.09 50 - 150 200 2 1 2.50 1.50 1.00
Indeno (1,2,3-cd) pyrene 110 8.40 50 - 150 200 3 ND 2.50 1.50 1.00
Phenanthrene 44.1 0.354 50 - 150 200 5 3 2.50 1.50 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Pyrene 100 23.5 33 - 130 200 3 ND 2.50 1.50 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 42 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - EPA 9040C/9045D
QC Sample ID: BYF0827-DUP1 QC Source Sample: 24F1419-11Batch: BYF0827
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
pH 0.00 3 10.5 10.5 0.1 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 43 of 47
Surrogates Report for Work Order (WO) - 24F1419
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8260D
BYF0810-BLK1 1,2-Dichloroethane-d4 99.4 70 BYF0810 1.001300.00994 0.0100
BYF0810-BLK1 1,2-Dichloroethane-d4 99.4 70 BYF0810 1.001300.00994 0.0100
BYF0810-BLK1 Toluene-d8 98.9 70 BYF0810 1.001300.00989 0.0100
BYF0810-BLK1 4-Bromofluorobenzene 104 70 BYF0810 1.001300.0104 0.0100
BYF0810-BLK1 4-Bromofluorobenzene 104 70 BYF0810 1.001300.0104 0.0100
BYF0810-BLK1 Toluene-d8 98.9 70 BYF0810 1.001300.00989 0.0100
BYF0881-BLK1 1,2-Dichloroethane-d4 97.1 64.2 BYF0881 1.001269.71 10.0
BYF0881-BLK1 1,2-Dichloroethane-d4 97.1 70 BYF0881 1.001300.00971 0.0100
BYF0881-BLK1 Toluene-d8 101 70 BYF0881 1.001300.0101 0.0100
BYF0881-BLK1 4-Bromofluorobenzene 98.5 71.4 BYF0881 1.001259.85 10.0
BYF0881-BLK1 4-Bromofluorobenzene 98.5 70 BYF0881 1.001300.00985 0.0100
BYF0881-BLK1 Toluene-d8 101 63.2 BYF0881 1.0012910.1 10.0
LCS - EPA 8260D
BYF0810-BS1 1,2-Dichloroethane-d4 95.6 70 BYF0810 1.001300.00956 0.0100
BYF0810-BS1 1,2-Dichloroethane-d4 95.6 70 BYF0810 1.001300.00956 0.0100
BYF0810-BS1 Toluene-d8 93.0 70 BYF0810 1.001300.00930 0.0100
BYF0810-BS1 4-Bromofluorobenzene 100 70 BYF0810 1.001300.0100 0.0100
BYF0810-BS1 4-Bromofluorobenzene 100 70 BYF0810 1.001300.0100 0.0100
BYF0810-BS1 Toluene-d8 93.0 70 BYF0810 1.001300.00930 0.0100
BYF0881-BS1 1,2-Dichloroethane-d4 98.5 64.2 BYF0881 1.001269.85 10.0
BYF0881-BS1 1,2-Dichloroethane-d4 98.5 70 BYF0881 1.001300.00985 0.0100
BYF0881-BS1 Toluene-d8 101 70 BYF0881 1.001300.0101 0.0100
BYF0881-BS1 4-Bromofluorobenzene 100 70 BYF0881 1.001300.0100 0.0100
BYF0881-BS1 4-Bromofluorobenzene 100 71.4 BYF0881 1.0012510.0 10.0
BYF0881-BS1 Toluene-d8 101 63.2 BYF0881 1.0012910.1 10.0
Matrix Spike - EPA 8260D
BYF0810-MS2 1,2-Dichloroethane-d4 99.8 70 BYF0810 1.001302.20 2.21
BYF0810-MS1 1,2-Dichloroethane-d4 108 70 BYF0810 1.001300.303 0.282
BYF0810-MS2 1,2-Dichloroethane-d4 99.8 70 BYF0810 1.001302.20 2.21
BYF0810-MS1 1,2-Dichloroethane-d4 108 70 BYF0810 1.001300.303 0.282
BYF0810-MS1 Toluene-d8 99.4 70 BYF0810 1.001300.280 0.282
BYF0810-MS2 Toluene-d8 95.6 70 BYF0810 1.001302.11 2.21
BYF0810-MS2 4-Bromofluorobenzene 97.8 70 BYF0810 1.001302.16 2.21
BYF0810-MS2 4-Bromofluorobenzene 97.8 70 BYF0810 1.001302.16 2.21
BYF0810-MS1 4-Bromofluorobenzene 104 70 BYF0810 1.001300.293 0.282
BYF0810-MS1 4-Bromofluorobenzene 104 70 BYF0810 1.001300.293 0.282
BYF0810-MS2 Toluene-d8 95.6 70 BYF0810 1.001302.11 2.21
BYF0810-MS1 Toluene-d8 99.4 70 BYF0810 1.001300.280 0.282
BYF0881-MS1 1,2-Dichloroethane-d4 99.4 70 BYF0881 1.001300.0497 0.0500
BYF0881-MS1 1,2-Dichloroethane-d4 99.4 64.2 BYF0881 1.0012649.7 50.0
BYF0881-MS1 Toluene-d8 101 70 BYF0881 1.001300.0506 0.0500
BYF0881-MS1 4-Bromofluorobenzene 100 71.4 BYF0881 1.0012550.1 50.0
BYF0881-MS1 4-Bromofluorobenzene 100 70 BYF0881 1.001300.0501 0.0500
BYF0881-MS1 Toluene-d8 101 63.2 BYF0881 1.0012950.6 50.0
Matrix Spike Dup - EPA 8260D
BYF0810-MSD2 1,2-Dichloroethane-d4 98.3 70 BYF0810 1.001302.53 2.57
CtF WO#: 24F1419
www.ChemtechFord.com Page 44 of 47
Matrix Spike Dup - EPA 8260D (cont.)
BYF0810-MSD2 1,2-Dichloroethane-d4 98.3 70 BYF0810 1.001302.53 2.57
BYF0810-MSD1 1,2-Dichloroethane-d4 100 70 BYF0810 1.001300.349 0.347
BYF0810-MSD1 1,2-Dichloroethane-d4 100 70 BYF0810 1.001300.349 0.347
BYF0810-MSD2 Toluene-d8 96.3 70 BYF0810 1.001302.48 2.57
BYF0810-MSD1 Toluene-d8 93.7 70 BYF0810 1.001300.326 0.347
BYF0810-MSD2 4-Bromofluorobenzene 96.1 70 BYF0810 1.001302.47 2.57
BYF0810-MSD1 4-Bromofluorobenzene 101 70 BYF0810 1.001300.351 0.347
BYF0810-MSD2 4-Bromofluorobenzene 96.1 70 BYF0810 1.001302.47 2.57
BYF0810-MSD1 4-Bromofluorobenzene 101 70 BYF0810 1.001300.351 0.347
BYF0810-MSD1 Toluene-d8 93.7 70 BYF0810 1.001300.326 0.347
BYF0810-MSD2 Toluene-d8 96.3 70 BYF0810 1.001302.48 2.57
BYF0881-MSD1 1,2-Dichloroethane-d4 98.7 64.2 BYF0881 1.0012649.4 50.0
BYF0881-MSD1 1,2-Dichloroethane-d4 98.7 70 BYF0881 1.001300.0494 0.0500
BYF0881-MSD1 Toluene-d8 100 70 BYF0881 1.001300.0502 0.0500
BYF0881-MSD1 4-Bromofluorobenzene 100 71.4 BYF0881 1.0012550.0 50.0
BYF0881-MSD1 4-Bromofluorobenzene 100 70 BYF0881 1.001300.0500 0.0500
BYF0881-MSD1 Toluene-d8 100 63.2 BYF0881 1.0012950.0 50.0
Blank - EPA 8270E
BYF0957-BLK1 2-Fluorobiphenyl 71.4 16 BYF0957 1.0015289.3 125
BYF0957-BLK2 2-Fluorobiphenyl 75.2 16 BYF0957 1.0015293.9 125
BYF0957-BLK2 Terphenyl-dl4 82.4 41 BYF0957 1.00174 103 125
BYF0957-BLK1 Terphenyl-dl4 77.5 41 BYF0957 1.0017496.8 125
BYF1007-BLK1 2-Fluorobiphenyl 101 37 BYF1007 1.001400.336 0.333
BYF1007-BLK1 Terphenyl-dl4 88.9 31 BYF1007 1.001400.296 0.333
LCS - EPA 8270E
BYF0957-BS1 2-Fluorobiphenyl 90.8 16 BYF0957 1.00152114125
BYF0957-BS1 Terphenyl-dl4 81.9 41 BYF0957 1.00174 102 125
BYF1007-BS1 2-Fluorobiphenyl 109 37 BYF1007 1.001400.362 0.333
BYF1007-BS1 Terphenyl-dl4 98.5 31 BYF1007 1.001400.328 0.333
Matrix Spike - EPA 8270E
BYF0957-MS1 2-Fluorobiphenyl 84.3 16 BYF0957 1.0015242200005000000
BYF0957-MS1 Terphenyl-dl4 81.4 41 BYF0957 1.0017440700005000000
BYF1007-MS1 2-Fluorobiphenyl 101 37 BYF1007 1.001401.26 1.25
BYF1007-MS1 Terphenyl-dl4 79.3 31 BYF1007 1.001400.991 1.25
Matrix Spike Dup - EPA 8270E
BYF0957-MSD1 2-Fluorobiphenyl 83.5 16 BYF0957 1.0015241700005000000
BYF0957-MSD1 Terphenyl-dl4 80.8 41 BYF0957 1.0017440400005000000
BYF1007-MSD1 2-Fluorobiphenyl 88.4 37 BYF1007 1.001401.11 1.25
BYF1007-MSD1 Terphenyl-dl4 90.2 31 BYF1007 1.001401.13 1.25
CtF WO#: 24F1419
www.ChemtechFord.com Page 45 of 47
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
8260 TPH Fractionation
24F1419-01 4-Bromofluorobenzene 0.280 95.2 70 1300.294
24F1419-01 Toluene-d8 0.288 98.0 70 1300.294
24F1419-01 1,2-Dichloroethane-d4 0.307 104 70 1300.294
8270 TPH Fractionation
24F1419-01 2-Fluorobiphenyl 0.365 89.4 37 1400.408
24F1419-01 Terphenyl-dl4 0.328 80.4 31 1400.408
8260 TPH Fractionation
24F1419-02 1,2-Dichloroethane-d4 0.302 106 70 1300.284
24F1419-02 4-Bromofluorobenzene 0.320 113 70 1300.284
24F1419-02 Toluene-d8 0.263 92.6 70 1300.284
8270 TPH Fractionation
24F1419-02 2-Fluorobiphenyl 1.23 98.3 37 1401.25
24F1419-02 Terphenyl-dl4 1.10 88.3 31 1401.25
8260 TPH Fractionation
24F1419-03 Toluene-d8 2.01 95.7 70 1302.10
24F1419-03 1,2-Dichloroethane-d4 2.10 99.9 70 1302.10
24F1419-03 4-Bromofluorobenzene 2.00 95.0 70 1302.10
8270 TPH Fractionation
24F1419-03 2-Fluorobiphenyl 0.889 81.3 37 1401.09
24F1419-03 Terphenyl-dl4 0.815 74.5 31 1401.09
8260 TPH Fractionation
24F1419-04 1,2-Dichloroethane-d4 0.331 102 70 1300.325
24F1419-04 4-Bromofluorobenzene 0.315 97.0 70 1300.325
24F1419-04 Toluene-d8 0.302 93.0 70 1300.325
8270 TPH Fractionation
24F1419-04 2-Fluorobiphenyl 0.378 84.0 37 1400.450
24F1419-04 Terphenyl-dl4 0.381 84.5 31 1400.450
8260 TPH Fractionation
24F1419-05 1,2-Dichloroethane-d4 0.306 103 70 1300.297
24F1419-05 4-Bromofluorobenzene 0.285 96.0 70 1300.297
24F1419-05 Toluene-d8 0.284 95.7 70 1300.297
8270 TPH Fractionation
24F1419-05 2-Fluorobiphenyl 0.389 91.0 37 1400.427
24F1419-05 Terphenyl-dl4 0.364 85.3 31 1400.427
8260 TPH Fractionation
24F1419-06 4-Bromofluorobenzene 0.294 97.8 70 1300.300
24F1419-06 Toluene-d8 0.291 97.0 70 1300.300
24F1419-06 1,2-Dichloroethane-d4 0.310 103 70 1300.300
CtF WO#: 24F1419
www.ChemtechFord.com Page 46 of 47
8270 TPH Fractionation
24F1419-06 Terphenyl-dl4 0.358 81.3 31 1400.441
24F1419-06 2-Fluorobiphenyl 0.442 100 37 1400.441
8260 TPH Fractionation
24F1419-07 1,2-Dichloroethane-d4 0.311 102 70 1300.303
24F1419-07 4-Bromofluorobenzene 0.293 96.6 70 1300.303
24F1419-07 Toluene-d8 0.296 97.7 70 1300.303
8270 TPH Fractionation
24F1419-07 2-Fluorobiphenyl 0.351 86.8 37 1400.405
24F1419-07 Terphenyl-dl4 0.335 82.9 31 1400.405
8270 TPH Fractionation
24F1419-08 2-Fluorobiphenyl 0.320 95.8 37 1400.334
24F1419-08 Terphenyl-dl4 0.244 73.1 31 1400.334
8270 TPH Fractionation
24F1419-09 Terphenyl-dl4 0.298 88.1 31 1400.338
24F1419-09 2-Fluorobiphenyl 0.351 104 37 1400.338
8270 TPH Fractionation
24F1419-10 2-Fluorobiphenyl 0.282 84.9 37 1400.333
24F1419-10 Terphenyl-dl4 0.233 70.1 31 1400.333
8260 F&D Volatiles
24F1419-11 Toluene-d8 2.73 97.2 70 1302.81
24F1419-11 1,2-Dichloroethane-d4 2.82 101 70 1302.81
24F1419-11 4-Bromofluorobenzene 2.80 99.6 70 1302.81
8260 Low Level Volatiles
24F1419-13 Toluene-d8 10.0 100 63.2 12910.0
24F1419-13 1,2-Dichloroethane-d4 10.0 100 64.2 12610.0
24F1419-13 4-Bromofluorobenzene 9.85 98.5 71.4 12510.0
8260 TPH Fractionation
24F1419-14 1,2-Dichloroethane-d4 0.124 99.1 70 1300.125
24F1419-14 4-Bromofluorobenzene 0.125 99.9 70 1300.125
24F1419-14 Toluene-d8 0.126 101 70 1300.125
8270 TPH Fractionation
24F1419-14 Terphenyl-dl4 111 89.1 41 174125
24F1419-14 2-Fluorobiphenyl 99.1 79.3 16 152125
CtF WO#: 24F1419
www.ChemtechFord.com Page 47 of 47

Appendix J
Analytical Laboratory Reports

The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H0986
Project: Former Sommers Auto Wrecking
8/14/2024
Approved By:
Andrew Royer, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
8/14/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-SW
Lab ID: 24H0986-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/7/24 9:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/13/248/13/2464EPA 8015 CNDDiesel Range Organics
Inorganic
%8/13/248/13/240.1 CTF800078.1Total Solids
MBTEXn
mg/kg dry 8/13/248/13/240.003 EPA 8260D/5035ANDBenzene
mg/kg dry 8/13/248/13/240.007 EPA 8260D/5035ANDEthylbenzene
mg/kg dry 8/13/248/13/240.004 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/13/248/13/240.007 EPA 8260D/5035A0.03Naphthalene
mg/kg dry 8/13/248/13/240.007 EPA 8260D/5035ANDToluene
mg/kg dry 8/13/248/13/240.02 EPA 8260D/5035ANDXylenes, total
Gasoline Range
mg/kg dry 8/13/248/13/240.0713 EPA 8260B/C 5035A/[CALC]0.644Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 2 of 17Page 2 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
8/14/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-SE
Lab ID: 24H0986-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/12/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/13/248/13/2462EPA 8015 CNDDiesel Range Organics
Inorganic
%8/13/248/13/240.1 CTF800080.5Total Solids
MBTEXn
mg/kg dry 8/12/248/12/240.003 EPA 8260D/5035ANDBenzene
mg/kg dry 8/12/248/12/240.007 EPA 8260D/5035ANDEthylbenzene
mg/kg dry J-LOW-L8/12/248/12/240.004 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/12/248/12/240.007 EPA 8260D/5035ANDNaphthalene
mg/kg dry 8/12/248/12/240.007 EPA 8260D/5035ANDToluene
mg/kg dry 8/12/248/12/240.02 EPA 8260D/5035ANDXylenes, total
Gasoline Range
mg/kg dry 8/12/248/12/240.0698 EPA 8260B/C 5035A/[CALC]0.0716Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 3 of 17Page 3 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
8/14/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-West 1
Lab ID: 24H0986-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/12/24 12:40
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/13/248/13/2463EPA 8015 CNDDiesel Range Organics
Inorganic
%8/13/248/13/240.1 CTF800079.1Total Solids
MBTEXn
mg/kg dry 8/12/248/12/240.002 EPA 8260D/5035A0.04Benzene
mg/kg dry 8/12/248/12/240.006 EPA 8260D/5035A0.01Ethylbenzene
mg/kg dry J-LOW-L8/12/248/12/240.004 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/12/248/12/240.006 EPA 8260D/5035A0.007Naphthalene
mg/kg dry 8/12/248/12/240.006 EPA 8260D/5035ANDToluene
mg/kg dry 8/12/248/12/240.02 EPA 8260D/5035A0.04Xylenes, total
Gasoline Range
mg/kg dry 8/12/248/12/240.0585 EPA 8260B/C 5035A/[CALC]0.651Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 4 of 17Page 4 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
8/14/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24H0986-04Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/7/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 8/12/248/12/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L 8/12/248/12/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 8/12/248/12/2420.0 EPA 8260D/5030BNDAcetone
ug/L 8/12/248/12/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 8/12/248/12/240.4 EPA 8260D/5030BNDBenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDBromodichloromethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDBromoform
ug/L J-LOW-L8/12/248/12/242.0 EPA 8260D/5030BNDBromomethane
ug/L 8/12/248/12/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 5 of 17Page 5 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
8/14/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24H0986-04Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/7/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDChloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDChloroform
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDChloromethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L 8/12/248/12/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDDibromochloromethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDDibromomethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 8/12/248/12/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 8/12/248/12/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 8/12/248/12/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 8/12/248/12/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L J-LOW-L8/12/248/12/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDNaphthalene
ug/L 8/12/248/12/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDStyrene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDToluene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 8/12/248/12/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 8/12/248/12/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 6 of 17Page 6 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
8/14/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-L = Estimated low due to low recovery of LCS
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 7 of 17Page 7 of 17
Page 8 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH0591-BLK1 Batch: BYH0591
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Diesel Range Organics ND 50 1.00
LCS - EPA 8015 C
QC Sample ID: BYH0591-BS1 Batch: BYH0591
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Diesel Range Organics 107 50 - 150 2150 2000 50 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH0591-MS1 QC Source Sample: 24H0986-01Batch: BYH0591
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Diesel Range Organics 101 50 - 150 2590 ND 2560 64 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH0591-MSD1 QC Source Sample: 24H0986-01Batch: BYH0591
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Diesel Range Organics 102 0.852 50 - 150 20 2610 ND 2560 64 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 9 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH0548-BLK1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.4 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 1.0 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 10 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYH0548-BLK1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 1.0 1.00
n-Butyl Alcohol ND 50.0 1.00
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 1.0 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 3.0 1.00
QC Sample ID: BYH0558-BLK1 Batch: BYH0558
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH0617-BLK1 Batch: BYH0617
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYH0548-BS1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,1,1,2-Tetrachloroethane 108 70 - 130 10.8 10.0 1.0 1.00
1,1,1-Trichloroethane 99.9 70 - 130 9.99 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 105 70 - 130 10.5 10.0 1.0 1.00
1,1,2-Trichloroethane 101 70 - 130 10.1 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 104 70 - 130 10.4 10.0 1.0 1.00
1,1-Dichloroethane 107 70 - 130 10.7 10.0 1.0 1.00
1,1-Dichloroethene 91.7 70 - 130 9.17 10.0 1.0 1.00
1,1-Dichloropropene 93.4 70 - 130 9.34 10.0 1.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 11 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH0548-BS1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,2,3-Trichlorobenzene 113 70 - 130 11.3 10.0 1.0 1.00
1,2,3-Trichloropropane 103 70 - 130 10.3 10.0 1.0 1.00
1,2,4-Trichlorobenzene 116 70 - 130 11.6 10.0 1.0 1.00
1,2,4-Trimethylbenzene 101 70 - 130 10.1 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dibromoethane (EDB)105 70 - 130 10.5 10.0 1.0 1.00
1,2-Dichlorobenzene 106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dichloroethane 99.9 70 - 130 9.99 10.0 1.0 1.00
1,2-Dichloropropane 99.7 70 - 130 9.97 10.0 1.0 1.00
1,3,5-Trimethylbenzene 102 70 - 130 10.2 10.0 1.0 1.00
1,3-Dichlorobenzene 108 70 - 130 10.8 10.0 1.0 1.00
1,3-Dichloropropane 101 70 - 130 10.1 10.0 1.0 1.00
1,4-Dichlorobenzene 108 70 - 130 10.8 10.0 1.0 1.00
2,2-Dichloropropane 93.2 70 - 130 9.32 10.0 1.0 1.00
2-Chlorotoluene 98.2 70 - 130 9.82 10.0 1.0 1.00
2-Hexanone 117 70 - 130 11.7 10.0 10.0 1.00
2-Nitropropane 84.5 70 - 130 25.4 30.0 2.0 1.00
4-Chlorotoluene 97.9 70 - 130 9.79 10.0 1.0 1.00
Acetone 99.6 70 - 130 99.6 100 20.0 1.00
Acrylonitrile 91.3 70 - 130 45.7 50.0 5.0 1.00
Benzene 102 70 - 130 10.2 10.0 0.4 1.00
Bromobenzene 98.8 70 - 130 9.88 10.0 1.0 1.00
Bromochloromethane 103 70 - 130 10.3 10.0 1.0 1.00
Bromodichloromethane 101 70 - 130 10.1 10.0 1.0 1.00
Bromoform 97.3 70 - 130 9.73 10.0 1.0 1.00
Bromomethane 54.0 70 - 130 5.40 10.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Carbon Disulfide 97.4 70 - 130 9.74 10.0 2.0 1.00
Carbon Tetrachloride 106 70 - 130 10.6 10.0 1.0 1.00
Chlorobenzene 103 70 - 130 10.3 10.0 1.0 1.00
Chloroethane 87.8 70 - 130 8.78 10.0 1.0 1.00
Chloroform 92.5 70 - 130 9.25 10.0 1.0 1.00
Chloromethane 79.9 70 - 130 7.99 10.0 1.0 1.00
cis-1,2-Dichloroethene 90.4 70 - 130 9.04 10.0 1.0 1.00
cis-1,3-Dichloropropene 110 70 - 130 11.0 10.0 1.0 1.00
Cyclohexanone 109 70 - 130 109 100 10.0 1.00
Dibromochloromethane 103 70 - 130 10.3 10.0 1.0 1.00
Dibromomethane 108 70 - 130 10.8 10.0 1.0 1.00
Dichlorodifluoromethane 84.8 70 - 130 8.48 10.0 1.0 1.00
Ethyl Acetate 96.1 70 - 130 19.2 20.0 2.0 1.00
Ethyl Ether 89.0 70 - 130 8.90 10.0 1.0 1.00
Ethylbenzene 95.1 70 - 130 9.51 10.0 1.0 1.00
Hexachlorobutadiene 108 70 - 130 10.8 10.0 1.0 1.00
Isobutanol 127 70 - 130 255 200 20.0 1.00
Isopropylbenzene 98.8 70 - 130 9.88 10.0 1.0 1.00
Methyl Ethyl Ketone 88.6 70 - 130 8.86 10.0 2.0 1.00
Methyl Isobutyl Ketone 101 70 - 130 10.1 10.0 5.0 1.00
Methylene Chloride 101 70 - 130 10.1 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)66.0 70 - 130 6.60 10.0 0.6 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 105 70 - 130 10.5 10.0 1.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 12 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH0548-BS1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
n-Butyl Alcohol 93.2 70 - 130 93.2 100 50.0 1.00
n-Butylbenzene 99.9 70 - 130 9.99 10.0 1.0 1.00
n-Propyl Benzene 99.8 70 - 130 9.98 10.0 1.0 1.00
Pentachloroethane 111 70 - 130 11.1 10.0 1.0 1.00
p-Isopropyltoluene 97.9 70 - 130 9.79 10.0 1.0 1.00
sec-Butyl Benzene 97.3 70 - 130 9.73 10.0 1.0 1.00
Styrene 107 70 - 130 10.7 10.0 1.0 1.00
tert-Butylbenzene 98.0 70 - 130 9.80 10.0 1.0 1.00
Tetrachloroethene 90.3 70 - 130 9.03 10.0 1.0 1.00
Toluene 94.6 70 - 130 9.46 10.0 1.0 1.00
trans-1,2-Dichloroethene 91.3 70 - 130 9.13 10.0 1.0 1.00
trans-1,3-Dichloropropene 111 70 - 130 11.1 10.0 1.0 1.00
Trichloroethene 100 70 - 130 10.0 10.0 1.0 1.00
Trichlorofluoromethane 85.0 70 - 130 8.50 10.0 1.0 1.00
Vinyl Chloride 78.2 70 - 130 7.82 10.0 0.8 1.00
Xylenes, total 103 70 - 130 30.9 30.0 3.0 1.00
QC Sample ID: BYH0558-BS1 Batch: BYH0558
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Benzene 85.1 70 - 130 0.009 0.0100 0.0004 1.00
Ethylbenzene 81.6 70 - 130 0.008 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)67.8 70 - 130 0.007 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 95.7 70 - 130 0.01 0.0100 0.001 1.00
Toluene 78.3 70 - 130 0.008 0.0100 0.001 1.00
Xylenes, total 89.0 70 - 130 0.03 0.0300 0.003 1.00
QC Sample ID: BYH0617-BS1 Batch: BYH0617
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Benzene 85.3 70 - 130 0.009 0.0100 0.0004 1.00
Ethylbenzene 98.0 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)95.4 70 - 130 0.01 0.0100 0.0006 1.00
Naphthalene 88.7 70 - 130 0.009 0.0100 0.001 1.00
Toluene 86.8 70 - 130 0.009 0.0100 0.001 1.00
Xylenes, total 97.4 70 - 130 0.03 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH0548-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,1,1,2-Tetrachloroethane 96.5 70 - 130 48.2 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 100 70 - 130 50.1 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 93.4 70 - 130 46.7 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 95.1 70 - 130 47.6 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 92.0 70 - 130 46.0 ND 50.0 5.0 1.00
1,1-Dichloroethane 99.1 70 - 130 49.6 ND 50.0 5.0 1.00
1,1-Dichloroethene 86.1 70 - 130 43.0 ND 50.0 5.0 1.00
1,1-Dichloropropene 87.5 70 - 130 43.8 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 95.0 70 - 130 47.5 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 92.6 70 - 130 46.3 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 98.2 70 - 130 49.1 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 95.7 70 - 130 47.8 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 87.2 70 - 130 43.6 ND 50.0 5.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 13 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH0548-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,2-Dibromoethane (EDB)93.4 70 - 130 46.7 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 96.0 70 - 130 48.0 ND 50.0 5.0 1.00
1,2-Dichloroethane 91.4 70 - 130 45.7 ND 50.0 5.0 1.00
1,2-Dichloropropane 94.1 70 - 130 47.0 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 97.5 70 - 130 48.8 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 99.8 70 - 130 49.9 ND 50.0 5.0 1.00
1,3-Dichloropropane 95.0 70 - 130 47.5 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 98.4 70 - 130 49.2 ND 50.0 5.0 1.00
2,2-Dichloropropane 71.0 70 - 130 35.5 ND 50.0 5.0 1.00
2-Chlorotoluene 94.3 70 - 130 47.2 ND 50.0 5.0 1.00
2-Hexanone 117 70 - 130 58.4 ND 50.0 50.0 1.00
2-Nitropropane 81.6 70 - 130 122 ND 150 10.0 1.00
4-Chlorotoluene 92.0 70 - 130 46.0 ND 50.0 5.0 1.00
Acetone 94.6 70 - 130 473 ND 500 100 1.00
Acrylonitrile 86.2 70 - 130 215 ND 250 25.0 1.00
Benzene 97.6 70 - 130 48.8 ND 50.0 2.0 1.00
Bromobenzene 93.3 70 - 130 46.6 ND 50.0 5.0 1.00
Bromochloromethane 94.4 70 - 130 47.2 ND 50.0 5.0 1.00
Bromodichloromethane 95.6 70 - 130 47.8 ND 50.0 5.0 1.00
Bromoform 90.5 70 - 130 45.2 ND 50.0 5.0 1.00
Bromomethane 46.5 70 - 130 23.2 ND 50.0 10.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Disulfide 77.4 70 - 130 38.7 ND 50.0 10.0 1.00
Carbon Tetrachloride 101 70 - 130 50.4 ND 50.0 5.0 1.00
Chlorobenzene 98.1 70 - 130 49.0 ND 50.0 5.0 1.00
Chloroethane 87.8 70 - 130 43.9 ND 50.0 5.0 1.00
Chloroform 89.2 70 - 130 44.6 ND 50.0 5.0 1.00
Chloromethane 68.2 70 - 130 34.1 ND 50.0 5.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
cis-1,2-Dichloroethene 88.4 70 - 130 44.2 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 101 70 - 130 50.4 ND 50.0 5.0 1.00
Cyclohexanone 112 70 - 130 560 ND 500 50.0 1.00
Dibromochloromethane 91.6 70 - 130 45.8 ND 50.0 5.0 1.00
Dibromomethane 104 70 - 130 51.8 ND 50.0 5.0 1.00
Dichlorodifluoromethane 56.9 70 - 130 28.4 ND 50.0 5.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Ethyl Acetate 89.8 70 - 130 89.8 ND 100 10.0 1.00
Ethyl Ether 79.2 70 - 130 39.6 ND 50.0 5.0 1.00
Ethylbenzene 91.9 70 - 130 46.0 ND 50.0 5.0 1.00
Hexachlorobutadiene 98.0 70 - 130 49.0 ND 50.0 5.0 1.00
Isobutanol 117 70 - 130 1170 ND 1000 100 1.00
Isopropylbenzene 94.7 70 - 130 47.4 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 83.1 70 - 130 41.6 ND 50.0 10.0 1.00
Methyl Isobutyl Ketone 98.8 70 - 130 49.4 ND 50.0 25.0 1.00
Methylene Chloride 88.3 70 - 130 44.2 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)57.8 70 - 130 28.9 ND 50.0 3.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 14 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH0548-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Naphthalene 85.4 70 - 130 42.7 ND 50.0 5.0 1.00
n-Butyl Alcohol 87.6 70 - 130 438 ND 500 250 1.00
n-Butylbenzene 91.2 70 - 130 45.6 ND 50.0 5.0 1.00
n-Propyl Benzene 94.4 70 - 130 47.2 ND 50.0 5.0 1.00
Pentachloroethane 90.4 70 - 130 45.2 ND 50.0 5.0 1.00
p-Isopropyltoluene 87.9 70 - 130 44.0 ND 50.0 5.0 1.00
sec-Butyl Benzene 94.1 70 - 130 47.0 ND 50.0 5.0 1.00
Styrene 99.2 70 - 130 49.6 ND 50.0 5.0 1.00
tert-Butylbenzene 93.5 70 - 130 46.8 ND 50.0 5.0 1.00
Tetrachloroethene 85.2 70 - 130 42.6 ND 50.0 5.0 1.00
Toluene 92.5 70 - 130 46.2 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 85.6 70 - 130 42.8 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 95.5 70 - 130 47.8 ND 50.0 5.0 1.00
Trichloroethene 97.6 70 - 130 48.8 ND 50.0 5.0 1.00
Trichlorofluoromethane 84.5 70 - 130 42.2 ND 50.0 5.0 1.00
Vinyl Chloride 73.1 70 - 130 36.6 ND 50.0 4.0 1.00
Xylenes, total 99.3 70 - 130 149 ND 150 15.0 1.00
QC Sample ID: BYH0558-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0558
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Benzene 109 70 - 130 3.27 ND 3.01 0.12 1.00
Ethylbenzene 104 50 - 150 3.12 ND 3.01 0.30 1.00
Methyl tert-Butyl Ether (MTBE)92.6 50 - 150 2.78 ND 3.01 0.18 1.00
Naphthalene 108 50 - 150 3.26 ND 3.01 0.30 1.00
Toluene 104 70 - 130 3.12 ND 3.01 0.30 1.00
Xylenes, total 110 70 - 130 9.96 ND 9.02 0.90 1.00
QC Sample ID: BYH0617-MS1 QC Source Sample: 24H0986-01Batch: BYH0617
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Benzene 86.9 70 - 130 2.78 ND 3.20 0.13 1.00
Ethylbenzene 90.0 50 - 150 2.88 ND 3.20 0.32 1.00
Methyl tert-Butyl Ether (MTBE)88.0 50 - 150 2.82 ND 3.20 0.19 1.00
Naphthalene 101 50 - 150 3.22 ND 3.20 0.32 1.00
Toluene 89.5 70 - 130 2.87 ND 3.20 0.32 1.00
Xylenes, total 87.3 70 - 130 8.38 ND 9.61 0.96 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH0548-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,1,1,2-Tetrachloroethane 98.5 2.05 70 - 130 20 49.2 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 95.8 4.49 70 - 130 20 47.9 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 95.9 2.64 70 - 130 20 48.0 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 93.7 1.48 70 - 130 20 46.8 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 86.4 6.28 70 - 130 20 43.2 ND 50.0 5.0 1.00
1,1-Dichloroethane 97.4 1.73 70 - 130 20 48.7 ND 50.0 5.0 1.00
1,1-Dichloroethene 79.4 8.10 70 - 130 20 39.7 ND 50.0 5.0 1.00
1,1-Dichloropropene 83.8 4.32 70 - 130 20 41.9 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 101 6.42 70 - 130 20 50.6 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 94.1 1.61 70 - 130 20 47.0 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 103 4.58 70 - 130 20 51.4 ND 50.0 5.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 15 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH0548-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,2,4-Trimethylbenzene 92.8 3.08 70 - 130 20 46.4 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 86.9 0.345 70 - 130 20 43.4 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)96.1 2.85 70 - 130 20 48.0 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 96.7 0.727 70 - 130 20 48.4 ND 50.0 5.0 1.00
1,2-Dichloroethane 91.6 0.219 70 - 130 20 45.8 ND 50.0 5.0 1.00
1,2-Dichloropropane 90.8 3.57 70 - 130 20 45.4 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 94.2 3.44 70 - 130 20 47.1 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 99.0 0.805 70 - 130 20 49.5 ND 50.0 5.0 1.00
1,3-Dichloropropane 93.8 1.27 70 - 130 20 46.9 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 98.3 0.102 70 - 130 20 49.2 ND 50.0 5.0 1.00
2,2-Dichloropropane 78.9 10.5 70 - 130 20 39.4 ND 50.0 5.0 1.00
2-Chlorotoluene 91.2 3.34 70 - 130 20 45.6 ND 50.0 5.0 1.00
2-Hexanone 108 7.93 70 - 130 20 53.9 ND 50.0 50.0 1.00
2-Nitropropane 77.9 4.60 70 - 130 20 117 ND 150 10.0 1.00
4-Chlorotoluene 90.2 1.98 70 - 130 20 45.1 ND 50.0 5.0 1.00
Acetone 97.0 2.60 70 - 130 20 485 ND 500 100 1.00
Acrylonitrile 87.8 1.89 70 - 130 20 220 ND 250 25.0 1.00
Benzene 94.2 3.55 70 - 130 20 47.1 ND 50.0 2.0 1.00
Bromobenzene 91.8 1.62 70 - 130 20 45.9 ND 50.0 5.0 1.00
Bromochloromethane 92.5 2.03 70 - 130 20 46.2 ND 50.0 5.0 1.00
Bromodichloromethane 93.4 2.33 70 - 130 20 46.7 ND 50.0 5.0 1.00
Bromoform 89.6 0.999 70 - 130 20 44.8 ND 50.0 5.0 1.00
Bromomethane 55.2 17.1 70 - 130 20 27.6 ND 50.0 10.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Disulfide 74.8 3.42 70 - 130 20 37.4 ND 50.0 10.0 1.00
Carbon Tetrachloride 96.8 4.15 70 - 130 20 48.4 ND 50.0 5.0 1.00
Chlorobenzene 95.8 2.37 70 - 130 20 47.9 ND 50.0 5.0 1.00
Chloroethane 80.9 8.18 70 - 130 20 40.4 ND 50.0 5.0 1.00
Chloroform 86.6 2.96 70 - 130 20 43.3 ND 50.0 5.0 1.00
Chloromethane 66.3 2.83 70 - 130 20 33.2 ND 50.0 5.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
cis-1,2-Dichloroethene 84.7 4.27 70 - 130 20 42.4 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 100 0.398 70 - 130 20 50.2 ND 50.0 5.0 1.00
Cyclohexanone 109 2.36 70 - 130 20 547 ND 500 50.0 1.00
Dibromochloromethane 92.6 1.09 70 - 130 20 46.3 ND 50.0 5.0 1.00
Dibromomethane 103 0.581 70 - 130 20 51.4 ND 50.0 5.0 1.00
Dichlorodifluoromethane 53.1 6.91 70 - 130 20 26.6 ND 50.0 5.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Ethyl Acetate 89.8 0.111 70 - 130 20 89.8 ND 100 10.0 1.00
Ethyl Ether 85.5 7.65 70 - 130 20 42.8 ND 50.0 5.0 1.00
Ethylbenzene 89.8 2.31 70 - 130 20 44.9 ND 50.0 5.0 1.00
Hexachlorobutadiene 97.1 0.923 70 - 130 20 48.6 ND 50.0 5.0 1.00
Isobutanol 113 3.27 70 - 130 20 1130 ND 1000 100 1.00
Isopropylbenzene 91.7 3.22 70 - 130 20 45.8 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 94.7 13.0 70 - 130 20 47.4 ND 50.0 10.0 1.00
Methyl Isobutyl Ketone 114 14.4 70 - 130 20 57.0 ND 50.0 25.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 16 of 17
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH0548-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Methylene Chloride 86.1 2.52 70 - 130 20 43.0 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)62.8 8.29 70 - 130 20 31.4 ND 50.0 3.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Naphthalene 94.2 9.80 70 - 130 20 47.1 ND 50.0 5.0 1.00
n-Butyl Alcohol 94.7 7.81 70 - 130 20 474 ND 500 250 1.00
n-Butylbenzene 88.8 2.67 70 - 130 20 44.4 ND 50.0 5.0 1.00
n-Propyl Benzene 87.7 7.36 70 - 130 20 43.8 ND 50.0 5.0 1.00
Pentachloroethane 67.8 28.6 70 - 130 20 33.9 ND 50.0 5.0 1.00
RPD-MSOut - The RPD between MS and MSD is outside established control limits.
p-Isopropyltoluene 88.7 0.906 70 - 130 20 44.4 ND 50.0 5.0 1.00
sec-Butyl Benzene 88.2 6.47 70 - 130 20 44.1 ND 50.0 5.0 1.00
Styrene 98.6 0.607 70 - 130 20 49.3 ND 50.0 5.0 1.00
tert-Butylbenzene 92.3 1.29 70 - 130 20 46.2 ND 50.0 5.0 1.00
Tetrachloroethene 81.9 3.95 70 - 130 20 41.0 ND 50.0 5.0 1.00
Toluene 89.3 3.52 70 - 130 20 44.6 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 80.4 6.27 70 - 130 20 40.2 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 98.1 2.69 70 - 130 20 49.0 ND 50.0 5.0 1.00
Trichloroethene 94.2 3.55 70 - 130 20 47.1 ND 50.0 5.0 1.00
Trichlorofluoromethane 82.1 2.88 70 - 130 20 41.0 ND 50.0 5.0 1.00
Vinyl Chloride 69.8 4.62 70 - 130 20 34.9 ND 50.0 4.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Xylenes, total 96.4 2.93 70 - 130 20 145 ND 150 15.0 1.00
QC Sample ID: BYH0558-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0558
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Benzene 107 2.13 70 - 130 20 3.21 ND 3.01 0.12 1.00
Ethylbenzene 101 2.93 50 - 150 25 3.03 ND 3.01 0.30 1.00
Methyl tert-Butyl Ether (MTBE)95.6 3.19 50 - 150 25 2.87 ND 3.01 0.18 1.00
Naphthalene 107 1.67 50 - 150 25 3.21 ND 3.01 0.30 1.00
Toluene 101 2.54 70 - 130 20 3.04 ND 3.01 0.30 1.00
Xylenes, total 109 1.37 70 - 130 20 9.83 ND 9.02 0.90 1.00
QC Sample ID: BYH0617-MSD1 QC Source Sample: 24H0986-01Batch: BYH0617
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Benzene 84.5 2.80 70 - 130 20 2.71 ND 3.20 0.13 1.00
Ethylbenzene 84.2 6.66 50 - 150 25 2.70 ND 3.20 0.32 1.00
Methyl tert-Butyl Ether (MTBE)88.9 1.02 50 - 150 25 2.85 ND 3.20 0.19 1.00
Naphthalene 93.8 7.00 50 - 150 25 3.00 ND 3.20 0.32 1.00
Toluene 84.1 6.22 70 - 130 20 2.69 ND 3.20 0.32 1.00
Xylenes, total 90.9 4.04 70 - 130 20 8.73 ND 9.61 0.96 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 17 of 17
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H1959
Project: Former Sommers Auto Wrecking
8/22/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 22
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H1959-01 EXC-2-N
24H1959-02 EXC-2-E
24H1959-03 EXC-2-SE
24H1959-04 EXC-2-S
24H1959-05 EXC-2-W
24H1959-06 EXC-2-Floor
24H1959-07 EXC-2-W2
24H1959-08 Frac Tank
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order, with the following exceptions: Arsenic and Lead were observed above the MRL in
BYH1068-BLK1. The concentration in the method blank is less than 10% of the sample result, which is negligible
according to method criteria.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria. Batch BYH1050 had low LCS recoveries for MTBE.
It is important to note that certain flags on an individual analyte do not constitute failure of the method as a whole. EPA
methodologies recognize that it may not be possible for every compound to meet all recovery or percent difference criteria .
The batch passed required method criteria for these analytes.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
Page 2 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-N
Lab ID: 24H1959-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:40
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800092.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.089 EPA 6020A/3050B24.4Arsenic, Total
mg/kg dry B8/22/248/21/240.107 EPA 6020A/3050B668Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 3 of 22Page 3 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-E
Lab ID: 24H1959-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:45
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800088.8Total Solids
Metals
mg/kg dry B8/22/248/21/240.051 EPA 6020A/3050B21.9Arsenic, Total
mg/kg dry B8/22/248/21/240.609 EPA 6020A/3050B643Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 4 of 22Page 4 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-SE
Lab ID: 24H1959-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800086.9Total Solids
Metals
mg/kg dry B8/22/248/21/240.082 EPA 6020A/3050B22.6Arsenic, Total
mg/kg dry B8/22/248/21/240.099 EPA 6020A/3050B165Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 5 of 22Page 5 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-S
Lab ID: 24H1959-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800097.2Total Solids
Metals
mg/kg dry B8/22/248/21/240.073 EPA 6020A/3050B12.6Arsenic, Total
mg/kg dry B8/22/248/21/240.087 EPA 6020A/3050B312Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 6 of 22Page 6 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-W
Lab ID: 24H1959-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800094.4Total Solids
Metals
mg/kg dry B8/22/248/21/240.064 EPA 6020A/3050B16.8Arsenic, Total
mg/kg dry B8/22/248/21/240.077 EPA 6020A/3050B352Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 7 of 22Page 7 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-Floor
Lab ID: 24H1959-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:05
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800083.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.057 EPA 6020A/3050B16.6Arsenic, Total
mg/kg dry B8/22/248/21/240.068 EPA 6020A/3050B221Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 8 of 22Page 8 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-W2
Lab ID: 24H1959-07Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800094.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.094 EPA 6020A/3050B13.9Arsenic, Total
mg/kg dry B8/22/248/21/240.113 EPA 6020A/3050B293Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 9 of 22Page 9 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: Frac Tank
Lab ID: 24H1959-08Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/21/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 8/21/248/21/241.0 EPA 8015 CNDDiesel Range Organics
Inorganic
mg/L 8/22/248/21/246EPA 1664BNDOil & Grease (HEM)
pH Units SPH8/22/24 13:568/22/24 12:040.1 SM 4500 H-B1.9pH
mg/L 8/21/248/21/24100SM 2540 C1300Total Dissolved Solids (TDS)
mg/L 8/21/248/21/244SM 2540 D4Total Suspended Solids (TSS)
mg/L 8/22/248/21/246EPA 1664BNDTRPH (SGT-HEM)
Metals
mg/L 8/22/248/21/240.0005 EPA 6020A/3010A0.149Arsenic, Total
mg/L 8/22/248/21/240.0030 EPA 6020A/3010A0.607Barium, Total
mg/L 8/22/248/21/240.0010 EPA 6020A/3010A0.0035Chromium, Total
mg/L 8/22/248/21/240.0009 EPA 6020A/3010A0.0019Copper, Total
mg/L 8/22/248/21/240.0006 EPA 6020A/3010A0.0031Lead, Total
mg/L 8/22/248/21/240.0100 EPA 6020A/3010ANDZinc, Total
MBTEXn
mg/L 8/21/248/21/240.005 EPA 8260D/5030BNDBenzene
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L J-LOW-L8/21/248/21/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDToluene
mg/L 8/21/248/21/240.038 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/L 8/21/248/21/240.125 EPA 8260B/C 5030A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 10 of 22Page 10 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
B = Analyte is found in the associated blank as well as in the sample (CLP B-flag).
J-LOW-L = Estimated low due to low recovery of LCS
SPH = Sample submitted past method specified holding time.
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 11 of 22Page 11 of 22
Zn
,
Pb
,
As
,
B
a
,
Cr
,
Cu
ad
d
e
d
pe
r
Bl
a
k
e
Do
w
n
e
y
em
a
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.
-
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Page 12 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYH1082-DUP1 QC Source Sample: 24H1959-01Batch: BYH1082
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Solids 0.834 20 93.3 92.5 0.1 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 13 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 1664B
QC Sample ID: BYH1063-BLK1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)ND 5 1.00
TRPH (SGT-HEM)ND 5 1.00
LCS - EPA 1664B
QC Sample ID: BYH1063-BS1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)87.8 78 - 114 35 40.0 5 1.00
TRPH (SGT-HEM)88.5 64 - 132 18 20.0 5 1.00
LCS Dup - EPA 1664B
QC Sample ID: BYH1063-BSD1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)83.8 4.66 78 - 114 18 34 40.0 5 1.00
TRPH (SGT-HEM)84.0 5.22 64 - 132 34 17 20.0 5 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 14 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6020A
QC Sample ID: BYH1068-BLK1 Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 0.106 0.050 1.00
QB-01 - The method blank contains analyte at a concentration above the MRL; however, concentration is less than 10% of the
sample result, which is negligible according to method criteria.
Lead, Total 0.110 0.060 1.00
QB-01 - The method blank contains analyte at a concentration above the MRL; however, concentration is less than 10% of the
sample result, which is negligible according to method criteria.
QC Sample ID: BYH1069-BLK1 Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total ND 0.0005 1.00
Barium, Total ND 0.0030 1.00
Chromium, Total ND 0.0010 1.00
Copper, Total ND 0.0009 1.00
Lead, Total ND 0.0006 1.00
Zinc, Total ND 0.0100 1.00
LCS - EPA 6020A
QC Sample ID: BYH1069-BS2 Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 99.0 85 - 115 0.396 0.400 0.0050 1.00
Barium, Total 99.9 85 - 115 0.400 0.400 0.0300 1.00
Chromium, Total 97.1 85 - 115 0.388 0.400 0.0100 1.00
Copper, Total 98.7 85 - 115 0.395 0.400 0.0090 1.00
Lead, Total 97.2 85 - 115 0.389 0.400 0.0060 1.00
Zinc, Total 108 85 - 115 0.434 0.400 0.100 1.00
Matrix Spike - EPA 6020A
QC Sample ID: BYH1068-MS2 QC Source Sample: 24H1959-01Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 17.7 75 - 125 25.5 24.4 6.10 0.076 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 298 75 - 125 686 668 6.10 0.092 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1069-MS1 QC Source Sample: 24H1959-08Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 89.8 70 - 130 0.221 0.149 0.0800 0.0005 1.00
Barium, Total 102 70 - 130 0.689 0.607 0.0800 0.0030 1.00
Chromium, Total 92.8 70 - 130 0.078 0.004 0.0800 0.0010 1.00
Copper, Total 81.4 70 - 130 0.067 0.002 0.0800 0.0009 1.00
Lead, Total 90.5 70 - 130 0.076 0.003 0.0800 0.0006 1.00
Zinc, Total 75.3 70 - 130 0.069 0.009 0.0800 0.0100 1.00
Matrix Spike Dup - EPA 6020A
QC Sample ID: BYH1068-MSD2 QC Source Sample: 24H1959-01Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 67.3 10.8 75 - 125 20 28.4 24.4 5.92 0.074 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 366 0.503 75 - 125 20 689 668 5.92 0.089 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
CtF WO#: 24H1959
www.ChemtechFord.com Page 15 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 6020A (cont.)
QC Sample ID: BYH1069-MSD1 QC Source Sample: 24H1959-08Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 93.3 1.26 70 - 130 20 0.224 0.149 0.0800 0.0005 1.00
Barium, Total 115 1.41 70 - 130 20 0.699 0.607 0.0800 0.0030 1.00
Chromium, Total 96.6 3.83 70 - 130 20 0.081 0.004 0.0800 0.0010 1.00
Copper, Total 84.3 3.37 70 - 130 20 0.069 0.002 0.0800 0.0009 1.00
Lead, Total 93.4 3.00 70 - 130 20 0.078 0.003 0.0800 0.0006 1.00
Zinc, Total 78.1 3.19 70 - 130 20 0.071 0.009 0.0800 0.0100 1.00
Reference - EPA 6020A
QC Sample ID: BYH1068-SRM1 Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 106 77.78 - 144.3 70.5 66.6 0.099 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 85.7 63.16 - 121.4 212 247 0.119 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
CtF WO#: 24H1959
www.ChemtechFord.com Page 16 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH1124-BLK1 Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics ND 1.0 1.00
LCS - EPA 8015 C
QC Sample ID: BYH1124-BS1 Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 109 50 - 150 44 40.0 1.0 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH1124-MS1 QC Source Sample: 24H1959-08Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 100 50 - 150 40 ND 40.0 1.0 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH1124-MSD1 QC Source Sample: 24H1959-08Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 108 7.11 50 - 150 20 43 ND 40.0 1.0 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 17 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH1050-BLK1 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH1050-BLK2 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene ND 0.100 1.00
Ethylbenzene ND 0.250 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.150 1.00
Naphthalene ND 0.250 1.00
Toluene ND 0.250 1.00
Xylenes, total ND 0.750 1.00
LCS - EPA 8260D
QC Sample ID: BYH1050-BS1 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 96.6 70 - 130 0.010 0.0100 0.0004 1.00
Ethylbenzene 105 70 - 130 0.011 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)50.3 70 - 130 0.005 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 124 70 - 130 0.012 0.0100 0.001 1.00
Toluene 96.6 70 - 130 0.010 0.0100 0.001 1.00
Xylenes, total 110 70 - 130 0.033 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH1050-MS2 QC Source Sample: 24H1959-08Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 88.9 70 - 130 0.111 ND 0.125 0.005 1.00
Ethylbenzene 89.2 70 - 130 0.112 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)62.7 70 - 130 0.078 ND 0.125 0.008 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Naphthalene 95.3 70 - 130 0.119 ND 0.125 0.012 1.00
Toluene 88.6 70 - 130 0.111 ND 0.125 0.012 1.00
Xylenes, total 94.9 70 - 130 0.356 ND 0.375 0.038 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH1050-MSD2 QC Source Sample: 24H1959-08Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 87.4 1.70 70 - 130 20 0.109 ND 0.125 0.005 1.00
Ethylbenzene 90.1 1.00 70 - 130 25 0.113 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)54.8 13.4 70 - 130 25 0.068 ND 0.125 0.008 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Naphthalene 92.0 3.52 70 - 130 25 0.115 ND 0.125 0.012 1.00
Toluene 87.2 1.59 70 - 130 20 0.109 ND 0.125 0.012 1.00
Xylenes, total 93.3 1.70 70 - 130 20 0.350 ND 0.375 0.038 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 18 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - SM 2540 C
QC Sample ID: BYH1067-BLK1 Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)ND 10 1.00
Duplicate - SM 2540 C
QC Sample ID: BYH1067-DUP1 QC Source Sample: 24H1959-08Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)0 10 1300 1300 100 1.00
LCS - SM 2540 C
QC Sample ID: BYH1067-BS1 Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)97 90 - 110 388 400 20 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 19 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
QC Sample ID: BYH1081-BLK1 Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)ND 1 1.00
QC Sample ID: BYH1081-DUP1 QC Source Sample: 24H1959-08Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)11.8 20 3 4 4 1.00
QC Sample ID: BYH1081-DUP2 QC Source Sample: XXXXXXX-XXBatch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)20.7 20 5 6 4 1.00
QM-020 - The RPD and/or percent recovery for this QC spike sample cannot be accurately calculated due to the low
concentration of analyte inherent in the sample. The batch was accepted based on acceptable LCS recovery.
QC Sample ID: BYH1081-SRM1 Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)91.0 80 - 120 91 100 10 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 20 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - SM 4500 H-B
QC Sample ID: BYH1104-DUP1 QC Source Sample: 24H1959-08Batch: BYH1104
Date Prepared: 08/22/2024 Date Analyzed: 08/22/2024
pH 1.60 3 1.9 1.9 0.1 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 21 of 22
Surrogates Report for Work Order (WO) - 24H1959
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH1124-BLK1 Bromofluorobenzene 78.4 50 BYH1124 1.001503.14 4.00
BYH1124-BLK1 Capric Acid 0 BYH1124 1.0010.00 10.0
LCS - EPA 8015 C
BYH1124-BS1 Bromofluorobenzene 80.1 50 BYH1124 1.001503.21 4.00
BYH1124-BS1 Capric Acid 0 BYH1124 1.0010.00 10.0
Matrix Spike - EPA 8015 C
BYH1124-MS1 Bromofluorobenzene 126 50 BYH1124 1.001505.06 4.00
BYH1124-MS1 Capric Acid 0 BYH1124 1.0010.00 10.0
Matrix Spike Dup - EPA 8015 C
BYH1124-MSD1 Bromofluorobenzene 125 50 BYH1124 1.001505.01 4.00
BYH1124-MSD1 Capric Acid 0 BYH1124 1.0010.00 10.0
Blank - EPA 8260D
BYH1050-BLK2 Toluene-d8 102 83.3 BYH1050 1.001222.55 2.50
BYH1050-BLK1 Toluene-d8 102 83.3 BYH1050 1.001220.0102 0.0100
LCS - EPA 8260D
BYH1050-BS1 Toluene-d8 101 83.3 BYH1050 1.001220.0101 0.0100
Matrix Spike - EPA 8260D
BYH1050-MS2 Toluene-d8 104 83.3 BYH1050 1.001220.130 0.125
BYH1050-MS1 Toluene-d8 102 83.3 BYH1050 1.001222.54 2.50
Matrix Spike Dup - EPA 8260D
BYH1050-MSD2 Toluene-d8 103 83.3 BYH1050 1.001220.129 0.125
BYH1050-MSD1 Toluene-d8 103 83.3 BYH1050 1.001222.56 2.50
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24H1959-08 Capric Acid 0.00 0 110.0
24H1959-08 Bromofluorobenzene 4.94 123 50 1504.00
MBTEXN-GRO
24H1959-08 Toluene-d8 0.129 103 83.3 1220.125
CtF WO#: 24H1959
www.ChemtechFord.com Page 22 of 22
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H2214
Project: Former Sommers Auto Wrecking
8/27/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 31
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H2214-01 EXC-3-N
24H2214-02 EXC-3-E
24H2214-03 EXC-3-S
24H2214-04 EXC-3-W
24H2214-05 EXC-3-Floor
24H2214-06 EXC-3-Floor 10
24H2214-07 Equipment Blank
24H2214-08 EXC-4-NE2
24H2214-09 EXC-1-Comp
24H2214-10 Trip Blank
24H2214-11 Frack Tank 2
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria, except as noted by qualifying flags. Batches
BYH1199 and BYH1214 for method 8260D and LCS recoveries outside of the control limits for several compounds. It is
important to note that certain flags on an individual analyte do not constitute failure of the method as a whole. EPA
methodologies recognize that it may not be possible for every compound to meet all recovery or percent difference criteria .
The batch passed required method criteria for these analytes.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
Page 2 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-N
Lab ID: 24H2214-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800078.6Total Solids
Metals
mg/kg dry 8/26/248/23/240.047 EPA 6020A/3050B15.9Arsenic, Total
mg/kg dry 8/26/248/23/240.056 EPA 6020A/3050B121Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 3 of 30Page 3 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-E
Lab ID: 24H2214-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:05
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800082.0Total Solids
Metals
mg/kg dry 8/26/248/23/240.043 EPA 6020A/3050B16.2Arsenic, Total
mg/kg dry 8/26/248/23/240.102 EPA 6020A/3050B183Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 4 of 30Page 4 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-S
Lab ID: 24H2214-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800092.3Total Solids
Metals
mg/kg dry 8/26/248/23/240.085 EPA 6020A/3050B21.4Arsenic, Total
mg/kg dry 8/26/248/23/240.511 EPA 6020A/3050B766Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 5 of 30Page 5 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-W
Lab ID: 24H2214-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:15
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800095.5Total Solids
Metals
mg/kg dry 8/26/248/23/240.082 EPA 6020A/3050B15.5Arsenic, Total
mg/kg dry 8/26/248/23/240.098 EPA 6020A/3050B120Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 6 of 30Page 6 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-Floor
Lab ID: 24H2214-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:20
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800086.6Total Solids
Metals
mg/kg dry 8/26/248/23/240.084 EPA 6020A/3050B11.0Arsenic, Total
mg/kg dry 8/26/248/23/240.101 EPA 6020A/3050B47.5Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 7 of 30Page 7 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-Floor 10
Lab ID: 24H2214-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:25
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800084.7Total Solids
Metals
mg/kg dry 8/26/248/23/240.107 EPA 6020A/3050B11.6Arsenic, Total
mg/kg dry 8/26/248/23/240.128 EPA 6020A/3050B107Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 8 of 30Page 8 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Equipment Blank
Lab ID: 24H2214-07Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:45
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Metals
mg/L 8/27/248/26/240.0005 EPA 6020A/3010ANDArsenic, Total
mg/L 8/27/248/26/240.0006 EPA 6020A/3010ANDLead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 9 of 30Page 9 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-NE2
Lab ID: 24H2214-08Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 13:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/23/248/23/2461EPA 8015 C296Diesel Range Organics
Inorganic
%8/23/248/23/240.1 CTF800082.5Total Solids
MBTEXn
mg/kg dry 8/23/248/23/240.12 EPA 8260D/5030BNDBenzene
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDEthylbenzene
mg/kg dry J-LOW-L8/23/248/23/240.18 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDNaphthalene
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDToluene
mg/kg dry 8/23/248/23/240.91 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/kg dry 8/23/248/23/243.03 EPA 8260B/C 5035A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 10 of 30Page 10 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-Comp
Lab ID: 24H2214-09Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 15:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800096.9Total Solids
Metals
mg/kg dry 8/26/248/23/240.085 EPA 6020A/3050B10.3Arsenic, Total
mg/kg dry 8/26/248/23/240.103 EPA 6020A/3050B290Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 11 of 30Page 11 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24H2214-10Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 12:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 8/23/248/23/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L J-LOW-L8/23/248/23/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 8/23/248/23/2420.0 EPA 8260D/5030BNDAcetone
ug/L 8/23/248/23/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 8/23/248/23/240.4 EPA 8260D/5030BNDBenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030B2.4Bromodichloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromoform
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDBromomethane
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 12 of 30Page 12 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24H2214-10Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 12:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030B8.0Chloroform
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L J-LOW-C8/23/248/23/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDibromochloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDibromomethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 8/23/248/23/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 8/23/248/23/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L 8/23/248/23/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDNaphthalene
ug/L 8/23/248/23/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDStyrene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDToluene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 8/23/248/23/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 8/23/248/23/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 13 of 30Page 13 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Frack Tank 2
Lab ID: 24H2214-11Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/23/24 10:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
mg/L 8/23/248/23/2420SM 2540 C1030Total Dissolved Solids (TDS)
Metals
mg/L 8/27/248/26/240.0005 EPA 6020A/3010A0.0870Arsenic, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 14 of 30Page 14 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-C = Estimated low due to low recovery of CCV
J-LOW-L = Estimated low due to low recovery of LCS
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 15 of 30Page 15 of 31
Page 16 of 31
Page 17 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYH1184-DUP1 QC Source Sample: XXXXXXX-XXBatch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.158 20 81.5 81.6 0.1 1.00
QC Sample ID: BYH1184-DUP2 QC Source Sample: 24H2214-01Batch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.625 20 79.1 78.6 0.1 1.00
QC Sample ID: BYH1184-DUP3 QC Source Sample: 24H2214-08Batch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.483 20 82.1 82.5 0.1 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 18 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6020A
QC Sample ID: BYH1194-BLK1 Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total ND 0.050 1.00
Lead, Total ND 0.060 1.00
QC Sample ID: BYH1238-BLK1 Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total ND 0.0005 1.00
Lead, Total ND 0.0006 1.00
LCS - EPA 6020A
QC Sample ID: BYH1238-BS1 Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 96.1 85 - 115 0.038 0.0400 0.0005 1.00
Lead, Total 94.0 85 - 115 0.038 0.0400 0.0006 1.00
Matrix Spike - EPA 6020A
QC Sample ID: BYH1194-MS1 QC Source Sample: 24H2214-01Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 141 75 - 125 23.6 15.9 5.49 0.069 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Lead, Total 844 75 - 125 168 121 5.49 0.082 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1238-MS1 QC Source Sample: 24H2214-11Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 90.4 70 - 130 0.123 0.087 0.0400 0.0005 1.00
Lead, Total 88.0 70 - 130 0.052 0.016 0.0400 0.0006 1.00
Matrix Spike Dup - EPA 6020A
QC Sample ID: BYH1194-MSD1 QC Source Sample: 24H2214-01Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 121 5.90 75 - 125 20 22.3 15.9 5.30 0.066 1.00
Lead, Total 899 0.791 75 - 125 20 169 121 5.30 0.079 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1238-MSD1 QC Source Sample: 24H2214-11Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 91.9 0.497 70 - 130 20 0.124 0.087 0.0400 0.0005 1.00
Lead, Total 86.6 1.13 70 - 130 20 0.051 0.016 0.0400 0.0006 1.00
Reference - EPA 6020A
QC Sample ID: BYH1194-SRM1 Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 108 77.78 - 144.3 72.0 66.6 0.177 1.00
Lead, Total 86.2 63.16 - 121.4 213 247 0.213 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 19 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH1227-BLK1 Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics ND 50 1.00
LCS - EPA 8015 C
QC Sample ID: BYH1227-BS1 Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 106 50 - 150 2120 2000 50 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH1227-MS1 QC Source Sample: 24H2214-08Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 105 50 - 150 2840 296 2430 61 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH1227-MSD1 QC Source Sample: 24H2214-08Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 94.3 9.56 50 - 150 20 2580 296 2430 61 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 20 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH1199-BLK1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.4 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 1.0 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 21 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYH1199-BLK1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 1.0 1.00
n-Butyl Alcohol ND 50.0 1.00
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 1.0 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 3.0 1.00
QC Sample ID: BYH1214-BLK1 Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 111 70 - 130 11.1 10.0 1.0 1.00
1,1,1-Trichloroethane 117 70 - 130 11.7 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 106 70 - 130 10.6 10.0 1.0 1.00
1,1,2-Trichloroethane 102 70 - 130 10.2 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 120 70 - 130 12.0 10.0 1.0 1.00
1,1-Dichloroethane 120 70 - 130 12.0 10.0 1.0 1.00
1,1-Dichloroethene 107 70 - 130 10.7 10.0 1.0 1.00
1,1-Dichloropropene 111 70 - 130 11.1 10.0 1.0 1.00
1,2,3-Trichlorobenzene 120 70 - 130 12.0 10.0 1.0 1.00
1,2,3-Trichloropropane 115 70 - 130 11.5 10.0 1.0 1.00
1,2,4-Trichlorobenzene 110 70 - 130 11.0 10.0 1.0 1.00
1,2,4-Trimethylbenzene 110 70 - 130 11.0 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 110 70 - 130 11.0 10.0 1.0 1.00
1,2-Dibromoethane (EDB)106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dichlorobenzene 111 70 - 130 11.1 10.0 1.0 1.00
1,2-Dichloroethane 106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dichloropropane 106 70 - 130 10.6 10.0 1.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 22 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,3,5-Trimethylbenzene 109 70 - 130 10.9 10.0 1.0 1.00
1,3-Dichlorobenzene 117 70 - 130 11.7 10.0 1.0 1.00
1,3-Dichloropropane 114 70 - 130 11.4 10.0 1.0 1.00
1,4-Dichlorobenzene 106 70 - 130 10.6 10.0 1.0 1.00
2,2-Dichloropropane 112 70 - 130 11.2 10.0 1.0 1.00
2-Chlorotoluene 114 70 - 130 11.4 10.0 1.0 1.00
2-Hexanone 132 70 - 130 13.2 10.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
2-Nitropropane 49.2 70 - 130 14.8 30.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
4-Chlorotoluene 114 70 - 130 11.4 10.0 1.0 1.00
Acetone 95.5 70 - 130 95.5 100 20.0 1.00
Acrylonitrile 108 70 - 130 53.9 50.0 5.0 1.00
Benzene 112 70 - 130 11.2 10.0 0.4 1.00
Bromobenzene 109 70 - 130 10.9 10.0 1.0 1.00
Bromochloromethane 116 70 - 130 11.6 10.0 1.0 1.00
Bromodichloromethane 98.9 70 - 130 9.89 10.0 1.0 1.00
Bromoform 109 70 - 130 10.9 10.0 1.0 1.00
Bromomethane 176 70 - 130 17.6 10.0 2.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 139 70 - 130 13.9 10.0 2.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Tetrachloride 114 70 - 130 11.4 10.0 1.0 1.00
Chlorobenzene 109 70 - 130 10.9 10.0 1.0 1.00
Chloroethane 124 70 - 130 12.4 10.0 1.0 1.00
Chloroform 108 70 - 130 10.8 10.0 1.0 1.00
Chloromethane 146 70 - 130 14.6 10.0 1.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
cis-1,2-Dichloroethene 113 70 - 130 11.3 10.0 1.0 1.00
cis-1,3-Dichloropropene 108 70 - 130 10.8 10.0 1.0 1.00
Cyclohexanone 34.5 70 - 130 34.5 100 10.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Dibromochloromethane 115 70 - 130 11.5 10.0 1.0 1.00
Dibromomethane 112 70 - 130 11.2 10.0 1.0 1.00
Dichlorodifluoromethane 143 70 - 130 14.3 10.0 1.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Acetate 102 70 - 130 20.4 20.0 2.0 1.00
Ethyl Ether 108 70 - 130 10.8 10.0 1.0 1.00
Ethylbenzene 111 70 - 130 11.1 10.0 1.0 1.00
Hexachlorobutadiene 117 70 - 130 11.7 10.0 1.0 1.00
Isobutanol 174 70 - 130 348 200 20.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 104 70 - 130 10.4 10.0 1.0 1.00
Methyl Ethyl Ketone 151 70 - 130 15.1 10.0 2.0 1.00
J-High-L - Analyte estimated high based on LCS recovery
Methyl Isobutyl Ketone 91.6 70 - 130 9.16 10.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 23 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Methylene Chloride 104 70 - 130 10.4 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)182 70 - 130 18.2 10.0 0.6 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 112 70 - 130 11.2 10.0 1.0 1.00
n-Butyl Alcohol 77.4 70 - 130 77.4 100 50.0 1.00
n-Butylbenzene 111 70 - 130 11.1 10.0 1.0 1.00
n-Propyl Benzene 110 70 - 130 11.0 10.0 1.0 1.00
Pentachloroethane 94.1 70 - 130 9.41 10.0 1.0 1.00
p-Isopropyltoluene 115 70 - 130 11.5 10.0 1.0 1.00
sec-Butyl Benzene 112 70 - 130 11.2 10.0 1.0 1.00
Styrene 108 70 - 130 10.8 10.0 1.0 1.00
tert-Butylbenzene 107 70 - 130 10.7 10.0 1.0 1.00
Tetrachloroethene 118 70 - 130 11.8 10.0 1.0 1.00
Toluene 100 70 - 130 10.0 10.0 1.0 1.00
trans-1,2-Dichloroethene 116 70 - 130 11.6 10.0 1.0 1.00
trans-1,3-Dichloropropene 107 70 - 130 10.7 10.0 1.0 1.00
Trichloroethene 120 70 - 130 12.0 10.0 1.0 1.00
Trichlorofluoromethane 118 70 - 130 11.8 10.0 1.0 1.00
Vinyl Chloride 162 70 - 130 16.2 10.0 0.8 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 107 70 - 130 32.2 30.0 3.0 1.00
QC Sample ID: BYH1214-BS1 Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 115 70 - 130 0.01 0.0100 0.0004 1.00
Ethylbenzene 118 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)52.1 70 - 130 0.005 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 105 70 - 130 0.01 0.0100 0.001 1.00
Toluene 112 70 - 130 0.01 0.0100 0.001 1.00
Xylenes, total 121 70 - 130 0.04 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 108 70 - 130 54.0 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 106 70 - 130 53.2 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 106 70 - 130 52.8 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 106 70 - 130 53.2 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 112 70 - 130 56.2 ND 50.0 5.0 1.00
1,1-Dichloroethane 111 70 - 130 55.3 ND 50.0 5.0 1.00
1,1-Dichloroethene 97.5 70 - 130 48.8 ND 50.0 5.0 1.00
1,1-Dichloropropene 104 70 - 130 52.2 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 110 70 - 130 55.1 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 117 70 - 130 58.6 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 99.3 70 - 130 49.6 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 106 70 - 130 53.0 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 100 70 - 130 50.2 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)110 70 - 130 54.9 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 107 70 - 130 53.4 ND 50.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 24 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,2-Dichloroethane 107 70 - 130 53.4 ND 50.0 5.0 1.00
1,2-Dichloropropane 102 70 - 130 50.8 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 99.0 70 - 130 49.5 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 109 70 - 130 54.6 ND 50.0 5.0 1.00
1,3-Dichloropropane 116 70 - 130 58.2 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 103 70 - 130 51.6 ND 50.0 5.0 1.00
2,2-Dichloropropane 99.4 70 - 130 49.7 ND 50.0 5.0 1.00
2-Chlorotoluene 107 70 - 130 53.3 ND 50.0 5.0 1.00
2-Hexanone 132 70 - 130 65.8 ND 50.0 50.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
2-Nitropropane 53.4 70 - 130 80.1 ND 150 10.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
4-Chlorotoluene 105 70 - 130 52.4 ND 50.0 5.0 1.00
Acetone 89.6 70 - 130 448 ND 500 100 1.00
Acrylonitrile 109 70 - 130 271 ND 250 25.0 1.00
Benzene 108 70 - 130 54.0 ND 50.0 2.0 1.00
Bromobenzene 102 70 - 130 51.2 ND 50.0 5.0 1.00
Bromochloromethane 114 70 - 130 57.0 ND 50.0 5.0 1.00
Bromodichloromethane 98.8 70 - 130 49.4 ND 50.0 5.0 1.00
Bromoform 115 70 - 130 57.3 ND 50.0 5.0 1.00
Bromomethane 167 70 - 130 83.7 ND 50.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 128 70 - 130 64.1 ND 50.0 10.0 1.00
Carbon Tetrachloride 106 70 - 130 53.0 ND 50.0 5.0 1.00
Chlorobenzene 105 70 - 130 52.7 ND 50.0 5.0 1.00
Chloroethane 116 70 - 130 58.0 ND 50.0 5.0 1.00
Chloroform 102 70 - 130 51.2 ND 50.0 5.0 1.00
Chloromethane 135 70 - 130 67.4 ND 50.0 5.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
cis-1,2-Dichloroethene 105 70 - 130 52.7 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 98.7 70 - 130 49.4 ND 50.0 5.0 1.00
Cyclohexanone 25.2 70 - 130 126 ND 500 50.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Dibromochloromethane 113 70 - 130 56.4 ND 50.0 5.0 1.00
Dibromomethane 112 70 - 130 56.1 ND 50.0 5.0 1.00
Dichlorodifluoromethane 129 70 - 130 64.5 ND 50.0 5.0 1.00
Ethyl Acetate 107 70 - 130 107 ND 100 10.0 1.00
Ethyl Ether 103 70 - 130 51.6 ND 50.0 5.0 1.00
Ethylbenzene 106 70 - 130 53.2 ND 50.0 5.0 1.00
Hexachlorobutadiene 107 70 - 130 53.5 ND 50.0 5.0 1.00
Isobutanol 147 70 - 130 1470 ND 1000 100 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 99.2 70 - 130 49.6 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 159 70 - 130 79.4 ND 50.0 10.0 1.00
MS-High - Estimated high due to Matrix Spike recovery.
Methyl Isobutyl Ketone 112 70 - 130 55.8 ND 50.0 25.0 1.00
Methylene Chloride 97.1 70 - 130 48.6 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)192 70 - 130 95.9 ND 50.0 3.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 25 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 104 70 - 130 51.8 ND 50.0 5.0 1.00
n-Butyl Alcohol 84.5 70 - 130 422 ND 500 250 1.00
n-Butylbenzene 98.4 70 - 130 49.2 ND 50.0 5.0 1.00
n-Propyl Benzene 103 70 - 130 51.6 ND 50.0 5.0 1.00
Pentachloroethane 93.7 70 - 130 46.8 ND 50.0 5.0 1.00
p-Isopropyltoluene 103 70 - 130 51.7 ND 50.0 5.0 1.00
sec-Butyl Benzene 102 70 - 130 50.8 ND 50.0 5.0 1.00
Styrene 105 70 - 130 52.3 ND 50.0 5.0 1.00
tert-Butylbenzene 102 70 - 130 50.8 ND 50.0 5.0 1.00
Tetrachloroethene 106 70 - 130 53.2 ND 50.0 5.0 1.00
Toluene 97.9 70 - 130 49.0 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 107 70 - 130 53.5 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 104 70 - 130 52.0 ND 50.0 5.0 1.00
Trichloroethene 115 70 - 130 57.4 ND 50.0 5.0 1.00
Trichlorofluoromethane 110 70 - 130 55.0 ND 50.0 5.0 1.00
Vinyl Chloride 150 70 - 130 75.2 ND 50.0 4.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 102 70 - 130 154 ND 150 15.0 1.00
QC Sample ID: BYH1214-MS1 QC Source Sample: 24H2214-08Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 101 70 - 130 3.06 ND 3.03 0.12 1.00
Ethylbenzene 102 50 - 150 3.10 ND 3.03 0.30 1.00
Methyl tert-Butyl Ether (MTBE)55.4 50 - 150 1.68 ND 3.03 0.18 1.00
Naphthalene 102 50 - 150 3.11 ND 3.03 0.30 1.00
Toluene 98.3 70 - 130 2.98 ND 3.03 0.30 1.00
Xylenes, total 107 70 - 130 9.72 ND 9.10 0.91 1.00
QC Sample ID: BYH1214-MS2 QC Source Sample: XXXXXXX-XXBatch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 103 70 - 130 0.28 ND 0.271 0.01 1.00
Ethylbenzene 101 50 - 150 0.27 ND 0.271 0.03 1.00
Methyl tert-Butyl Ether (MTBE)55.6 50 - 150 0.15 ND 0.271 0.02 1.00
Naphthalene 110 50 - 150 0.30 ND 0.271 0.03 1.00
Toluene 100 70 - 130 0.27 ND 0.271 0.03 1.00
Xylenes, total 106 70 - 130 0.86 ND 0.813 0.08 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 108 0.278 70 - 130 20 53.9 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 101 5.41 70 - 130 20 50.4 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 106 0.754 70 - 130 20 53.2 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 102 4.12 70 - 130 20 51.0 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 106 5.86 70 - 130 20 53.0 ND 50.0 5.0 1.00
1,1-Dichloroethane 104 6.34 70 - 130 20 51.9 ND 50.0 5.0 1.00
1,1-Dichloroethene 89.7 8.33 70 - 130 20 44.8 ND 50.0 5.0 1.00
1,1-Dichloropropene 99.2 5.20 70 - 130 20 49.6 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 115 4.26 70 - 130 20 57.5 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 117 0.0854 70 - 130 20 58.6 ND 50.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 26 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,2,4-Trichlorobenzene 105 5.68 70 - 130 20 52.6 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 101 5.02 70 - 130 20 50.4 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 107 6.64 70 - 130 20 53.6 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)111 1.09 70 - 130 20 55.5 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 104 2.56 70 - 130 20 52.1 ND 50.0 5.0 1.00
1,2-Dichloroethane 106 0.658 70 - 130 20 53.0 ND 50.0 5.0 1.00
1,2-Dichloropropane 98.5 3.00 70 - 130 20 49.2 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 96.9 2.14 70 - 130 20 48.4 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 99.4 9.49 70 - 130 20 49.7 ND 50.0 5.0 1.00
1,3-Dichloropropane 112 3.58 70 - 130 20 56.2 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 118 13.4 70 - 130 20 59.0 ND 50.0 5.0 1.00
2,2-Dichloropropane 99.0 0.403 70 - 130 20 49.5 ND 50.0 5.0 1.00
2-Chlorotoluene 90.1 16.8 70 - 130 20 45.0 ND 50.0 5.0 1.00
2-Hexanone 122 7.89 70 - 130 20 60.8 ND 50.0 50.0 1.00
2-Nitropropane 60.0 11.6 70 - 130 20 90.0 ND 150 10.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
4-Chlorotoluene 104 0.767 70 - 130 20 52.0 ND 50.0 5.0 1.00
Acetone 89.4 0.268 70 - 130 20 447 ND 500 100 1.00
Acrylonitrile 108 0.647 70 - 130 20 270 ND 250 25.0 1.00
Benzene 103 4.74 70 - 130 20 51.4 ND 50.0 2.0 1.00
Bromobenzene 99.1 3.18 70 - 130 20 49.6 ND 50.0 5.0 1.00
Bromochloromethane 112 1.86 70 - 130 20 56.0 ND 50.0 5.0 1.00
Bromodichloromethane 96.4 2.46 70 - 130 20 48.2 ND 50.0 5.0 1.00
Bromoform 110 4.19 70 - 130 20 55.0 ND 50.0 5.0 1.00
Bromomethane 171 2.30 70 - 130 20 85.6 ND 50.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 122 5.28 70 - 130 20 60.8 ND 50.0 10.0 1.00
Carbon Tetrachloride 101 4.73 70 - 130 20 50.6 ND 50.0 5.0 1.00
Chlorobenzene 105 0.285 70 - 130 20 52.6 ND 50.0 5.0 1.00
Chloroethane 107 8.25 70 - 130 20 53.4 ND 50.0 5.0 1.00
Chloroform 96.8 5.62 70 - 130 20 48.4 ND 50.0 5.0 1.00
Chloromethane 125 7.47 70 - 130 20 62.5 ND 50.0 5.0 1.00
cis-1,2-Dichloroethene 99.0 6.26 70 - 130 20 49.5 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 100 1.51 70 - 130 20 50.1 ND 50.0 5.0 1.00
Cyclohexanone 21.2 17.3 70 - 130 20 106 ND 500 50.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Dibromochloromethane 114 0.883 70 - 130 20 56.8 ND 50.0 5.0 1.00
Dibromomethane 110 2.34 70 - 130 20 54.8 ND 50.0 5.0 1.00
Dichlorodifluoromethane 116 10.4 70 - 130 20 58.2 ND 50.0 5.0 1.00
Ethyl Acetate 104 2.46 70 - 130 20 104 ND 100 10.0 1.00
Ethyl Ether 103 0.486 70 - 130 20 51.4 ND 50.0 5.0 1.00
Ethylbenzene 101 5.31 70 - 130 20 50.4 ND 50.0 5.0 1.00
Hexachlorobutadiene 104 2.94 70 - 130 20 52.0 ND 50.0 5.0 1.00
Isobutanol 141 4.22 70 - 130 20 1410 ND 1000 100 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 93.4 6.02 70 - 130 20 46.7 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 142 11.2 70 - 130 20 70.9 ND 50.0 10.0 1.00
MS-High - Estimated high due to Matrix Spike recovery.
Methyl Isobutyl Ketone 104 7.25 70 - 130 20 51.8 ND 50.0 25.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 27 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Methylene Chloride 93.9 3.35 70 - 130 20 47.0 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)202 4.93 70 - 130 20 101 ND 50.0 3.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 112 7.62 70 - 130 20 55.8 ND 50.0 5.0 1.00
n-Butyl Alcohol 86.4 2.32 70 - 130 20 432 ND 500 250 1.00
n-Butylbenzene 98.2 0.203 70 - 130 20 49.1 ND 50.0 5.0 1.00
n-Propyl Benzene 98.1 4.97 70 - 130 20 49.0 ND 50.0 5.0 1.00
Pentachloroethane 88.9 5.26 70 - 130 20 44.4 ND 50.0 5.0 1.00
p-Isopropyltoluene 93.0 10.6 70 - 130 20 46.5 ND 50.0 5.0 1.00
sec-Butyl Benzene 97.6 3.92 70 - 130 20 48.8 ND 50.0 5.0 1.00
Styrene 103 1.44 70 - 130 20 51.6 ND 50.0 5.0 1.00
tert-Butylbenzene 99.5 2.09 70 - 130 20 49.8 ND 50.0 5.0 1.00
Tetrachloroethene 99.3 6.81 70 - 130 20 49.6 ND 50.0 5.0 1.00
Toluene 95.8 2.17 70 - 130 20 47.9 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 99.2 7.57 70 - 130 20 49.6 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 104 0.288 70 - 130 20 52.2 ND 50.0 5.0 1.00
Trichloroethene 108 6.65 70 - 130 20 53.8 ND 50.0 5.0 1.00
Trichlorofluoromethane 98.8 10.7 70 - 130 20 49.4 ND 50.0 5.0 1.00
Vinyl Chloride 140 6.81 70 - 130 20 70.2 ND 50.0 4.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 100 2.27 70 - 130 20 150 ND 150 15.0 1.00
QC Sample ID: BYH1214-MSD1 QC Source Sample: 24H2214-08Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 97.6 3.23 70 - 130 20 2.96 ND 3.03 0.12 1.00
Ethylbenzene 96.8 5.52 50 - 150 25 2.93 ND 3.03 0.30 1.00
Methyl tert-Butyl Ether (MTBE)59.1 6.46 50 - 150 25 1.79 ND 3.03 0.18 1.00
Naphthalene 96.6 5.93 50 - 150 25 2.93 ND 3.03 0.30 1.00
Toluene 95.0 3.41 70 - 130 20 2.88 ND 3.03 0.30 1.00
Xylenes, total 101 5.18 70 - 130 20 9.23 ND 9.10 0.91 1.00
QC Sample ID: BYH1214-MSD2 QC Source Sample: XXXXXXX-XXBatch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 102 3.89 70 - 130 20 0.27 ND 0.264 0.01 1.00
Ethylbenzene 98.7 4.63 50 - 150 25 0.26 ND 0.264 0.03 1.00
Methyl tert-Butyl Ether (MTBE)57.2 0.217 50 - 150 25 0.15 ND 0.264 0.02 1.00
Naphthalene 117 3.53 50 - 150 25 0.31 ND 0.264 0.03 1.00
Toluene 98.3 4.63 70 - 130 20 0.26 ND 0.264 0.03 1.00
Xylenes, total 104 4.72 70 - 130 20 0.82 ND 0.792 0.08 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 28 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - SM 2540 C
QC Sample ID: BYH1211-BLK1 Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)ND 10 1.00
Duplicate - SM 2540 C
QC Sample ID: BYH1211-DUP1 QC Source Sample: XXXXXXX-XXBatch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)0.8 10 1260 1250 20 1.00
QC Sample ID: BYH1211-DUP2 QC Source Sample: 24H2214-11Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)2 10 1010 1030 20 1.00
LCS - SM 2540 C
QC Sample ID: BYH1211-BS1 Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)102 90 - 110 408 400 20 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 29 of 31
Surrogates Report for Work Order (WO) - 24H2214
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH1227-BLK1 Bromofluorobenzene 101 50 BYH1227 1.00150 203 200
BYH1227-BLK1 Capric Acid 0 BYH1227 1.0010.00 500
LCS - EPA 8015 C
BYH1227-BS1 Bromofluorobenzene 118 50 BYH1227 1.00150 236 200
BYH1227-BS1 Capric Acid 0 BYH1227 1.0010.00 500
Matrix Spike - EPA 8015 C
BYH1227-MS1 Bromofluorobenzene 100 50 BYH1227 1.00150 243 243
BYH1227-MS1 Capric Acid 0 BYH1227 1.0010.00 606
Matrix Spike Dup - EPA 8015 C
BYH1227-MSD1 Bromofluorobenzene 99.5 50 BYH1227 1.00150 241 243
BYH1227-MSD1 Capric Acid 0 BYH1227 1.0010.00 606
Blank - EPA 8260D
BYH1199-BLK1 1,2-Dichloroethane-d4 102 64.2 BYH1199 1.0012610.2 10.0
BYH1199-BLK1 4-Bromofluorobenzene 99.0 71.4 BYH1199 1.001259.90 10.0
BYH1199-BLK1 Toluene-d8 94.6 63.2 BYH1199 1.001299.46 10.0
BYH1214-BLK1 Toluene-d8 100 82 BYH1214 1.001260.0100 0.0100
LCS - EPA 8260D
BYH1199-BS1 1,2-Dichloroethane-d4 96.4 64.2 BYH1199 1.001269.64 10.0
BYH1199-BS1 4-Bromofluorobenzene 98.1 71.4 BYH1199 1.001259.81 10.0
BYH1199-BS1 Toluene-d8 91.1 63.2 BYH1199 1.001299.11 10.0
BYH1214-BS1 Toluene-d8 99.9 82 BYH1214 1.001260.00999 0.0100
Matrix Spike - EPA 8260D
BYH1199-MS1 1,2-Dichloroethane-d4 100 64.2 BYH1199 1.0012650.1 50.0
BYH1199-MS1 4-Bromofluorobenzene 95.5 71.4 BYH1199 1.0012547.8 50.0
BYH1199-MS1 Toluene-d8 92.8 63.2 BYH1199 1.0012946.4 50.0
BYH1214-MS1 Toluene-d8 101 82 BYH1214 1.001263.06 3.03
BYH1214-MS2 Toluene-d8 102 82 BYH1214 1.001260.276 0.271
Matrix Spike Dup - EPA 8260D
BYH1199-MSD1 1,2-Dichloroethane-d4 102 64.2 BYH1199 1.0012650.9 50.0
BYH1199-MSD1 4-Bromofluorobenzene 98.8 71.4 BYH1199 1.0012549.4 50.0
BYH1199-MSD1 Toluene-d8 91.8 63.2 BYH1199 1.0012945.9 50.0
BYH1214-MSD1 Toluene-d8 101 82 BYH1214 1.001263.07 3.03
BYH1214-MSD2 Toluene-d8 101 82 BYH1214 1.001260.268 0.264
CtF WO#: 24H2214
www.ChemtechFord.com Page 30 of 31
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24H2214-08 Capric Acid 0.00 0 1606
24H2214-08 Bromofluorobenzene 165 68.2 50 150243
MBTEXN-GRO
24H2214-08 Toluene-d8 3.08 102 82 1263.03
8260 Low Level Volatiles
24H2214-10 Toluene-d8 9.56 95.6 63.2 12910.0
24H2214-10 4-Bromofluorobenzene 9.61 96.1 71.4 12510.0
24H2214-10 1,2-Dichloroethane-d4 10.2 102 64.2 12610.0
CtF WO#: 24H2214
www.ChemtechFord.com Page 31 of 31
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H1461
Project: Former Sommers Auto Wrecking
8/16/2024
Approved By:
Reed Hendricks, Lab Director
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 33
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H1461-01 EXC-4-Floor1
24H1461-02 EXC-4-Floor2
24H1461-03 EXC-4-East1
24H1461-04 EXC-4-East10
24H1461-05 EXC-4-West2
24H1461-06 EXC-4-NW
24H1461-07 EXC-4-Floor3
24H1461-08 EXC-4-West3
24H1461-09 Trip Blank
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
Page 2 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-Floor1
Lab ID: 24H1461-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/13/24 10:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/15/248/15/2464EPA 8015 C77Diesel Range Organics
Inorganic
%8/15/248/15/240.1 CTF800078.1Total Solids
MBTEXn
mg/kg dry 8/15/248/15/240.002 EPA 8260D/5035A0.02Benzene
mg/kg dry 8/15/248/15/240.005 EPA 8260D/5035A0.02Ethylbenzene
mg/kg dry J-LOW-C8/15/248/15/240.003 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/15/248/15/240.005 EPA 8260D/5035A0.02Naphthalene
mg/kg dry 8/15/248/15/240.005 EPA 8260D/5035ANDToluene
mg/kg dry 8/15/248/15/240.01 EPA 8260D/5035A0.12Xylenes, total
mg/kg dry 8/15/248/15/240.05 EPA 8260D/5035A1.91Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 3 of 33Page 3 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-Floor2
Lab ID: 24H1461-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/13/24 10:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/15/248/15/2467EPA 8015 CNDDiesel Range Organics
Inorganic
%8/15/248/15/240.1 CTF800074.9Total Solids
MBTEXn
mg/kg dry 8/15/248/15/240.003 EPA 8260D/5035A0.01Benzene
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035A0.01Ethylbenzene
mg/kg dry J-LOW-C8/15/248/15/240.004 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035A0.007Naphthalene
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035A0.05Toluene
mg/kg dry 8/15/248/15/240.02 EPA 8260D/5035A0.15Xylenes, total
mg/kg dry 8/15/248/15/240.06 EPA 8260D/5035A1.04Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 4 of 33Page 4 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-East1
Lab ID: 24H1461-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/14/24 12:45
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/15/248/15/2463EPA 8015 CNDDiesel Range Organics
Inorganic
%8/15/248/15/240.1 CTF800079.2Total Solids
MBTEXn
mg/kg dry 8/15/248/15/240.003 EPA 8260D/5035A0.04Benzene
mg/kg dry 8/15/248/15/240.007 EPA 8260D/5035ANDEthylbenzene
mg/kg dry J-LOW-C8/15/248/15/240.004 EPA 8260D/5035A0.02Methyl tert-Butyl Ether (MTBE)
mg/kg dry 8/15/248/15/240.007 EPA 8260D/5035ANDNaphthalene
mg/kg dry 8/15/248/15/240.007 EPA 8260D/5035ANDToluene
mg/kg dry 8/15/248/15/240.02 EPA 8260D/5035ANDXylenes, total
mg/kg dry 8/15/248/15/240.07 EPA 8260D/5035A0.33Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 5 of 33Page 5 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-East10
Lab ID: 24H1461-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/14/24 13:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/15/248/15/2462EPA 8015 CNDDiesel Range Organics
Inorganic
%8/15/248/15/240.1 CTF800080.3Total Solids
MBTEXn
mg/kg dry 8/15/248/15/240.003 EPA 8260D/5035A0.02Benzene
mg/kg dry 8/15/248/15/240.007 EPA 8260D/5035ANDEthylbenzene
mg/kg dry J-LOW-C8/15/248/15/240.004 EPA 8260D/5035A0.01Methyl tert-Butyl Ether (MTBE)
mg/kg dry 8/15/248/15/240.007 EPA 8260D/5035ANDNaphthalene
mg/kg dry 8/15/248/15/240.007 EPA 8260D/5035ANDToluene
mg/kg dry 8/15/248/15/240.02 EPA 8260D/5035ANDXylenes, total
mg/kg dry 8/15/248/15/240.07 EPA 8260D/5035A0.17Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 6 of 33Page 6 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-West2
Lab ID: 24H1461-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/15/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/15/248/15/2460EPA 8015 CNDDiesel Range Organics
Inorganic
%8/15/248/15/240.1 CTF800083.0Total Solids
BETX Compounds
mg/kg dry 8/16/248/16/240.06 EPA 8260D/5035A0.19C5-C6 Aliphatic hydrocarbons
mg/kg dry 8/16/248/16/240.06 EPA 8260D/5035A0.17C7-C8 Aliphatic hydrocarbons
mg/kg dry 8/16/248/16/240.06 EPA 8260D/5035A0.08C9-C10 Aliphatic hydrocarbons
mg/kg dry 8/16/248/16/240.06 EPA 8260D/5035A0.12C9-C10 Alkyl Benzenes
mg/kg dry 8/16/248/16/240.003 EPA 8260D/5035A0.11Benzene
mg/kg dry 8/16/248/16/240.006 EPA 8260D/5035A0.006Ethylbenzene
mg/kg dry 8/16/248/16/240.006 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/16/248/16/240.006 EPA 8260D/5035A0.007Naphthalene
mg/kg dry 8/16/248/16/240.006 EPA 8260D/5035ANDToluene
mg/kg dry 8/16/248/16/240.02 EPA 8260D/5035ANDXylenes, total
MBTEXn
mg/kg dry 8/16/248/16/240.003 EPA 8260D/5035A0.11Benzene
mg/kg dry 8/16/248/16/240.006 EPA 8260D/5035A0.006Ethylbenzene
mg/kg dry 8/16/248/16/240.004 EPA 8260D/5035A0.03Methyl tert-Butyl Ether (MTBE)
mg/kg dry 8/16/248/16/240.006 EPA 8260D/5035A0.007Naphthalene
mg/kg dry 8/16/248/16/240.006 EPA 8260D/5035ANDToluene
mg/kg dry 8/16/248/16/240.02 EPA 8260D/5035ANDXylenes, total
mg/kg dry 8/16/248/16/240.06 EPA 8260D/5035A0.69Gasoline Range Organics
Semi-Volatile Compounds
mg/kg dry 8/15/248/15/242.41 EPA 8270E/3570NDC11-12 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.41 EPA 8270E/3570NDC13-C16 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.41 EPA 8270E/3570NDC17-C21 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.41 EPA 8270E/357023.9C22-C35 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.41 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 8/15/248/15/242.41 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDAcenaphthene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDAnthracene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDBenzo (k) fluoranthene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 7 of 33Page 7 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-West2 (cont.)
Lab ID: 24H1461-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/15/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Semi-Volatile Compounds (cont.)
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDChrysene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDFluoranthene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDFluorene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDPhenanthrene
mg/kg dry 8/15/248/15/244.82 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 8 of 33Page 8 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-NW
Lab ID: 24H1461-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/15/24 9:30
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/15/248/15/2462EPA 8015 CNDDiesel Range Organics
Inorganic
%8/15/248/15/240.1 CTF800080.6Total Solids
MBTEXn
mg/kg dry 8/15/248/15/240.002 EPA 8260D/5035ANDBenzene
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035A0.02Ethylbenzene
mg/kg dry J-LOW-C8/15/248/15/240.003 EPA 8260D/5035A0.006Methyl tert-Butyl Ether (MTBE)
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035A0.02Naphthalene
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035ANDToluene
mg/kg dry 8/15/248/15/240.02 EPA 8260D/5035A0.17Xylenes, total
mg/kg dry 8/15/248/15/240.06 EPA 8260D/5035A1.19Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 9 of 33Page 9 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-Floor3
Lab ID: 24H1461-07Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/15/24 9:40
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/15/248/15/2461EPA 8015 CNDDiesel Range Organics
Inorganic
%8/15/248/15/240.1 CTF800081.9Total Solids
MBTEXn
mg/kg dry 8/15/248/15/240.002 EPA 8260D/5035A0.007Benzene
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035ANDEthylbenzene
mg/kg dry J-LOW-C8/15/248/15/240.004 EPA 8260D/5035A0.01Methyl tert-Butyl Ether (MTBE)
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035ANDNaphthalene
mg/kg dry 8/15/248/15/240.006 EPA 8260D/5035ANDToluene
mg/kg dry 8/15/248/15/240.02 EPA 8260D/5035A0.02Xylenes, total
mg/kg dry 8/15/248/15/240.06 EPA 8260D/5035A0.18Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 10 of 33Page 10 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-West3
Lab ID: 24H1461-08Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/15/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/15/248/15/2459EPA 8015 C1310Diesel Range Organics
Inorganic
%8/15/248/15/240.1 CTF800084.4Total Solids
BETX Compounds
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A251C5-C6 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A390C7-C8 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A181C9-C10 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A671C9-C10 Alkyl Benzenes
mg/kg dry 8/15/248/15/240.12 EPA 8260D/5035ANDBenzene
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A164Ethylbenzene
mg/kg dry 8/15/248/15/240.30 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A50.4Naphthalene
mg/kg dry 8/15/248/15/240.30 EPA 8260D/5035A3.00Toluene
mg/kg dry 8/15/248/15/2488.8 EPA 8260D/5035A794Xylenes, total
MBTEXn
mg/kg dry 8/15/248/15/240.12 EPA 8260D/5035ANDBenzene
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A164Ethylbenzene
mg/kg dry J-LOW-C8/15/248/15/240.18 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A50.4Naphthalene
mg/kg dry 8/15/248/15/240.30 EPA 8260D/5035A3.00Toluene
mg/kg dry 8/15/248/15/2488.8 EPA 8260D/5035A794Xylenes, total
mg/kg dry 8/15/248/15/242.96 EPA 8260D/5035A1500Gasoline Range Organics
Semi-Volatile Compounds
mg/kg dry 8/15/248/15/242.37 EPA 8270E/357025.4C11-12 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.37 EPA 8270E/357010.4C13-C16 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.37 EPA 8270E/357012.0C17-C21 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.37 EPA 8270E/357026.5C22-C35 Aliphatic hydrocarbons
mg/kg dry 8/15/248/15/242.37 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 8/15/248/15/242.37 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDAcenaphthene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDAnthracene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDBenzo (k) fluoranthene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 11 of 33Page 11 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-West3 (cont.)
Lab ID: 24H1461-08Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/15/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Semi-Volatile Compounds (cont.)
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDChrysene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDFluoranthene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDFluorene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDPhenanthrene
mg/kg dry 8/15/248/15/244.74 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 12 of 33Page 12 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24H1461-09Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/13/24 8:15
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,1-Dichloropropene
ug/L J-LOW-C8/15/248/15/24125EPA 8260D/5030BND2-Hexanone
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L J-LOW-C8/15/248/15/2412.5 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND2-Chlorotoluene
ug/L 8/15/248/15/2425.0 EPA 8260D/5030BND2-Nitropropane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BND4-Chlorotoluene
ug/L 8/15/248/15/24250EPA 8260D/5030BNDAcetone
ug/L 8/15/248/15/2462.5 EPA 8260D/5030BNDAcrylonitrile
ug/L 8/15/248/15/245.0 EPA 8260D/5030BNDBenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDBromobenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDBromochloromethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDBromodichloromethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDBromoform
ug/L J-LOW-C8/15/248/15/2425.0 EPA 8260D/5030BNDBromomethane
ug/L 8/15/248/15/2425.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 13 of 33Page 13 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24H1461-09Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/13/24 8:15
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDChloroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDChloroform
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDChloromethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L 8/15/248/15/24125EPA 8260D/5030BNDCyclohexanone
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDDibromochloromethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDDibromomethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 8/15/248/15/2425.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDEthylbenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDEthyl Ether
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 8/15/248/15/24250EPA 8260D/5030BNDIsobutanol
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDIsopropylbenzene
ug/L 8/15/248/15/2425.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 8/15/248/15/2462.5 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDMethylene Chloride
ug/L J-LOW-C8/15/248/15/247.5 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDNaphthalene
ug/L 8/15/248/15/24625EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDn-Butylbenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDPentachloroethane
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDStyrene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDTetrachloroethene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDToluene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDTrichloroethene
ug/L 8/15/248/15/2412.5 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 8/15/248/15/2410.0 EPA 8260D/5030BNDVinyl Chloride
ug/L 8/15/248/15/2437.5 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 14 of 33Page 14 of 33
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/15/24 13:59 @ 0.5 °C
8/16/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-C = Estimated low due to low recovery of CCV
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1461
www.ChemtechFord.com
Page 15 of 33Page 15 of 33
Page 16 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYH0781-DUP1 QC Source Sample: 24H1461-05Batch: BYH0781
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Total Solids 1.96 20 81.4 83.0 0.1 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 17 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH0801-BLK1 Batch: BYH0801
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Diesel Range Organics ND 50 1.00
LCS - EPA 8015 C
QC Sample ID: BYH0801-BS1 Batch: BYH0801
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Diesel Range Organics 102 50 - 150 2030 2000 50 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH0801-MS1 QC Source Sample: 24H1461-05Batch: BYH0801
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Diesel Range Organics 107 50 - 150 2590 ND 2410 60 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH0801-MSD1 QC Source Sample: 24H1461-05Batch: BYH0801
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Diesel Range Organics 104 2.87 50 - 150 20 2520 ND 2410 60 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 18 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH0760-BLK1 Batch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.4 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 19 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYH0760-BLK1 Batch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Ethylbenzene ND 1.0 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Naphthalene ND 1.0 1.00
n-Butyl Alcohol ND 50.0 1.00
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 1.0 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 3.0 1.00
QC Sample ID: BYH0786-BLK1 Batch: BYH0786
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH0840-BLK1 Batch: BYH0840
Date Prepared: 08/16/2024 Date Analyzed: 08/16/2024
Benzene ND 0.0004 1.00
C5-C6 Aliphatic hydrocarbons ND 0.01 1.00
C7-C8 Aliphatic hydrocarbons ND 0.01 1.00
C9-C10 Aliphatic hydrocarbons ND 0.01 1.00
C9-C10 Alkyl Benzenes ND 0.01 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
CtF WO#: 24H1461
www.ChemtechFord.com Page 20 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH0760-BS1 Batch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
1,1,1,2-Tetrachloroethane 106 70 - 130 10.6 10.0 1.0 1.00
1,1,1-Trichloroethane 112 70 - 130 11.2 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 99.1 70 - 130 9.91 10.0 1.0 1.00
1,1,2-Trichloroethane 96.0 70 - 130 9.60 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 122 70 - 130 12.2 10.0 1.0 1.00
1,1-Dichloroethane 111 70 - 130 11.1 10.0 1.0 1.00
1,1-Dichloroethene 100 70 - 130 10.0 10.0 1.0 1.00
1,1-Dichloropropene 103 70 - 130 10.3 10.0 1.0 1.00
1,2,3-Trichlorobenzene 112 70 - 130 11.2 10.0 1.0 1.00
1,2,3-Trichloropropane 96.9 70 - 130 9.69 10.0 1.0 1.00
1,2,4-Trichlorobenzene 114 70 - 130 11.4 10.0 1.0 1.00
1,2,4-Trimethylbenzene 103 70 - 130 10.3 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 94.4 70 - 130 9.44 10.0 1.0 1.00
1,2-Dibromoethane (EDB)103 70 - 130 10.3 10.0 1.0 1.00
1,2-Dichlorobenzene 103 70 - 130 10.3 10.0 1.0 1.00
1,2-Dichloroethane 96.7 70 - 130 9.67 10.0 1.0 1.00
1,2-Dichloropropane 102 70 - 130 10.2 10.0 1.0 1.00
1,3,5-Trimethylbenzene 107 70 - 130 10.7 10.0 1.0 1.00
1,3-Dichlorobenzene 110 70 - 130 11.0 10.0 1.0 1.00
1,3-Dichloropropane 97.4 70 - 130 9.74 10.0 1.0 1.00
1,4-Dichlorobenzene 108 70 - 130 10.8 10.0 1.0 1.00
2,2-Dichloropropane 97.7 70 - 130 9.77 10.0 1.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
2-Chlorotoluene 104 70 - 130 10.4 10.0 1.0 1.00
2-Hexanone 142 70 - 130 14.2 10.0 10.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
2-Nitropropane 91.9 70 - 130 27.6 30.0 2.0 1.00
4-Chlorotoluene 102 70 - 130 10.2 10.0 1.0 1.00
Acetone 100 70 - 130 100 100 20.0 1.00
Acrylonitrile 89.8 70 - 130 44.9 50.0 5.0 1.00
Benzene 109 70 - 130 10.9 10.0 0.4 1.00
Bromobenzene 102 70 - 130 10.2 10.0 1.0 1.00
Bromochloromethane 99.3 70 - 130 9.93 10.0 1.0 1.00
Bromodichloromethane 96.9 70 - 130 9.69 10.0 1.0 1.00
Bromoform 90.6 70 - 130 9.06 10.0 1.0 1.00
Bromomethane 46.6 70 - 130 4.66 10.0 2.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Carbon Disulfide 111 70 - 130 11.1 10.0 2.0 1.00
Carbon Tetrachloride 117 70 - 130 11.7 10.0 1.0 1.00
Chlorobenzene 108 70 - 130 10.8 10.0 1.0 1.00
Chloroethane 103 70 - 130 10.3 10.0 1.0 1.00
Chloroform 95.5 70 - 130 9.55 10.0 1.0 1.00
Chloromethane 86.0 70 - 130 8.60 10.0 1.0 1.00
cis-1,2-Dichloroethene 94.1 70 - 130 9.41 10.0 1.0 1.00
cis-1,3-Dichloropropene 107 70 - 130 10.7 10.0 1.0 1.00
Cyclohexanone 109 70 - 130 109 100 10.0 1.00
Dibromochloromethane 96.4 70 - 130 9.64 10.0 1.0 1.00
Dibromomethane 106 70 - 130 10.6 10.0 1.0 1.00
Dichlorodifluoromethane 97.4 70 - 130 9.74 10.0 1.0 1.00
Ethyl Acetate 95.4 70 - 130 19.1 20.0 2.0 1.00
Ethyl Ether 92.0 70 - 130 9.20 10.0 1.0 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 21 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH0760-BS1 Batch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Ethylbenzene 103 70 - 130 10.3 10.0 1.0 1.00
Hexachlorobutadiene 123 70 - 130 12.3 10.0 1.0 1.00
Isobutanol 140 70 - 130 280 200 20.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 108 70 - 130 10.8 10.0 1.0 1.00
Methyl Ethyl Ketone 89.3 70 - 130 8.93 10.0 2.0 1.00
Methyl Isobutyl Ketone 102 70 - 130 10.2 10.0 5.0 1.00
Methylene Chloride 89.8 70 - 130 8.98 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)48.6 70 - 130 4.86 10.0 0.6 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Naphthalene 98.8 70 - 130 9.88 10.0 1.0 1.00
n-Butyl Alcohol 93.1 70 - 130 93.1 100 50.0 1.00
n-Butylbenzene 110 70 - 130 11.0 10.0 1.0 1.00
n-Propyl Benzene 107 70 - 130 10.7 10.0 1.0 1.00
Pentachloroethane 104 70 - 130 10.4 10.0 1.0 1.00
p-Isopropyltoluene 106 70 - 130 10.6 10.0 1.0 1.00
sec-Butyl Benzene 108 70 - 130 10.8 10.0 1.0 1.00
Styrene 109 70 - 130 10.9 10.0 1.0 1.00
tert-Butylbenzene 108 70 - 130 10.8 10.0 1.0 1.00
Tetrachloroethene 97.8 70 - 130 9.78 10.0 1.0 1.00
Toluene 101 70 - 130 10.1 10.0 1.0 1.00
trans-1,2-Dichloroethene 98.4 70 - 130 9.84 10.0 1.0 1.00
trans-1,3-Dichloropropene 104 70 - 130 10.4 10.0 1.0 1.00
Trichloroethene 109 70 - 130 10.9 10.0 1.0 1.00
Trichlorofluoromethane 99.0 70 - 130 9.90 10.0 1.0 1.00
Vinyl Chloride 96.0 70 - 130 9.60 10.0 0.8 1.00
Xylenes, total 109 70 - 130 32.7 30.0 3.0 1.00
QC Sample ID: BYH0786-BS1 Batch: BYH0786
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Benzene 106 70 - 130 0.01 0.0100 0.0004 1.00
Ethylbenzene 99.5 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)47.5 70 - 130 0.005 0.0100 0.0006 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Naphthalene 112 70 - 130 0.01 0.0100 0.001 1.00
Toluene 100 70 - 130 0.01 0.0100 0.001 1.00
Xylenes, total 109 70 - 130 0.03 0.0300 0.003 1.00
QC Sample ID: BYH0840-BS1 Batch: BYH0840
Date Prepared: 08/16/2024 Date Analyzed: 08/16/2024
Benzene 101 70 - 130 0.01 0.0100 0.0004 1.00
Ethylbenzene 96.2 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)87.1 70 - 130 0.009 0.0100 0.0006 1.00
Naphthalene 99.1 70 - 130 0.01 0.0100 0.001 1.00
Toluene 95.7 70 - 130 0.01 0.0100 0.001 1.00
Xylenes, total 103 70 - 130 0.03 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH0760-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
1,1,1,2-Tetrachloroethane 104 70 - 130 51.8 ND 50.0 5.0 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 22 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH0760-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
1,1,1-Trichloroethane 109 70 - 130 54.6 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 111 70 - 130 55.4 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 106 70 - 130 52.8 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 122 70 - 130 60.8 ND 50.0 5.0 1.00
1,1-Dichloroethane 111 70 - 130 55.7 ND 50.0 5.0 1.00
1,1-Dichloroethene 102 70 - 130 50.8 ND 50.0 5.0 1.00
1,1-Dichloropropene 100 70 - 130 50.2 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 114 70 - 130 57.2 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 106 70 - 130 52.8 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 117 70 - 130 58.6 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 103 70 - 130 51.4 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 98.5 70 - 130 49.2 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)108 70 - 130 54.0 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 108 70 - 130 54.1 ND 50.0 5.0 1.00
1,2-Dichloroethane 102 70 - 130 51.1 ND 50.0 5.0 1.00
1,2-Dichloropropane 101 70 - 130 50.5 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 107 70 - 130 53.4 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 111 70 - 130 55.4 ND 50.0 5.0 1.00
1,3-Dichloropropane 103 70 - 130 51.4 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 110 70 - 130 54.8 ND 50.0 5.0 1.00
2,2-Dichloropropane 100 70 - 130 50.0 ND 50.0 5.0 1.00
2-Chlorotoluene 101 70 - 130 50.4 ND 50.0 5.0 1.00
2-Hexanone 112 70 - 130 56.1 ND 50.0 50.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
2-Nitropropane 89.3 70 - 130 134 ND 150 10.0 1.00
4-Chlorotoluene 98.9 70 - 130 49.4 ND 50.0 5.0 1.00
Acetone 109 70 - 130 543 ND 500 100 1.00
Acrylonitrile 97.6 70 - 130 244 ND 250 25.0 1.00
Benzene 106 70 - 130 53.1 ND 50.0 2.0 1.00
Bromobenzene 102 70 - 130 50.8 ND 50.0 5.0 1.00
Bromochloromethane 104 70 - 130 52.1 ND 50.0 5.0 1.00
Bromodichloromethane 102 70 - 130 50.8 ND 50.0 5.0 1.00
Bromoform 96.9 70 - 130 48.4 ND 50.0 5.0 1.00
Bromomethane 45.5 70 - 130 34.7 12.0 50.0 10.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Carbon Disulfide 112 70 - 130 56.0 ND 50.0 10.0 1.00
Carbon Tetrachloride 115 70 - 130 57.6 ND 50.0 5.0 1.00
Chlorobenzene 106 70 - 130 52.8 ND 50.0 5.0 1.00
Chloroethane 106 70 - 130 52.9 ND 50.0 5.0 1.00
Chloroform 97.1 70 - 130 48.6 ND 50.0 5.0 1.00
Chloromethane 91.3 70 - 130 45.6 ND 50.0 5.0 1.00
cis-1,2-Dichloroethene 93.9 70 - 130 47.0 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 112 70 - 130 55.8 ND 50.0 5.0 1.00
Cyclohexanone 74.2 70 - 130 371 ND 500 50.0 1.00
Dibromochloromethane 100 70 - 130 50.2 ND 50.0 5.0 1.00
Dibromomethane 118 70 - 130 59.0 ND 50.0 5.0 1.00
Dichlorodifluoromethane 102 70 - 130 50.8 ND 50.0 5.0 1.00
Ethyl Acetate 104 70 - 130 104 ND 100 10.0 1.00
Ethyl Ether 96.9 70 - 130 48.4 ND 50.0 5.0 1.00
Ethylbenzene 98.7 70 - 130 49.4 ND 50.0 5.0 1.00
Hexachlorobutadiene 112 70 - 130 56.2 ND 50.0 5.0 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 23 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH0760-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Isobutanol 140 70 - 130 1400 ND 1000 100 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 105 70 - 130 52.6 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 100 70 - 130 50.0 ND 50.0 10.0 1.00
Methyl Isobutyl Ketone 114 70 - 130 56.8 ND 50.0 25.0 1.00
Methylene Chloride 91.8 70 - 130 45.9 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)51.0 70 - 130 25.5 ND 50.0 3.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Naphthalene 108 70 - 130 54.2 ND 50.0 5.0 1.00
n-Butyl Alcohol 98.8 70 - 130 494 ND 500 250 1.00
n-Butylbenzene 104 70 - 130 51.9 ND 50.0 5.0 1.00
n-Propyl Benzene 104 70 - 130 52.1 ND 50.0 5.0 1.00
Pentachloroethane 81.8 70 - 130 40.9 ND 50.0 5.0 1.00
p-Isopropyltoluene 101 70 - 130 50.4 ND 50.0 5.0 1.00
sec-Butyl Benzene 105 70 - 130 52.6 ND 50.0 5.0 1.00
Styrene 107 70 - 130 53.4 ND 50.0 5.0 1.00
tert-Butylbenzene 104 70 - 130 52.0 ND 50.0 5.0 1.00
Tetrachloroethene 92.4 70 - 130 46.2 ND 50.0 5.0 1.00
Toluene 100 70 - 130 50.1 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 98.1 70 - 130 49.0 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 112 70 - 130 55.8 ND 50.0 5.0 1.00
Trichloroethene 109 70 - 130 54.4 ND 50.0 5.0 1.00
Trichlorofluoromethane 103 70 - 130 51.3 ND 50.0 5.0 1.00
Vinyl Chloride 94.9 70 - 130 47.4 ND 50.0 4.0 1.00
Xylenes, total 106 70 - 130 159 ND 150 15.0 1.00
QC Sample ID: BYH0786-MS1 QC Source Sample: 24H1461-05Batch: BYH0786
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Benzene 92.3 70 - 130 2.94 0.16 3.01 0.12 1.00
Ethylbenzene 86.5 50 - 150 2.73 0.13 3.01 0.30 1.00
Methyl tert-Butyl Ether (MTBE)63.0 50 - 150 1.90 ND 3.01 0.18 1.00
Naphthalene 116 50 - 150 3.50 ND 3.01 0.30 1.00
Toluene 86.1 70 - 130 2.59 ND 3.01 0.30 1.00
Xylenes, total 94.3 70 - 130 9.09 0.56 9.04 0.90 1.00
QC Sample ID: BYH0840-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0840
Date Prepared: 08/16/2024 Date Analyzed: 08/16/2024
Benzene 93.7 70 - 130 2.34 ND 2.50 0.10 1.00
Ethylbenzene 87.7 50 - 150 2.19 ND 2.50 0.25 1.00
Methyl tert-Butyl Ether (MTBE)86.4 50 - 150 2.16 ND 2.50 0.15 1.00
Naphthalene 93.8 50 - 150 2.34 ND 2.50 0.25 1.00
Toluene 87.1 70 - 130 2.18 ND 2.50 0.25 1.00
Xylenes, total 95.4 70 - 130 7.15 ND 7.50 0.75 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH0760-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
1,1,1,2-Tetrachloroethane 104 0.482 70 - 130 20 52.0 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 105 4.21 70 - 130 20 52.3 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 108 2.74 70 - 130 20 54.0 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 104 1.91 70 - 130 20 51.8 ND 50.0 5.0 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 24 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH0760-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
1,1,2-Trichlorotrifluoroethane 119 1.91 70 - 130 20 59.7 ND 50.0 5.0 1.00
1,1-Dichloroethane 108 3.47 70 - 130 20 53.8 ND 50.0 5.0 1.00
1,1-Dichloroethene 96.5 5.25 70 - 130 20 48.2 ND 50.0 5.0 1.00
1,1-Dichloropropene 98.3 2.21 70 - 130 20 49.2 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 116 1.56 70 - 130 20 58.1 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 107 1.41 70 - 130 20 53.5 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 117 0.00 70 - 130 20 58.6 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 105 2.41 70 - 130 20 52.6 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 103 4.85 70 - 130 20 51.7 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)106 1.40 70 - 130 20 53.2 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 108 0.370 70 - 130 20 53.9 ND 50.0 5.0 1.00
1,2-Dichloroethane 98.8 3.38 70 - 130 20 49.4 ND 50.0 5.0 1.00
1,2-Dichloropropane 96.9 4.14 70 - 130 20 48.4 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 105 1.51 70 - 130 20 52.6 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 112 0.720 70 - 130 20 55.8 ND 50.0 5.0 1.00
1,3-Dichloropropane 103 0.485 70 - 130 20 51.6 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 109 0.548 70 - 130 20 54.6 ND 50.0 5.0 1.00
2,2-Dichloropropane 92.6 7.68 70 - 130 20 46.3 ND 50.0 5.0 1.00
2-Chlorotoluene 99.6 1.30 70 - 130 20 49.8 ND 50.0 5.0 1.00
2-Hexanone 112 0.267 70 - 130 20 56.2 ND 50.0 50.0 1.00
2-Nitropropane 86.2 3.53 70 - 130 20 129 ND 150 10.0 1.00
4-Chlorotoluene 99.2 0.303 70 - 130 20 49.6 ND 50.0 5.0 1.00
Acetone 104 4.39 70 - 130 20 520 ND 500 100 1.00
Acrylonitrile 97.8 0.266 70 - 130 20 245 ND 250 25.0 1.00
Benzene 105 1.14 70 - 130 20 52.5 ND 50.0 2.0 1.00
Bromobenzene 102 0.393 70 - 130 20 51.0 ND 50.0 5.0 1.00
Bromochloromethane 104 0.385 70 - 130 20 51.9 ND 50.0 5.0 1.00
Bromodichloromethane 99.2 2.39 70 - 130 20 49.6 ND 50.0 5.0 1.00
Bromoform 98.3 1.43 70 - 130 20 49.2 ND 50.0 5.0 1.00
Bromomethane 52.1 9.08 70 - 130 20 38.0 12.0 50.0 10.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Carbon Disulfide 106 5.22 70 - 130 20 53.2 ND 50.0 10.0 1.00
Carbon Tetrachloride 110 4.98 70 - 130 20 54.8 ND 50.0 5.0 1.00
Chlorobenzene 104 1.62 70 - 130 20 52.0 ND 50.0 5.0 1.00
Chloroethane 95.7 10.0 70 - 130 20 47.8 ND 50.0 5.0 1.00
Chloroform 92.6 4.74 70 - 130 20 46.3 ND 50.0 5.0 1.00
Chloromethane 92.4 1.20 70 - 130 20 46.2 ND 50.0 5.0 1.00
cis-1,2-Dichloroethene 92.9 1.07 70 - 130 20 46.4 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 111 0.990 70 - 130 20 55.3 ND 50.0 5.0 1.00
Cyclohexanone 73.6 0.758 70 - 130 20 368 ND 500 50.0 1.00
Dibromochloromethane 101 0.398 70 - 130 20 50.4 ND 50.0 5.0 1.00
Dibromomethane 114 3.63 70 - 130 20 56.8 ND 50.0 5.0 1.00
Dichlorodifluoromethane 95.1 6.71 70 - 130 20 47.6 ND 50.0 5.0 1.00
Ethyl Acetate 104 0.818 70 - 130 20 104 ND 100 10.0 1.00
Ethyl Ether 93.9 3.14 70 - 130 20 47.0 ND 50.0 5.0 1.00
Ethylbenzene 99.0 0.303 70 - 130 20 49.5 ND 50.0 5.0 1.00
Hexachlorobutadiene 112 0.268 70 - 130 20 56.0 ND 50.0 5.0 1.00
Isobutanol 136 2.90 70 - 130 20 1360 ND 1000 100 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 101 3.78 70 - 130 20 50.6 ND 50.0 5.0 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 25 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH0760-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0760
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Methyl Ethyl Ketone 98.5 1.61 70 - 130 20 49.2 ND 50.0 10.0 1.00
Methyl Isobutyl Ketone 112 1.69 70 - 130 20 55.8 ND 50.0 25.0 1.00
Methylene Chloride 89.4 2.65 70 - 130 20 44.7 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)47.3 7.53 70 - 130 20 23.6 ND 50.0 3.0 1.00
J-LOW-C - Estimated low due to low recovery of CCV
Naphthalene 110 1.19 70 - 130 20 54.8 ND 50.0 5.0 1.00
n-Butyl Alcohol 85.9 14.0 70 - 130 20 429 ND 500 250 1.00
n-Butylbenzene 101 2.73 70 - 130 20 50.5 ND 50.0 5.0 1.00
n-Propyl Benzene 103 1.45 70 - 130 20 51.4 ND 50.0 5.0 1.00
Pentachloroethane 106 26.1 70 - 130 20 53.2 ND 50.0 5.0 1.00
RPD-01 - RPD between MS and MSD is outside established limits. Data is acceptable based on MS and MSD being within
acceptable recovery limits.
p-Isopropyltoluene 102 1.57 70 - 130 20 51.2 ND 50.0 5.0 1.00
sec-Butyl Benzene 102 3.38 70 - 130 20 50.9 ND 50.0 5.0 1.00
Styrene 106 0.941 70 - 130 20 52.9 ND 50.0 5.0 1.00
tert-Butylbenzene 102 1.65 70 - 130 20 51.2 ND 50.0 5.0 1.00
Tetrachloroethene 92.5 0.108 70 - 130 20 46.2 ND 50.0 5.0 1.00
Toluene 96.7 3.56 70 - 130 20 48.4 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 95.1 3.11 70 - 130 20 47.6 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 108 3.55 70 - 130 20 53.9 ND 50.0 5.0 1.00
Trichloroethene 104 4.80 70 - 130 20 51.8 ND 50.0 5.0 1.00
Trichlorofluoromethane 97.5 5.10 70 - 130 20 48.8 ND 50.0 5.0 1.00
Vinyl Chloride 91.3 3.87 70 - 130 20 45.6 ND 50.0 4.0 1.00
Xylenes, total 105 1.49 70 - 130 20 157 ND 150 15.0 1.00
QC Sample ID: BYH0786-MSD1 QC Source Sample: 24H1461-05Batch: BYH0786
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Benzene 89.8 2.59 70 - 130 20 2.87 0.16 3.01 0.12 1.00
Ethylbenzene 79.7 7.79 50 - 150 25 2.53 0.13 3.01 0.30 1.00
Methyl tert-Butyl Ether (MTBE)50.8 21.4 50 - 150 25 1.53 ND 3.01 0.18 1.00
Naphthalene 106 8.98 50 - 150 25 3.20 ND 3.01 0.30 1.00
Toluene 82.7 4.03 70 - 130 20 2.49 ND 3.01 0.30 1.00
Xylenes, total 85.6 9.08 70 - 130 20 8.30 0.56 9.04 0.90 1.00
QC Sample ID: BYH0840-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0840
Date Prepared: 08/16/2024 Date Analyzed: 08/16/2024
Benzene 90.5 3.47 70 - 130 20 2.26 ND 2.50 0.10 1.00
Ethylbenzene 86.1 1.84 50 - 150 25 2.15 ND 2.50 0.25 1.00
Methyl tert-Butyl Ether (MTBE)77.1 11.4 50 - 150 25 1.93 ND 2.50 0.15 1.00
Naphthalene 94.8 1.06 50 - 150 25 2.37 ND 2.50 0.25 1.00
Toluene 84.4 3.15 70 - 130 20 2.11 ND 2.50 0.25 1.00
Xylenes, total 95.7 0.384 70 - 130 20 7.18 ND 7.50 0.75 1.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 26 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8270E
QC Sample ID: BYH0787-BLK1 Batch: BYH0787
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Acenaphthene ND 0.40 1.00
Acenaphthylene ND 0.40 1.00
Anthracene ND 0.40 1.00
Benzo (a) anthracene ND 0.40 1.00
Benzo (a) pyrene ND 0.40 1.00
Benzo (b) fluoranthene ND 0.40 1.00
Benzo (g,h,i) perylene ND 0.40 1.00
Benzo (k) fluoranthene ND 0.40 1.00
C11-12 Aliphatic hydrocarbons ND 0.20 1.00
C11-C13 Alkyl Naphthalenes ND 0.20 1.00
C13-C16 Aliphatic hydrocarbons ND 0.20 1.00
C17-C21 Aliphatic hydrocarbons ND 0.20 1.00
C22-C35 Aliphatic hydrocarbons ND 0.20 1.00
Chrysene ND 0.40 1.00
Fluoranthene ND 0.40 1.00
Fluorene ND 0.40 1.00
Indeno (1,2,3-cd) pyrene ND 0.40 1.00
Phenanthrene ND 0.40 1.00
Pyrene ND 0.40 1.00
Total C12-C22 PAH ND 0.20 1.00
LCS - EPA 8270E
QC Sample ID: BYH0787-BS1 Batch: BYH0787
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Acenaphthene 66.0 47 - 145 0.4 0.667 0.40 1.00
Acenaphthylene 72.5 65 - 135 0.5 0.667 0.40 1.00
Anthracene 74.4 65 - 135 0.5 0.667 0.40 1.00
Benzo (a) anthracene 78.6 65 - 135 0.5 0.667 0.40 1.00
Benzo (a) pyrene 80.7 65 - 135 0.5 0.667 0.40 1.00
Benzo (b) fluoranthene 92.3 65 - 135 0.6 0.667 0.40 1.00
Benzo (g,h,i) perylene 82.6 65 - 135 0.6 0.667 0.40 1.00
Benzo (k) fluoranthene 93.8 65 - 135 0.6 0.667 0.40 1.00
Chrysene 80.0 65 - 135 0.5 0.667 0.40 1.00
Fluoranthene 88.9 65 - 135 0.6 0.667 0.40 1.00
Fluorene 66.9 65 - 135 0.4 0.667 0.40 1.00
Indeno (1,2,3-cd) pyrene 73.2 65 - 135 0.5 0.667 0.40 1.00
Phenanthrene 75.4 65 - 135 0.5 0.667 0.40 1.00
Pyrene 80.0 33 - 130 0.5 0.667 0.40 1.00
Matrix Spike - EPA 8270E
QC Sample ID: BYH0787-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0787
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Acenaphthene 47 - 145 ND ND 0.667 8.00 20.00
Acenaphthylene 50 - 150 ND ND 0.667 8.00 20.00
Anthracene 50 - 150 ND ND 0.667 8.00 20.00
Benzo (a) anthracene 50 - 150 ND ND 0.667 8.00 20.00
Benzo (a) pyrene 50 - 150 ND ND 0.667 8.00 20.00
Benzo (b) fluoranthene 50 - 150 ND ND 0.667 8.00 20.00
Benzo (g,h,i) perylene 50 - 150 ND ND 0.667 8.00 20.00
Benzo (k) fluoranthene 50 - 150 ND ND 0.667 8.00 20.00
Chrysene 50 - 150 ND ND 0.667 8.00 20.00
Fluoranthene 50 - 150 ND ND 0.667 8.00 20.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 27 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8270E (cont.)
QC Sample ID: BYH0787-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0787
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Fluorene 50 - 150 ND ND 0.667 8.00 20.00
Indeno (1,2,3-cd) pyrene 50 - 150 ND ND 0.667 8.00 20.00
Phenanthrene 50 - 150 ND ND 0.667 8.00 20.00
Pyrene 33 - 130 ND ND 0.667 8.00 20.00
QC Sample ID: BYH0787-MS2 QC Source Sample: 24H1461-05Batch: BYH0787
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Acenaphthene 47 - 145 ND ND 0.803 9.64 20.00
Acenaphthylene 50 - 150 ND ND 0.803 9.64 20.00
Anthracene 50 - 150 ND ND 0.803 9.64 20.00
Benzo (a) anthracene 50 - 150 ND ND 0.803 9.64 20.00
Benzo (a) pyrene 50 - 150 ND ND 0.803 9.64 20.00
Benzo (b) fluoranthene 50 - 150 ND ND 0.803 9.64 20.00
Benzo (g,h,i) perylene 50 - 150 ND ND 0.803 9.64 20.00
Benzo (k) fluoranthene 50 - 150 ND ND 0.803 9.64 20.00
Chrysene 50 - 150 ND ND 0.803 9.64 20.00
Fluoranthene 50 - 150 ND ND 0.803 9.64 20.00
Fluorene 50 - 150 ND ND 0.803 9.64 20.00
Indeno (1,2,3-cd) pyrene 50 - 150 ND ND 0.803 9.64 20.00
Phenanthrene 50 - 150 ND ND 0.803 9.64 20.00
Pyrene 33 - 130 ND ND 0.803 9.64 20.00
Matrix Spike Dup - EPA 8270E
QC Sample ID: BYH0787-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0787
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Acenaphthene 47 - 145 200 ND ND 0.667 8.00 20.00
Acenaphthylene 50 - 150 200 ND ND 0.667 8.00 20.00
Anthracene 50 - 150 200 ND ND 0.667 8.00 20.00
Benzo (a) anthracene 50 - 150 200 ND ND 0.667 8.00 20.00
Benzo (a) pyrene 50 - 150 200 ND ND 0.667 8.00 20.00
Benzo (b) fluoranthene 50 - 150 200 ND ND 0.667 8.00 20.00
Benzo (g,h,i) perylene 50 - 150 200 ND ND 0.667 8.00 20.00
Benzo (k) fluoranthene 50 - 150 200 ND ND 0.667 8.00 20.00
Chrysene 50 - 150 200 ND ND 0.667 8.00 20.00
Fluoranthene 50 - 150 200 ND ND 0.667 8.00 20.00
Fluorene 50 - 150 200 ND ND 0.667 8.00 20.00
Indeno (1,2,3-cd) pyrene 50 - 150 200 ND ND 0.667 8.00 20.00
Phenanthrene 50 - 150 200 ND ND 0.667 8.00 20.00
Pyrene 33 - 130 200 ND ND 0.667 8.00 20.00
QC Sample ID: BYH0787-MSD2 QC Source Sample: 24H1461-05Batch: BYH0787
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Acenaphthene 47 - 145 200 ND ND 0.803 9.64 20.00
Acenaphthylene 50 - 150 200 ND ND 0.803 9.64 20.00
Anthracene 50 - 150 200 ND ND 0.803 9.64 20.00
Benzo (a) anthracene 50 - 150 200 ND ND 0.803 9.64 20.00
Benzo (a) pyrene 50 - 150 200 ND ND 0.803 9.64 20.00
Benzo (b) fluoranthene 50 - 150 200 ND ND 0.803 9.64 20.00
Benzo (g,h,i) perylene 50 - 150 200 ND ND 0.803 9.64 20.00
Benzo (k) fluoranthene 50 - 150 200 ND ND 0.803 9.64 20.00
Chrysene 50 - 150 200 ND ND 0.803 9.64 20.00
Fluoranthene 50 - 150 200 ND ND 0.803 9.64 20.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 28 of 33
QC Report for Work Order (WO) - 24H1461
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8270E (cont.)
QC Sample ID: BYH0787-MSD2 QC Source Sample: 24H1461-05Batch: BYH0787
Date Prepared: 08/15/2024 Date Analyzed: 08/15/2024
Fluorene 50 - 150 200 ND ND 0.803 9.64 20.00
Indeno (1,2,3-cd) pyrene 50 - 150 200 ND ND 0.803 9.64 20.00
Phenanthrene 50 - 150 200 ND ND 0.803 9.64 20.00
Pyrene 33 - 130 200 ND ND 0.803 9.64 20.00
CtF WO#: 24H1461
www.ChemtechFord.com Page 29 of 33
Surrogates Report for Work Order (WO) - 24H1461
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH0801-BLK1 Bromofluorobenzene 99.8 50 BYH0801 1.00150 200 200
BYH0801-BLK1 Capric Acid 0 BYH0801 1.0010.00 500
LCS - EPA 8015 C
BYH0801-BS1 Bromofluorobenzene 105 50 BYH0801 1.00150 210 200
BYH0801-BS1 Capric Acid 0 BYH0801 1.0010.00 500
Matrix Spike - EPA 8015 C
BYH0801-MS1 Bromofluorobenzene 96.1 50 BYH0801 1.00150 231 241
BYH0801-MS1 Capric Acid 0 BYH0801 1.0010.00 602
Matrix Spike Dup - EPA 8015 C
BYH0801-MSD1 Bromofluorobenzene 100 50 BYH0801 1.00150 241 241
BYH0801-MSD1 Capric Acid 0 BYH0801 1.0010.00 602
Blank - EPA 8260D
BYH0760-BLK1 1,2-Dichloroethane-d4 109 64.2 BYH0760 1.0012610.9 10.0
BYH0760-BLK1 4-Bromofluorobenzene 95.9 71.4 BYH0760 1.001259.59 10.0
BYH0760-BLK1 Toluene-d8 100 63.2 BYH0760 1.0012910.0 10.0
BYH0786-BLK1 Toluene-d8 101 82 BYH0786 1.001260.0101 0.0100
BYH0840-BLK1 1,2-Dichloroethane-d4 99.2 70 BYH0840 1.001300.00992 0.0100
BYH0840-BLK1 Toluene-d8 100 82 BYH0840 1.001260.0100 0.0100
BYH0840-BLK1 Toluene-d8 100 70 BYH0840 1.001300.0100 0.0100
BYH0840-BLK1 4-Bromofluorobenzene 94.4 70 BYH0840 1.001300.00944 0.0100
LCS - EPA 8260D
BYH0760-BS1 1,2-Dichloroethane-d4 95.0 64.2 BYH0760 1.001269.50 10.0
BYH0760-BS1 4-Bromofluorobenzene 96.8 71.4 BYH0760 1.001259.68 10.0
BYH0760-BS1 Toluene-d8 101 63.2 BYH0760 1.0012910.1 10.0
BYH0786-BS1 1,2-Dichloroethane-d4 100 70 BYH0786 1.001300.0100 0.0100
BYH0786-BS1 Toluene-d8 101 82 BYH0786 1.001260.0101 0.0100
BYH0786-BS1 Toluene-d8 101 70 BYH0786 1.001300.0101 0.0100
BYH0786-BS1 4-Bromofluorobenzene 98.8 70 BYH0786 1.001300.00988 0.0100
BYH0840-BS1 1,2-Dichloroethane-d4 95.3 70 BYH0840 1.001300.00953 0.0100
BYH0840-BS1 Toluene-d8 100 82 BYH0840 1.001260.0100 0.0100
BYH0840-BS1 Toluene-d8 100 70 BYH0840 1.001300.0100 0.0100
BYH0840-BS1 4-Bromofluorobenzene 95.9 70 BYH0840 1.001300.00959 0.0100
Matrix Spike - EPA 8260D
BYH0760-MS1 1,2-Dichloroethane-d4 98.8 64.2 BYH0760 1.0012649.4 50.0
BYH0760-MS1 4-Bromofluorobenzene 97.2 71.4 BYH0760 1.0012548.6 50.0
BYH0760-MS1 Toluene-d8 100 63.2 BYH0760 1.0012950.0 50.0
BYH0786-MS1 1,2-Dichloroethane-d4 99.7 70 BYH0786 1.001303.00 3.01
BYH0786-MS1 Toluene-d8 99.6 70 BYH0786 1.001303.00 3.01
BYH0786-MS1 Toluene-d8 99.6 82 BYH0786 1.001263.00 3.01
BYH0786-MS1 4-Bromofluorobenzene 92.7 70 BYH0786 1.001302.79 3.01
BYH0840-MS1 1,2-Dichloroethane-d4 96.3 70 BYH0840 1.001302.41 2.50
BYH0840-MS1 Toluene-d8 101 82 BYH0840 1.001262.52 2.50
BYH0840-MS1 Toluene-d8 101 70 BYH0840 1.001302.52 2.50
BYH0840-MS1 4-Bromofluorobenzene 96.5 70 BYH0840 1.001302.41 2.50
Matrix Spike Dup - EPA 8260D
CtF WO#: 24H1461
www.ChemtechFord.com Page 30 of 33
Matrix Spike Dup - EPA 8260D (cont.)
BYH0760-MSD1 1,2-Dichloroethane-d4 99.0 64.2 BYH0760 1.0012649.5 50.0
BYH0760-MSD1 4-Bromofluorobenzene 97.1 71.4 BYH0760 1.0012548.6 50.0
BYH0760-MSD1 Toluene-d8 100 63.2 BYH0760 1.0012950.1 50.0
BYH0786-MSD1 1,2-Dichloroethane-d4 99.3 70 BYH0786 1.001302.99 3.01
BYH0786-MSD1 Toluene-d8 99.8 70 BYH0786 1.001303.01 3.01
BYH0786-MSD1 Toluene-d8 99.8 82 BYH0786 1.001263.01 3.01
BYH0786-MSD1 4-Bromofluorobenzene 95.4 70 BYH0786 1.001302.87 3.01
BYH0840-MSD1 1,2-Dichloroethane-d4 96.3 70 BYH0840 1.001302.41 2.50
BYH0840-MSD1 Toluene-d8 100 82 BYH0840 1.001262.51 2.50
BYH0840-MSD1 Toluene-d8 100 70 BYH0840 1.001302.51 2.50
BYH0840-MSD1 4-Bromofluorobenzene 97.5 70 BYH0840 1.001302.44 2.50
Blank - EPA 8270E
BYH0787-BLK1 2-Fluorobiphenyl 60.5 37 BYH0787 1.001400.202 0.333
BYH0787-BLK1 Terphenyl-dl4 43.9 31 BYH0787 1.001400.146 0.333
LCS - EPA 8270E
BYH0787-BS1 2-Fluorobiphenyl 52.8 37 BYH0787 1.001400.176 0.333
BYH0787-BS1 Terphenyl-dl4 43.1 31 BYH0787 1.001400.144 0.333
Matrix Spike - EPA 8270E
BYH0787-MS2 2-Fluorobiphenyl 36.2 37 BYH0787 20.001400.145 0.402
BYH0787-MS1 2-Fluorobiphenyl 36.8 37 BYH0787 20.001400.123 0.333
BYH0787-MS2 Terphenyl-dl4 37.6 31 BYH0787 20.001400.151 0.402
BYH0787-MS1 Terphenyl-dl4 6.16 31 BYH0787 20.001400.0205 0.333
Matrix Spike Dup - EPA 8270E
BYH0787-MSD1 2-Fluorobiphenyl 29.0 37 BYH0787 20.001400.0968 0.333
BYH0787-MSD2 2-Fluorobiphenyl 46.0 37 BYH0787 20.001400.185 0.402
BYH0787-MSD1 Terphenyl-dl4 5.16 31 BYH0787 20.001400.0172 0.333
BYH0787-MSD2 Terphenyl-dl4 40.5 31 BYH0787 20.001400.163 0.402
CtF WO#: 24H1461
www.ChemtechFord.com Page 31 of 33
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24H1461-01 Capric Acid 0.00 0 1640
24H1461-01 Bromofluorobenzene 206 80.4 50 150256
MBTEXN-GRO by 5035
24H1461-01 Toluene-d8 0.0490 99.3 82 1260.0493
DRO with silica gel cleanup
24H1461-02 Bromofluorobenzene 215 80.4 50 150267
24H1461-02 Capric Acid 0.00 0 1668
MBTEXN-GRO by 5035
24H1461-02 Toluene-d8 0.0640 101 82 1260.0636
DRO with silica gel cleanup
24H1461-03 Bromofluorobenzene 208 82.4 50 150253
24H1461-03 Capric Acid 0.00 0 1631
MBTEXN-GRO by 5035
24H1461-03 Toluene-d8 0.0688 100 82 1260.0686
DRO with silica gel cleanup
24H1461-04 Bromofluorobenzene 210 84.1 50 150249
24H1461-04 Capric Acid 0.00 0 1623
MBTEXN-GRO by 5035
24H1461-04 Toluene-d8 0.0670 102 82 1260.0654
8260 TPH Fractionation
24H1461-05 1,2-Dichloroethane-d4 0.0755 120 70 1300.0628
24H1461-05 4-Bromofluorobenzene 0.0595 94.8 70 1300.0628
24H1461-05 Toluene-d8 0.0634 101 70 1300.0628
8270 TPH Fractionation
24H1461-05 2-Fluorobiphenyl 0.228 56.7 37 1400.402
24H1461-05 Terphenyl-dl4 0.156 38.8 31 1400.402
DRO with silica gel cleanup
24H1461-05 Capric Acid 0.00 0 1602
24H1461-05 Bromofluorobenzene 200 82.9 50 150241
MBTEXN-GRO by 5035
24H1461-05 Toluene-d8 0.0634 101 82 1260.0628
DRO with silica gel cleanup
24H1461-06 Bromofluorobenzene 201 80.9 50 150248
24H1461-06 Capric Acid 0.00 0 1620
MBTEXN-GRO by 5035
24H1461-06 Toluene-d8 0.0559 100 82 1260.0558
DRO with silica gel cleanup
24H1461-07 Capric Acid 0.00 0 1611
CtF WO#: 24H1461
www.ChemtechFord.com Page 32 of 33
24H1461-07 Bromofluorobenzene 193 79.1 50 150244
MBTEXN-GRO by 5035
24H1461-07 Toluene-d8 0.0621 101 82 1260.0616
8260 TPH Fractionation
24H1461-08 1,2-Dichloroethane-d4 3.03 102 70 1302.96
24H1461-08 4-Bromofluorobenzene 3.15 106 70 1302.96
24H1461-08 Toluene-d8 2.89 97.5 70 1302.96
8270 TPH Fractionation
24H1461-08 2-Fluorobiphenyl 0.181 45.8 37 1400.395
24H1461-08 Terphenyl-dl4 0.152 38.5 31 1400.395
DRO with silica gel cleanup
24H1461-08 Bromofluorobenzene 205 86.5 50 150237
24H1461-08 Capric Acid 0.00 0 1592
MBTEXN-GRO by 5035
24H1461-08 Toluene-d8 2.89 97.5 82 1262.96
8260 Low Level Volatiles
24H1461-09 Toluene-d8 125 99.8 63.2 129125
24H1461-09 1,2-Dichloroethane-d4 127 102 64.2 126125
24H1461-09 4-Bromofluorobenzene 118 94.7 71.4 125125
CtF WO#: 24H1461
www.ChemtechFord.com Page 33 of 33
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24I1821
Project: Former Sommers Auto Wrecking
9/23/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 25
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24I1821-01 EXC-1-1
24I1821-02 EXC-1-2
24I1821-03 EXC-1-3
24I1821-04 EXC-1-4
24I1821-05 EXC-1-5
24I1821-06 EXC-1-6
24I1821-07 EXC-1-7
24I1821-08 EXC-1-8
24I1821-09 EXC-1-9
24I1821-10 EXC-1-10
24I1821-11 EXC-1-11
24I1821-12 EXC-1-12
24I1821-13 EXC-1-13
24I1821-14 EXC-1-130
24I1821-15 EXC-1-14
24I1821-16 EXC-1-15
24I1821-17 EXC-1-16
24I1821-18 EXC-1-160
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
Page 2 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-1
Lab ID: 24I1821-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 8:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800094.9Total Solids
Metals
mg/kg dry 9/23/249/20/245.23 EPA 6020A/3050B131Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 3 of 24Page 3 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-2
Lab ID: 24I1821-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 8:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800098.1Total Solids
Metals
mg/kg dry 9/23/249/20/243.86 EPA 6020A/3050B628Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 4 of 24Page 4 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-3
Lab ID: 24I1821-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800092.2Total Solids
Metals
mg/kg dry 9/23/249/20/246.48 EPA 6020A/3050B159Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 5 of 24Page 5 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-4
Lab ID: 24I1821-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:05
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800098.1Total Solids
Metals
mg/kg dry 9/23/249/20/245.44 EPA 6020A/3050B629Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 6 of 24Page 6 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-5
Lab ID: 24I1821-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800097.6Total Solids
Metals
mg/kg dry 9/23/249/20/245.26 EPA 6020A/3050B599Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 7 of 24Page 7 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-6
Lab ID: 24I1821-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:15
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800096.6Total Solids
Metals
mg/kg dry 9/23/249/20/245.64 EPA 6020A/3050B198Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 8 of 24Page 8 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-7
Lab ID: 24I1821-07Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:20
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800098.5Total Solids
Metals
mg/kg dry 9/23/249/20/245.18 EPA 6020A/3050B279Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 9 of 24Page 9 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-8
Lab ID: 24I1821-08Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:25
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800098.3Total Solids
Metals
mg/kg dry 9/23/249/20/244.36 EPA 6020A/3050B112Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 10 of 24Page 10 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-9
Lab ID: 24I1821-09Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:30
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800096.6Total Solids
Metals
mg/kg dry 9/23/249/20/245.42 EPA 6020A/3050B141Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 11 of 24Page 11 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-10
Lab ID: 24I1821-10Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:35
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800097.6Total Solids
Metals
mg/kg dry 9/23/249/20/244.85 EPA 6020A/3050B223Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 12 of 24Page 12 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-11
Lab ID: 24I1821-11Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:40
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800097.6Total Solids
Metals
mg/kg dry 9/23/249/20/245.73 EPA 6020A/3050B309Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 13 of 24Page 13 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-12
Lab ID: 24I1821-12Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:45
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800097.0Total Solids
Metals
mg/kg dry 9/23/249/20/245.26 EPA 6020A/3050B536Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 14 of 24Page 14 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-13
Lab ID: 24I1821-13Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800098.0Total Solids
Metals
mg/kg dry 9/23/249/20/243.26 EPA 6020A/3050B303Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 15 of 24Page 15 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-130
Lab ID: 24I1821-14Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:52
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800097.5Total Solids
Metals
mg/kg dry 9/23/249/20/245.39 EPA 6020A/3050B420Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 16 of 24Page 16 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-14
Lab ID: 24I1821-15Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 9:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800096.9Total Solids
Metals
mg/kg dry 9/23/249/20/245.51 EPA 6020A/3050B411Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 17 of 24Page 17 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-15
Lab ID: 24I1821-16Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 10:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800095.4Total Solids
Metals
mg/kg dry 9/23/249/20/245.70 EPA 6020A/3050B272Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 18 of 24Page 18 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-16
Lab ID: 24I1821-17Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 10:05
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800096.9Total Solids
Metals
mg/kg dry 9/23/249/20/245.79 EPA 6020A/3050B188Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 19 of 24Page 19 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-160
Lab ID: 24I1821-18Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 9/20/24 10:07
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%9/20/249/20/240.1 CTF800098.1Total Solids
Metals
mg/kg dry 9/23/249/20/245.54 EPA 6020A/3050B213Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 20 of 24Page 20 of 25
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
9/20/24 10:40 @ 15.5 °C
9/23/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Project Name: Former Sommers Auto Wrecking CtF WO#: 24I1821
www.ChemtechFord.com
Page 21 of 24Page 21 of 25
Page 22 of 25
Page 23 of 25
QC Report for Work Order (WO) - 24I1821
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYI0999-DUP1 QC Source Sample: 24I1821-01Batch: BYI0999
Date Prepared: 09/20/2024 Date Analyzed: 09/20/2024
Total Solids 0.543 20 95.4 94.9 0.1 1.00
CtF WO#: 24I1821
www.ChemtechFord.com Page 24 of 25
QC Report for Work Order (WO) - 24I1821
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6020A
QC Sample ID: BYI0979-BLK1 Batch: BYI0979
Date Prepared: 09/20/2024 Date Analyzed: 09/20/2024
Lead, Total ND 0.060 1.00
Matrix Spike - EPA 6020A
QC Sample ID: BYI0979-MS1 QC Source Sample: 24I1821-01Batch: BYI0979
Date Prepared: 09/20/2024 Date Analyzed: 09/23/2024
Lead, Total 50.5 75 - 125 139 131 17.4 5.22 20.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Matrix Spike Dup - EPA 6020A
QC Sample ID: BYI0979-MSD1 QC Source Sample: 24I1821-01Batch: BYI0979
Date Prepared: 09/20/2024 Date Analyzed: 09/23/2024
Lead, Total 83.6 3.96 75 - 125 20 145 131 17.2 5.17 20.00
Reference - EPA 6020A
QC Sample ID: BYI0979-SRM1 Batch: BYI0979
Date Prepared: 09/20/2024 Date Analyzed: 09/20/2024
Lead, Total 80.7 63.16 - 121.4 199 247 0.346 1.00
CtF WO#: 24I1821
www.ChemtechFord.com Page 25 of 25
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H2214
Project: Former Sommers Auto Wrecking
8/27/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 31
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H2214-01 EXC-3-N
24H2214-02 EXC-3-E
24H2214-03 EXC-3-S
24H2214-04 EXC-3-W
24H2214-05 EXC-3-Floor
24H2214-06 EXC-3-Floor 10
24H2214-07 Equipment Blank
24H2214-08 EXC-4-NE2
24H2214-09 EXC-1-Comp
24H2214-10 Trip Blank
24H2214-11 Frack Tank 2
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria, except as noted by qualifying flags. Batches
BYH1199 and BYH1214 for method 8260D and LCS recoveries outside of the control limits for several compounds. It is
important to note that certain flags on an individual analyte do not constitute failure of the method as a whole. EPA
methodologies recognize that it may not be possible for every compound to meet all recovery or percent difference criteria .
The batch passed required method criteria for these analytes.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
Page 2 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-N
Lab ID: 24H2214-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800078.6Total Solids
Metals
mg/kg dry 8/26/248/23/240.047 EPA 6020A/3050B15.9Arsenic, Total
mg/kg dry 8/26/248/23/240.056 EPA 6020A/3050B121Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 3 of 30Page 3 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-E
Lab ID: 24H2214-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:05
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800082.0Total Solids
Metals
mg/kg dry 8/26/248/23/240.043 EPA 6020A/3050B16.2Arsenic, Total
mg/kg dry 8/26/248/23/240.102 EPA 6020A/3050B183Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 4 of 30Page 4 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-S
Lab ID: 24H2214-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800092.3Total Solids
Metals
mg/kg dry 8/26/248/23/240.085 EPA 6020A/3050B21.4Arsenic, Total
mg/kg dry 8/26/248/23/240.511 EPA 6020A/3050B766Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 5 of 30Page 5 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-W
Lab ID: 24H2214-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:15
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800095.5Total Solids
Metals
mg/kg dry 8/26/248/23/240.082 EPA 6020A/3050B15.5Arsenic, Total
mg/kg dry 8/26/248/23/240.098 EPA 6020A/3050B120Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 6 of 30Page 6 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-Floor
Lab ID: 24H2214-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:20
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800086.6Total Solids
Metals
mg/kg dry 8/26/248/23/240.084 EPA 6020A/3050B11.0Arsenic, Total
mg/kg dry 8/26/248/23/240.101 EPA 6020A/3050B47.5Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 7 of 30Page 7 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-Floor 10
Lab ID: 24H2214-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:25
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800084.7Total Solids
Metals
mg/kg dry 8/26/248/23/240.107 EPA 6020A/3050B11.6Arsenic, Total
mg/kg dry 8/26/248/23/240.128 EPA 6020A/3050B107Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 8 of 30Page 8 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Equipment Blank
Lab ID: 24H2214-07Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:45
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Metals
mg/L 8/27/248/26/240.0005 EPA 6020A/3010ANDArsenic, Total
mg/L 8/27/248/26/240.0006 EPA 6020A/3010ANDLead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 9 of 30Page 9 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-NE2
Lab ID: 24H2214-08Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 13:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/23/248/23/2461EPA 8015 C296Diesel Range Organics
Inorganic
%8/23/248/23/240.1 CTF800082.5Total Solids
MBTEXn
mg/kg dry 8/23/248/23/240.12 EPA 8260D/5030BNDBenzene
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDEthylbenzene
mg/kg dry J-LOW-L8/23/248/23/240.18 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDNaphthalene
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDToluene
mg/kg dry 8/23/248/23/240.91 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/kg dry 8/23/248/23/243.03 EPA 8260B/C 5035A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 10 of 30Page 10 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-Comp
Lab ID: 24H2214-09Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 15:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800096.9Total Solids
Metals
mg/kg dry 8/26/248/23/240.085 EPA 6020A/3050B10.3Arsenic, Total
mg/kg dry 8/26/248/23/240.103 EPA 6020A/3050B290Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 11 of 30Page 11 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24H2214-10Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 12:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 8/23/248/23/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L J-LOW-L8/23/248/23/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 8/23/248/23/2420.0 EPA 8260D/5030BNDAcetone
ug/L 8/23/248/23/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 8/23/248/23/240.4 EPA 8260D/5030BNDBenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030B2.4Bromodichloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromoform
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDBromomethane
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 12 of 30Page 12 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24H2214-10Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 12:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030B8.0Chloroform
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L J-LOW-C8/23/248/23/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDibromochloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDibromomethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 8/23/248/23/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 8/23/248/23/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L 8/23/248/23/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDNaphthalene
ug/L 8/23/248/23/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDStyrene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDToluene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 8/23/248/23/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 8/23/248/23/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 13 of 30Page 13 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Frack Tank 2
Lab ID: 24H2214-11Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/23/24 10:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
mg/L 8/23/248/23/2420SM 2540 C1030Total Dissolved Solids (TDS)
Metals
mg/L 8/27/248/26/240.0005 EPA 6020A/3010A0.0870Arsenic, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 14 of 30Page 14 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-C = Estimated low due to low recovery of CCV
J-LOW-L = Estimated low due to low recovery of LCS
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 15 of 30Page 15 of 31
Page 16 of 31
Page 17 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYH1184-DUP1 QC Source Sample: XXXXXXX-XXBatch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.158 20 81.5 81.6 0.1 1.00
QC Sample ID: BYH1184-DUP2 QC Source Sample: 24H2214-01Batch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.625 20 79.1 78.6 0.1 1.00
QC Sample ID: BYH1184-DUP3 QC Source Sample: 24H2214-08Batch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.483 20 82.1 82.5 0.1 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 18 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6020A
QC Sample ID: BYH1194-BLK1 Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total ND 0.050 1.00
Lead, Total ND 0.060 1.00
QC Sample ID: BYH1238-BLK1 Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total ND 0.0005 1.00
Lead, Total ND 0.0006 1.00
LCS - EPA 6020A
QC Sample ID: BYH1238-BS1 Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 96.1 85 - 115 0.038 0.0400 0.0005 1.00
Lead, Total 94.0 85 - 115 0.038 0.0400 0.0006 1.00
Matrix Spike - EPA 6020A
QC Sample ID: BYH1194-MS1 QC Source Sample: 24H2214-01Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 141 75 - 125 23.6 15.9 5.49 0.069 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Lead, Total 844 75 - 125 168 121 5.49 0.082 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1238-MS1 QC Source Sample: 24H2214-11Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 90.4 70 - 130 0.123 0.087 0.0400 0.0005 1.00
Lead, Total 88.0 70 - 130 0.052 0.016 0.0400 0.0006 1.00
Matrix Spike Dup - EPA 6020A
QC Sample ID: BYH1194-MSD1 QC Source Sample: 24H2214-01Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 121 5.90 75 - 125 20 22.3 15.9 5.30 0.066 1.00
Lead, Total 899 0.791 75 - 125 20 169 121 5.30 0.079 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1238-MSD1 QC Source Sample: 24H2214-11Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 91.9 0.497 70 - 130 20 0.124 0.087 0.0400 0.0005 1.00
Lead, Total 86.6 1.13 70 - 130 20 0.051 0.016 0.0400 0.0006 1.00
Reference - EPA 6020A
QC Sample ID: BYH1194-SRM1 Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 108 77.78 - 144.3 72.0 66.6 0.177 1.00
Lead, Total 86.2 63.16 - 121.4 213 247 0.213 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 19 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH1227-BLK1 Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics ND 50 1.00
LCS - EPA 8015 C
QC Sample ID: BYH1227-BS1 Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 106 50 - 150 2120 2000 50 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH1227-MS1 QC Source Sample: 24H2214-08Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 105 50 - 150 2840 296 2430 61 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH1227-MSD1 QC Source Sample: 24H2214-08Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 94.3 9.56 50 - 150 20 2580 296 2430 61 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 20 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH1199-BLK1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.4 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 1.0 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 21 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYH1199-BLK1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 1.0 1.00
n-Butyl Alcohol ND 50.0 1.00
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 1.0 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 3.0 1.00
QC Sample ID: BYH1214-BLK1 Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 111 70 - 130 11.1 10.0 1.0 1.00
1,1,1-Trichloroethane 117 70 - 130 11.7 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 106 70 - 130 10.6 10.0 1.0 1.00
1,1,2-Trichloroethane 102 70 - 130 10.2 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 120 70 - 130 12.0 10.0 1.0 1.00
1,1-Dichloroethane 120 70 - 130 12.0 10.0 1.0 1.00
1,1-Dichloroethene 107 70 - 130 10.7 10.0 1.0 1.00
1,1-Dichloropropene 111 70 - 130 11.1 10.0 1.0 1.00
1,2,3-Trichlorobenzene 120 70 - 130 12.0 10.0 1.0 1.00
1,2,3-Trichloropropane 115 70 - 130 11.5 10.0 1.0 1.00
1,2,4-Trichlorobenzene 110 70 - 130 11.0 10.0 1.0 1.00
1,2,4-Trimethylbenzene 110 70 - 130 11.0 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 110 70 - 130 11.0 10.0 1.0 1.00
1,2-Dibromoethane (EDB)106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dichlorobenzene 111 70 - 130 11.1 10.0 1.0 1.00
1,2-Dichloroethane 106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dichloropropane 106 70 - 130 10.6 10.0 1.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 22 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,3,5-Trimethylbenzene 109 70 - 130 10.9 10.0 1.0 1.00
1,3-Dichlorobenzene 117 70 - 130 11.7 10.0 1.0 1.00
1,3-Dichloropropane 114 70 - 130 11.4 10.0 1.0 1.00
1,4-Dichlorobenzene 106 70 - 130 10.6 10.0 1.0 1.00
2,2-Dichloropropane 112 70 - 130 11.2 10.0 1.0 1.00
2-Chlorotoluene 114 70 - 130 11.4 10.0 1.0 1.00
2-Hexanone 132 70 - 130 13.2 10.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
2-Nitropropane 49.2 70 - 130 14.8 30.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
4-Chlorotoluene 114 70 - 130 11.4 10.0 1.0 1.00
Acetone 95.5 70 - 130 95.5 100 20.0 1.00
Acrylonitrile 108 70 - 130 53.9 50.0 5.0 1.00
Benzene 112 70 - 130 11.2 10.0 0.4 1.00
Bromobenzene 109 70 - 130 10.9 10.0 1.0 1.00
Bromochloromethane 116 70 - 130 11.6 10.0 1.0 1.00
Bromodichloromethane 98.9 70 - 130 9.89 10.0 1.0 1.00
Bromoform 109 70 - 130 10.9 10.0 1.0 1.00
Bromomethane 176 70 - 130 17.6 10.0 2.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 139 70 - 130 13.9 10.0 2.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Tetrachloride 114 70 - 130 11.4 10.0 1.0 1.00
Chlorobenzene 109 70 - 130 10.9 10.0 1.0 1.00
Chloroethane 124 70 - 130 12.4 10.0 1.0 1.00
Chloroform 108 70 - 130 10.8 10.0 1.0 1.00
Chloromethane 146 70 - 130 14.6 10.0 1.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
cis-1,2-Dichloroethene 113 70 - 130 11.3 10.0 1.0 1.00
cis-1,3-Dichloropropene 108 70 - 130 10.8 10.0 1.0 1.00
Cyclohexanone 34.5 70 - 130 34.5 100 10.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Dibromochloromethane 115 70 - 130 11.5 10.0 1.0 1.00
Dibromomethane 112 70 - 130 11.2 10.0 1.0 1.00
Dichlorodifluoromethane 143 70 - 130 14.3 10.0 1.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Acetate 102 70 - 130 20.4 20.0 2.0 1.00
Ethyl Ether 108 70 - 130 10.8 10.0 1.0 1.00
Ethylbenzene 111 70 - 130 11.1 10.0 1.0 1.00
Hexachlorobutadiene 117 70 - 130 11.7 10.0 1.0 1.00
Isobutanol 174 70 - 130 348 200 20.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 104 70 - 130 10.4 10.0 1.0 1.00
Methyl Ethyl Ketone 151 70 - 130 15.1 10.0 2.0 1.00
J-High-L - Analyte estimated high based on LCS recovery
Methyl Isobutyl Ketone 91.6 70 - 130 9.16 10.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 23 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Methylene Chloride 104 70 - 130 10.4 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)182 70 - 130 18.2 10.0 0.6 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 112 70 - 130 11.2 10.0 1.0 1.00
n-Butyl Alcohol 77.4 70 - 130 77.4 100 50.0 1.00
n-Butylbenzene 111 70 - 130 11.1 10.0 1.0 1.00
n-Propyl Benzene 110 70 - 130 11.0 10.0 1.0 1.00
Pentachloroethane 94.1 70 - 130 9.41 10.0 1.0 1.00
p-Isopropyltoluene 115 70 - 130 11.5 10.0 1.0 1.00
sec-Butyl Benzene 112 70 - 130 11.2 10.0 1.0 1.00
Styrene 108 70 - 130 10.8 10.0 1.0 1.00
tert-Butylbenzene 107 70 - 130 10.7 10.0 1.0 1.00
Tetrachloroethene 118 70 - 130 11.8 10.0 1.0 1.00
Toluene 100 70 - 130 10.0 10.0 1.0 1.00
trans-1,2-Dichloroethene 116 70 - 130 11.6 10.0 1.0 1.00
trans-1,3-Dichloropropene 107 70 - 130 10.7 10.0 1.0 1.00
Trichloroethene 120 70 - 130 12.0 10.0 1.0 1.00
Trichlorofluoromethane 118 70 - 130 11.8 10.0 1.0 1.00
Vinyl Chloride 162 70 - 130 16.2 10.0 0.8 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 107 70 - 130 32.2 30.0 3.0 1.00
QC Sample ID: BYH1214-BS1 Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 115 70 - 130 0.01 0.0100 0.0004 1.00
Ethylbenzene 118 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)52.1 70 - 130 0.005 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 105 70 - 130 0.01 0.0100 0.001 1.00
Toluene 112 70 - 130 0.01 0.0100 0.001 1.00
Xylenes, total 121 70 - 130 0.04 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 108 70 - 130 54.0 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 106 70 - 130 53.2 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 106 70 - 130 52.8 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 106 70 - 130 53.2 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 112 70 - 130 56.2 ND 50.0 5.0 1.00
1,1-Dichloroethane 111 70 - 130 55.3 ND 50.0 5.0 1.00
1,1-Dichloroethene 97.5 70 - 130 48.8 ND 50.0 5.0 1.00
1,1-Dichloropropene 104 70 - 130 52.2 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 110 70 - 130 55.1 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 117 70 - 130 58.6 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 99.3 70 - 130 49.6 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 106 70 - 130 53.0 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 100 70 - 130 50.2 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)110 70 - 130 54.9 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 107 70 - 130 53.4 ND 50.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 24 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,2-Dichloroethane 107 70 - 130 53.4 ND 50.0 5.0 1.00
1,2-Dichloropropane 102 70 - 130 50.8 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 99.0 70 - 130 49.5 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 109 70 - 130 54.6 ND 50.0 5.0 1.00
1,3-Dichloropropane 116 70 - 130 58.2 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 103 70 - 130 51.6 ND 50.0 5.0 1.00
2,2-Dichloropropane 99.4 70 - 130 49.7 ND 50.0 5.0 1.00
2-Chlorotoluene 107 70 - 130 53.3 ND 50.0 5.0 1.00
2-Hexanone 132 70 - 130 65.8 ND 50.0 50.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
2-Nitropropane 53.4 70 - 130 80.1 ND 150 10.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
4-Chlorotoluene 105 70 - 130 52.4 ND 50.0 5.0 1.00
Acetone 89.6 70 - 130 448 ND 500 100 1.00
Acrylonitrile 109 70 - 130 271 ND 250 25.0 1.00
Benzene 108 70 - 130 54.0 ND 50.0 2.0 1.00
Bromobenzene 102 70 - 130 51.2 ND 50.0 5.0 1.00
Bromochloromethane 114 70 - 130 57.0 ND 50.0 5.0 1.00
Bromodichloromethane 98.8 70 - 130 49.4 ND 50.0 5.0 1.00
Bromoform 115 70 - 130 57.3 ND 50.0 5.0 1.00
Bromomethane 167 70 - 130 83.7 ND 50.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 128 70 - 130 64.1 ND 50.0 10.0 1.00
Carbon Tetrachloride 106 70 - 130 53.0 ND 50.0 5.0 1.00
Chlorobenzene 105 70 - 130 52.7 ND 50.0 5.0 1.00
Chloroethane 116 70 - 130 58.0 ND 50.0 5.0 1.00
Chloroform 102 70 - 130 51.2 ND 50.0 5.0 1.00
Chloromethane 135 70 - 130 67.4 ND 50.0 5.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
cis-1,2-Dichloroethene 105 70 - 130 52.7 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 98.7 70 - 130 49.4 ND 50.0 5.0 1.00
Cyclohexanone 25.2 70 - 130 126 ND 500 50.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Dibromochloromethane 113 70 - 130 56.4 ND 50.0 5.0 1.00
Dibromomethane 112 70 - 130 56.1 ND 50.0 5.0 1.00
Dichlorodifluoromethane 129 70 - 130 64.5 ND 50.0 5.0 1.00
Ethyl Acetate 107 70 - 130 107 ND 100 10.0 1.00
Ethyl Ether 103 70 - 130 51.6 ND 50.0 5.0 1.00
Ethylbenzene 106 70 - 130 53.2 ND 50.0 5.0 1.00
Hexachlorobutadiene 107 70 - 130 53.5 ND 50.0 5.0 1.00
Isobutanol 147 70 - 130 1470 ND 1000 100 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 99.2 70 - 130 49.6 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 159 70 - 130 79.4 ND 50.0 10.0 1.00
MS-High - Estimated high due to Matrix Spike recovery.
Methyl Isobutyl Ketone 112 70 - 130 55.8 ND 50.0 25.0 1.00
Methylene Chloride 97.1 70 - 130 48.6 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)192 70 - 130 95.9 ND 50.0 3.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 25 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 104 70 - 130 51.8 ND 50.0 5.0 1.00
n-Butyl Alcohol 84.5 70 - 130 422 ND 500 250 1.00
n-Butylbenzene 98.4 70 - 130 49.2 ND 50.0 5.0 1.00
n-Propyl Benzene 103 70 - 130 51.6 ND 50.0 5.0 1.00
Pentachloroethane 93.7 70 - 130 46.8 ND 50.0 5.0 1.00
p-Isopropyltoluene 103 70 - 130 51.7 ND 50.0 5.0 1.00
sec-Butyl Benzene 102 70 - 130 50.8 ND 50.0 5.0 1.00
Styrene 105 70 - 130 52.3 ND 50.0 5.0 1.00
tert-Butylbenzene 102 70 - 130 50.8 ND 50.0 5.0 1.00
Tetrachloroethene 106 70 - 130 53.2 ND 50.0 5.0 1.00
Toluene 97.9 70 - 130 49.0 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 107 70 - 130 53.5 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 104 70 - 130 52.0 ND 50.0 5.0 1.00
Trichloroethene 115 70 - 130 57.4 ND 50.0 5.0 1.00
Trichlorofluoromethane 110 70 - 130 55.0 ND 50.0 5.0 1.00
Vinyl Chloride 150 70 - 130 75.2 ND 50.0 4.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 102 70 - 130 154 ND 150 15.0 1.00
QC Sample ID: BYH1214-MS1 QC Source Sample: 24H2214-08Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 101 70 - 130 3.06 ND 3.03 0.12 1.00
Ethylbenzene 102 50 - 150 3.10 ND 3.03 0.30 1.00
Methyl tert-Butyl Ether (MTBE)55.4 50 - 150 1.68 ND 3.03 0.18 1.00
Naphthalene 102 50 - 150 3.11 ND 3.03 0.30 1.00
Toluene 98.3 70 - 130 2.98 ND 3.03 0.30 1.00
Xylenes, total 107 70 - 130 9.72 ND 9.10 0.91 1.00
QC Sample ID: BYH1214-MS2 QC Source Sample: XXXXXXX-XXBatch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 103 70 - 130 0.28 ND 0.271 0.01 1.00
Ethylbenzene 101 50 - 150 0.27 ND 0.271 0.03 1.00
Methyl tert-Butyl Ether (MTBE)55.6 50 - 150 0.15 ND 0.271 0.02 1.00
Naphthalene 110 50 - 150 0.30 ND 0.271 0.03 1.00
Toluene 100 70 - 130 0.27 ND 0.271 0.03 1.00
Xylenes, total 106 70 - 130 0.86 ND 0.813 0.08 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 108 0.278 70 - 130 20 53.9 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 101 5.41 70 - 130 20 50.4 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 106 0.754 70 - 130 20 53.2 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 102 4.12 70 - 130 20 51.0 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 106 5.86 70 - 130 20 53.0 ND 50.0 5.0 1.00
1,1-Dichloroethane 104 6.34 70 - 130 20 51.9 ND 50.0 5.0 1.00
1,1-Dichloroethene 89.7 8.33 70 - 130 20 44.8 ND 50.0 5.0 1.00
1,1-Dichloropropene 99.2 5.20 70 - 130 20 49.6 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 115 4.26 70 - 130 20 57.5 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 117 0.0854 70 - 130 20 58.6 ND 50.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 26 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,2,4-Trichlorobenzene 105 5.68 70 - 130 20 52.6 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 101 5.02 70 - 130 20 50.4 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 107 6.64 70 - 130 20 53.6 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)111 1.09 70 - 130 20 55.5 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 104 2.56 70 - 130 20 52.1 ND 50.0 5.0 1.00
1,2-Dichloroethane 106 0.658 70 - 130 20 53.0 ND 50.0 5.0 1.00
1,2-Dichloropropane 98.5 3.00 70 - 130 20 49.2 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 96.9 2.14 70 - 130 20 48.4 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 99.4 9.49 70 - 130 20 49.7 ND 50.0 5.0 1.00
1,3-Dichloropropane 112 3.58 70 - 130 20 56.2 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 118 13.4 70 - 130 20 59.0 ND 50.0 5.0 1.00
2,2-Dichloropropane 99.0 0.403 70 - 130 20 49.5 ND 50.0 5.0 1.00
2-Chlorotoluene 90.1 16.8 70 - 130 20 45.0 ND 50.0 5.0 1.00
2-Hexanone 122 7.89 70 - 130 20 60.8 ND 50.0 50.0 1.00
2-Nitropropane 60.0 11.6 70 - 130 20 90.0 ND 150 10.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
4-Chlorotoluene 104 0.767 70 - 130 20 52.0 ND 50.0 5.0 1.00
Acetone 89.4 0.268 70 - 130 20 447 ND 500 100 1.00
Acrylonitrile 108 0.647 70 - 130 20 270 ND 250 25.0 1.00
Benzene 103 4.74 70 - 130 20 51.4 ND 50.0 2.0 1.00
Bromobenzene 99.1 3.18 70 - 130 20 49.6 ND 50.0 5.0 1.00
Bromochloromethane 112 1.86 70 - 130 20 56.0 ND 50.0 5.0 1.00
Bromodichloromethane 96.4 2.46 70 - 130 20 48.2 ND 50.0 5.0 1.00
Bromoform 110 4.19 70 - 130 20 55.0 ND 50.0 5.0 1.00
Bromomethane 171 2.30 70 - 130 20 85.6 ND 50.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 122 5.28 70 - 130 20 60.8 ND 50.0 10.0 1.00
Carbon Tetrachloride 101 4.73 70 - 130 20 50.6 ND 50.0 5.0 1.00
Chlorobenzene 105 0.285 70 - 130 20 52.6 ND 50.0 5.0 1.00
Chloroethane 107 8.25 70 - 130 20 53.4 ND 50.0 5.0 1.00
Chloroform 96.8 5.62 70 - 130 20 48.4 ND 50.0 5.0 1.00
Chloromethane 125 7.47 70 - 130 20 62.5 ND 50.0 5.0 1.00
cis-1,2-Dichloroethene 99.0 6.26 70 - 130 20 49.5 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 100 1.51 70 - 130 20 50.1 ND 50.0 5.0 1.00
Cyclohexanone 21.2 17.3 70 - 130 20 106 ND 500 50.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Dibromochloromethane 114 0.883 70 - 130 20 56.8 ND 50.0 5.0 1.00
Dibromomethane 110 2.34 70 - 130 20 54.8 ND 50.0 5.0 1.00
Dichlorodifluoromethane 116 10.4 70 - 130 20 58.2 ND 50.0 5.0 1.00
Ethyl Acetate 104 2.46 70 - 130 20 104 ND 100 10.0 1.00
Ethyl Ether 103 0.486 70 - 130 20 51.4 ND 50.0 5.0 1.00
Ethylbenzene 101 5.31 70 - 130 20 50.4 ND 50.0 5.0 1.00
Hexachlorobutadiene 104 2.94 70 - 130 20 52.0 ND 50.0 5.0 1.00
Isobutanol 141 4.22 70 - 130 20 1410 ND 1000 100 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 93.4 6.02 70 - 130 20 46.7 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 142 11.2 70 - 130 20 70.9 ND 50.0 10.0 1.00
MS-High - Estimated high due to Matrix Spike recovery.
Methyl Isobutyl Ketone 104 7.25 70 - 130 20 51.8 ND 50.0 25.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 27 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Methylene Chloride 93.9 3.35 70 - 130 20 47.0 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)202 4.93 70 - 130 20 101 ND 50.0 3.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 112 7.62 70 - 130 20 55.8 ND 50.0 5.0 1.00
n-Butyl Alcohol 86.4 2.32 70 - 130 20 432 ND 500 250 1.00
n-Butylbenzene 98.2 0.203 70 - 130 20 49.1 ND 50.0 5.0 1.00
n-Propyl Benzene 98.1 4.97 70 - 130 20 49.0 ND 50.0 5.0 1.00
Pentachloroethane 88.9 5.26 70 - 130 20 44.4 ND 50.0 5.0 1.00
p-Isopropyltoluene 93.0 10.6 70 - 130 20 46.5 ND 50.0 5.0 1.00
sec-Butyl Benzene 97.6 3.92 70 - 130 20 48.8 ND 50.0 5.0 1.00
Styrene 103 1.44 70 - 130 20 51.6 ND 50.0 5.0 1.00
tert-Butylbenzene 99.5 2.09 70 - 130 20 49.8 ND 50.0 5.0 1.00
Tetrachloroethene 99.3 6.81 70 - 130 20 49.6 ND 50.0 5.0 1.00
Toluene 95.8 2.17 70 - 130 20 47.9 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 99.2 7.57 70 - 130 20 49.6 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 104 0.288 70 - 130 20 52.2 ND 50.0 5.0 1.00
Trichloroethene 108 6.65 70 - 130 20 53.8 ND 50.0 5.0 1.00
Trichlorofluoromethane 98.8 10.7 70 - 130 20 49.4 ND 50.0 5.0 1.00
Vinyl Chloride 140 6.81 70 - 130 20 70.2 ND 50.0 4.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 100 2.27 70 - 130 20 150 ND 150 15.0 1.00
QC Sample ID: BYH1214-MSD1 QC Source Sample: 24H2214-08Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 97.6 3.23 70 - 130 20 2.96 ND 3.03 0.12 1.00
Ethylbenzene 96.8 5.52 50 - 150 25 2.93 ND 3.03 0.30 1.00
Methyl tert-Butyl Ether (MTBE)59.1 6.46 50 - 150 25 1.79 ND 3.03 0.18 1.00
Naphthalene 96.6 5.93 50 - 150 25 2.93 ND 3.03 0.30 1.00
Toluene 95.0 3.41 70 - 130 20 2.88 ND 3.03 0.30 1.00
Xylenes, total 101 5.18 70 - 130 20 9.23 ND 9.10 0.91 1.00
QC Sample ID: BYH1214-MSD2 QC Source Sample: XXXXXXX-XXBatch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 102 3.89 70 - 130 20 0.27 ND 0.264 0.01 1.00
Ethylbenzene 98.7 4.63 50 - 150 25 0.26 ND 0.264 0.03 1.00
Methyl tert-Butyl Ether (MTBE)57.2 0.217 50 - 150 25 0.15 ND 0.264 0.02 1.00
Naphthalene 117 3.53 50 - 150 25 0.31 ND 0.264 0.03 1.00
Toluene 98.3 4.63 70 - 130 20 0.26 ND 0.264 0.03 1.00
Xylenes, total 104 4.72 70 - 130 20 0.82 ND 0.792 0.08 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 28 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - SM 2540 C
QC Sample ID: BYH1211-BLK1 Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)ND 10 1.00
Duplicate - SM 2540 C
QC Sample ID: BYH1211-DUP1 QC Source Sample: XXXXXXX-XXBatch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)0.8 10 1260 1250 20 1.00
QC Sample ID: BYH1211-DUP2 QC Source Sample: 24H2214-11Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)2 10 1010 1030 20 1.00
LCS - SM 2540 C
QC Sample ID: BYH1211-BS1 Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)102 90 - 110 408 400 20 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 29 of 31
Surrogates Report for Work Order (WO) - 24H2214
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH1227-BLK1 Bromofluorobenzene 101 50 BYH1227 1.00150 203 200
BYH1227-BLK1 Capric Acid 0 BYH1227 1.0010.00 500
LCS - EPA 8015 C
BYH1227-BS1 Bromofluorobenzene 118 50 BYH1227 1.00150 236 200
BYH1227-BS1 Capric Acid 0 BYH1227 1.0010.00 500
Matrix Spike - EPA 8015 C
BYH1227-MS1 Bromofluorobenzene 100 50 BYH1227 1.00150 243 243
BYH1227-MS1 Capric Acid 0 BYH1227 1.0010.00 606
Matrix Spike Dup - EPA 8015 C
BYH1227-MSD1 Bromofluorobenzene 99.5 50 BYH1227 1.00150 241 243
BYH1227-MSD1 Capric Acid 0 BYH1227 1.0010.00 606
Blank - EPA 8260D
BYH1199-BLK1 1,2-Dichloroethane-d4 102 64.2 BYH1199 1.0012610.2 10.0
BYH1199-BLK1 4-Bromofluorobenzene 99.0 71.4 BYH1199 1.001259.90 10.0
BYH1199-BLK1 Toluene-d8 94.6 63.2 BYH1199 1.001299.46 10.0
BYH1214-BLK1 Toluene-d8 100 82 BYH1214 1.001260.0100 0.0100
LCS - EPA 8260D
BYH1199-BS1 1,2-Dichloroethane-d4 96.4 64.2 BYH1199 1.001269.64 10.0
BYH1199-BS1 4-Bromofluorobenzene 98.1 71.4 BYH1199 1.001259.81 10.0
BYH1199-BS1 Toluene-d8 91.1 63.2 BYH1199 1.001299.11 10.0
BYH1214-BS1 Toluene-d8 99.9 82 BYH1214 1.001260.00999 0.0100
Matrix Spike - EPA 8260D
BYH1199-MS1 1,2-Dichloroethane-d4 100 64.2 BYH1199 1.0012650.1 50.0
BYH1199-MS1 4-Bromofluorobenzene 95.5 71.4 BYH1199 1.0012547.8 50.0
BYH1199-MS1 Toluene-d8 92.8 63.2 BYH1199 1.0012946.4 50.0
BYH1214-MS1 Toluene-d8 101 82 BYH1214 1.001263.06 3.03
BYH1214-MS2 Toluene-d8 102 82 BYH1214 1.001260.276 0.271
Matrix Spike Dup - EPA 8260D
BYH1199-MSD1 1,2-Dichloroethane-d4 102 64.2 BYH1199 1.0012650.9 50.0
BYH1199-MSD1 4-Bromofluorobenzene 98.8 71.4 BYH1199 1.0012549.4 50.0
BYH1199-MSD1 Toluene-d8 91.8 63.2 BYH1199 1.0012945.9 50.0
BYH1214-MSD1 Toluene-d8 101 82 BYH1214 1.001263.07 3.03
BYH1214-MSD2 Toluene-d8 101 82 BYH1214 1.001260.268 0.264
CtF WO#: 24H2214
www.ChemtechFord.com Page 30 of 31
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24H2214-08 Capric Acid 0.00 0 1606
24H2214-08 Bromofluorobenzene 165 68.2 50 150243
MBTEXN-GRO
24H2214-08 Toluene-d8 3.08 102 82 1263.03
8260 Low Level Volatiles
24H2214-10 Toluene-d8 9.56 95.6 63.2 12910.0
24H2214-10 4-Bromofluorobenzene 9.61 96.1 71.4 12510.0
24H2214-10 1,2-Dichloroethane-d4 10.2 102 64.2 12610.0
CtF WO#: 24H2214
www.ChemtechFord.com Page 31 of 31
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H1959
Project: Former Sommers Auto Wrecking
8/22/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 22
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H1959-01 EXC-2-N
24H1959-02 EXC-2-E
24H1959-03 EXC-2-SE
24H1959-04 EXC-2-S
24H1959-05 EXC-2-W
24H1959-06 EXC-2-Floor
24H1959-07 EXC-2-W2
24H1959-08 Frac Tank
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order, with the following exceptions: Arsenic and Lead were observed above the MRL in
BYH1068-BLK1. The concentration in the method blank is less than 10% of the sample result, which is negligible
according to method criteria.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria. Batch BYH1050 had low LCS recoveries for MTBE.
It is important to note that certain flags on an individual analyte do not constitute failure of the method as a whole. EPA
methodologies recognize that it may not be possible for every compound to meet all recovery or percent difference criteria .
The batch passed required method criteria for these analytes.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
Page 2 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-N
Lab ID: 24H1959-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:40
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800092.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.089 EPA 6020A/3050B24.4Arsenic, Total
mg/kg dry B8/22/248/21/240.107 EPA 6020A/3050B668Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 3 of 22Page 3 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-E
Lab ID: 24H1959-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:45
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800088.8Total Solids
Metals
mg/kg dry B8/22/248/21/240.051 EPA 6020A/3050B21.9Arsenic, Total
mg/kg dry B8/22/248/21/240.609 EPA 6020A/3050B643Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 4 of 22Page 4 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-SE
Lab ID: 24H1959-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800086.9Total Solids
Metals
mg/kg dry B8/22/248/21/240.082 EPA 6020A/3050B22.6Arsenic, Total
mg/kg dry B8/22/248/21/240.099 EPA 6020A/3050B165Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 5 of 22Page 5 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-S
Lab ID: 24H1959-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800097.2Total Solids
Metals
mg/kg dry B8/22/248/21/240.073 EPA 6020A/3050B12.6Arsenic, Total
mg/kg dry B8/22/248/21/240.087 EPA 6020A/3050B312Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 6 of 22Page 6 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-W
Lab ID: 24H1959-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800094.4Total Solids
Metals
mg/kg dry B8/22/248/21/240.064 EPA 6020A/3050B16.8Arsenic, Total
mg/kg dry B8/22/248/21/240.077 EPA 6020A/3050B352Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 7 of 22Page 7 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-Floor
Lab ID: 24H1959-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:05
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800083.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.057 EPA 6020A/3050B16.6Arsenic, Total
mg/kg dry B8/22/248/21/240.068 EPA 6020A/3050B221Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 8 of 22Page 8 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-W2
Lab ID: 24H1959-07Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800094.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.094 EPA 6020A/3050B13.9Arsenic, Total
mg/kg dry B8/22/248/21/240.113 EPA 6020A/3050B293Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 9 of 22Page 9 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: Frac Tank
Lab ID: 24H1959-08Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/21/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 8/21/248/21/241.0 EPA 8015 CNDDiesel Range Organics
Inorganic
mg/L 8/22/248/21/246EPA 1664BNDOil & Grease (HEM)
pH Units SPH8/22/24 13:568/22/24 12:040.1 SM 4500 H-B1.9pH
mg/L 8/21/248/21/24100SM 2540 C1300Total Dissolved Solids (TDS)
mg/L 8/21/248/21/244SM 2540 D4Total Suspended Solids (TSS)
mg/L 8/22/248/21/246EPA 1664BNDTRPH (SGT-HEM)
Metals
mg/L 8/22/248/21/240.0005 EPA 6020A/3010A0.149Arsenic, Total
mg/L 8/22/248/21/240.0030 EPA 6020A/3010A0.607Barium, Total
mg/L 8/22/248/21/240.0010 EPA 6020A/3010A0.0035Chromium, Total
mg/L 8/22/248/21/240.0009 EPA 6020A/3010A0.0019Copper, Total
mg/L 8/22/248/21/240.0006 EPA 6020A/3010A0.0031Lead, Total
mg/L 8/22/248/21/240.0100 EPA 6020A/3010ANDZinc, Total
MBTEXn
mg/L 8/21/248/21/240.005 EPA 8260D/5030BNDBenzene
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L J-LOW-L8/21/248/21/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDToluene
mg/L 8/21/248/21/240.038 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/L 8/21/248/21/240.125 EPA 8260B/C 5030A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 10 of 22Page 10 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
B = Analyte is found in the associated blank as well as in the sample (CLP B-flag).
J-LOW-L = Estimated low due to low recovery of LCS
SPH = Sample submitted past method specified holding time.
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 11 of 22Page 11 of 22
Zn
,
Pb
,
As
,
B
a
,
Cr
,
Cu
ad
d
e
d
pe
r
Bl
a
k
e
Do
w
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y
em
a
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.
-
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-
8/
2
2
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Page 12 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYH1082-DUP1 QC Source Sample: 24H1959-01Batch: BYH1082
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Solids 0.834 20 93.3 92.5 0.1 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 13 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 1664B
QC Sample ID: BYH1063-BLK1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)ND 5 1.00
TRPH (SGT-HEM)ND 5 1.00
LCS - EPA 1664B
QC Sample ID: BYH1063-BS1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)87.8 78 - 114 35 40.0 5 1.00
TRPH (SGT-HEM)88.5 64 - 132 18 20.0 5 1.00
LCS Dup - EPA 1664B
QC Sample ID: BYH1063-BSD1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)83.8 4.66 78 - 114 18 34 40.0 5 1.00
TRPH (SGT-HEM)84.0 5.22 64 - 132 34 17 20.0 5 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 14 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6020A
QC Sample ID: BYH1068-BLK1 Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 0.106 0.050 1.00
QB-01 - The method blank contains analyte at a concentration above the MRL; however, concentration is less than 10% of the
sample result, which is negligible according to method criteria.
Lead, Total 0.110 0.060 1.00
QB-01 - The method blank contains analyte at a concentration above the MRL; however, concentration is less than 10% of the
sample result, which is negligible according to method criteria.
QC Sample ID: BYH1069-BLK1 Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total ND 0.0005 1.00
Barium, Total ND 0.0030 1.00
Chromium, Total ND 0.0010 1.00
Copper, Total ND 0.0009 1.00
Lead, Total ND 0.0006 1.00
Zinc, Total ND 0.0100 1.00
LCS - EPA 6020A
QC Sample ID: BYH1069-BS2 Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 99.0 85 - 115 0.396 0.400 0.0050 1.00
Barium, Total 99.9 85 - 115 0.400 0.400 0.0300 1.00
Chromium, Total 97.1 85 - 115 0.388 0.400 0.0100 1.00
Copper, Total 98.7 85 - 115 0.395 0.400 0.0090 1.00
Lead, Total 97.2 85 - 115 0.389 0.400 0.0060 1.00
Zinc, Total 108 85 - 115 0.434 0.400 0.100 1.00
Matrix Spike - EPA 6020A
QC Sample ID: BYH1068-MS2 QC Source Sample: 24H1959-01Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 17.7 75 - 125 25.5 24.4 6.10 0.076 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 298 75 - 125 686 668 6.10 0.092 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1069-MS1 QC Source Sample: 24H1959-08Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 89.8 70 - 130 0.221 0.149 0.0800 0.0005 1.00
Barium, Total 102 70 - 130 0.689 0.607 0.0800 0.0030 1.00
Chromium, Total 92.8 70 - 130 0.078 0.004 0.0800 0.0010 1.00
Copper, Total 81.4 70 - 130 0.067 0.002 0.0800 0.0009 1.00
Lead, Total 90.5 70 - 130 0.076 0.003 0.0800 0.0006 1.00
Zinc, Total 75.3 70 - 130 0.069 0.009 0.0800 0.0100 1.00
Matrix Spike Dup - EPA 6020A
QC Sample ID: BYH1068-MSD2 QC Source Sample: 24H1959-01Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 67.3 10.8 75 - 125 20 28.4 24.4 5.92 0.074 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 366 0.503 75 - 125 20 689 668 5.92 0.089 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
CtF WO#: 24H1959
www.ChemtechFord.com Page 15 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 6020A (cont.)
QC Sample ID: BYH1069-MSD1 QC Source Sample: 24H1959-08Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 93.3 1.26 70 - 130 20 0.224 0.149 0.0800 0.0005 1.00
Barium, Total 115 1.41 70 - 130 20 0.699 0.607 0.0800 0.0030 1.00
Chromium, Total 96.6 3.83 70 - 130 20 0.081 0.004 0.0800 0.0010 1.00
Copper, Total 84.3 3.37 70 - 130 20 0.069 0.002 0.0800 0.0009 1.00
Lead, Total 93.4 3.00 70 - 130 20 0.078 0.003 0.0800 0.0006 1.00
Zinc, Total 78.1 3.19 70 - 130 20 0.071 0.009 0.0800 0.0100 1.00
Reference - EPA 6020A
QC Sample ID: BYH1068-SRM1 Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 106 77.78 - 144.3 70.5 66.6 0.099 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 85.7 63.16 - 121.4 212 247 0.119 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
CtF WO#: 24H1959
www.ChemtechFord.com Page 16 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH1124-BLK1 Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics ND 1.0 1.00
LCS - EPA 8015 C
QC Sample ID: BYH1124-BS1 Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 109 50 - 150 44 40.0 1.0 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH1124-MS1 QC Source Sample: 24H1959-08Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 100 50 - 150 40 ND 40.0 1.0 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH1124-MSD1 QC Source Sample: 24H1959-08Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 108 7.11 50 - 150 20 43 ND 40.0 1.0 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 17 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH1050-BLK1 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH1050-BLK2 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene ND 0.100 1.00
Ethylbenzene ND 0.250 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.150 1.00
Naphthalene ND 0.250 1.00
Toluene ND 0.250 1.00
Xylenes, total ND 0.750 1.00
LCS - EPA 8260D
QC Sample ID: BYH1050-BS1 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 96.6 70 - 130 0.010 0.0100 0.0004 1.00
Ethylbenzene 105 70 - 130 0.011 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)50.3 70 - 130 0.005 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 124 70 - 130 0.012 0.0100 0.001 1.00
Toluene 96.6 70 - 130 0.010 0.0100 0.001 1.00
Xylenes, total 110 70 - 130 0.033 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH1050-MS2 QC Source Sample: 24H1959-08Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 88.9 70 - 130 0.111 ND 0.125 0.005 1.00
Ethylbenzene 89.2 70 - 130 0.112 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)62.7 70 - 130 0.078 ND 0.125 0.008 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Naphthalene 95.3 70 - 130 0.119 ND 0.125 0.012 1.00
Toluene 88.6 70 - 130 0.111 ND 0.125 0.012 1.00
Xylenes, total 94.9 70 - 130 0.356 ND 0.375 0.038 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH1050-MSD2 QC Source Sample: 24H1959-08Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 87.4 1.70 70 - 130 20 0.109 ND 0.125 0.005 1.00
Ethylbenzene 90.1 1.00 70 - 130 25 0.113 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)54.8 13.4 70 - 130 25 0.068 ND 0.125 0.008 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Naphthalene 92.0 3.52 70 - 130 25 0.115 ND 0.125 0.012 1.00
Toluene 87.2 1.59 70 - 130 20 0.109 ND 0.125 0.012 1.00
Xylenes, total 93.3 1.70 70 - 130 20 0.350 ND 0.375 0.038 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 18 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - SM 2540 C
QC Sample ID: BYH1067-BLK1 Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)ND 10 1.00
Duplicate - SM 2540 C
QC Sample ID: BYH1067-DUP1 QC Source Sample: 24H1959-08Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)0 10 1300 1300 100 1.00
LCS - SM 2540 C
QC Sample ID: BYH1067-BS1 Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)97 90 - 110 388 400 20 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 19 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
QC Sample ID: BYH1081-BLK1 Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)ND 1 1.00
QC Sample ID: BYH1081-DUP1 QC Source Sample: 24H1959-08Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)11.8 20 3 4 4 1.00
QC Sample ID: BYH1081-DUP2 QC Source Sample: XXXXXXX-XXBatch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)20.7 20 5 6 4 1.00
QM-020 - The RPD and/or percent recovery for this QC spike sample cannot be accurately calculated due to the low
concentration of analyte inherent in the sample. The batch was accepted based on acceptable LCS recovery.
QC Sample ID: BYH1081-SRM1 Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)91.0 80 - 120 91 100 10 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 20 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - SM 4500 H-B
QC Sample ID: BYH1104-DUP1 QC Source Sample: 24H1959-08Batch: BYH1104
Date Prepared: 08/22/2024 Date Analyzed: 08/22/2024
pH 1.60 3 1.9 1.9 0.1 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 21 of 22
Surrogates Report for Work Order (WO) - 24H1959
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH1124-BLK1 Bromofluorobenzene 78.4 50 BYH1124 1.001503.14 4.00
BYH1124-BLK1 Capric Acid 0 BYH1124 1.0010.00 10.0
LCS - EPA 8015 C
BYH1124-BS1 Bromofluorobenzene 80.1 50 BYH1124 1.001503.21 4.00
BYH1124-BS1 Capric Acid 0 BYH1124 1.0010.00 10.0
Matrix Spike - EPA 8015 C
BYH1124-MS1 Bromofluorobenzene 126 50 BYH1124 1.001505.06 4.00
BYH1124-MS1 Capric Acid 0 BYH1124 1.0010.00 10.0
Matrix Spike Dup - EPA 8015 C
BYH1124-MSD1 Bromofluorobenzene 125 50 BYH1124 1.001505.01 4.00
BYH1124-MSD1 Capric Acid 0 BYH1124 1.0010.00 10.0
Blank - EPA 8260D
BYH1050-BLK2 Toluene-d8 102 83.3 BYH1050 1.001222.55 2.50
BYH1050-BLK1 Toluene-d8 102 83.3 BYH1050 1.001220.0102 0.0100
LCS - EPA 8260D
BYH1050-BS1 Toluene-d8 101 83.3 BYH1050 1.001220.0101 0.0100
Matrix Spike - EPA 8260D
BYH1050-MS2 Toluene-d8 104 83.3 BYH1050 1.001220.130 0.125
BYH1050-MS1 Toluene-d8 102 83.3 BYH1050 1.001222.54 2.50
Matrix Spike Dup - EPA 8260D
BYH1050-MSD2 Toluene-d8 103 83.3 BYH1050 1.001220.129 0.125
BYH1050-MSD1 Toluene-d8 103 83.3 BYH1050 1.001222.56 2.50
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24H1959-08 Capric Acid 0.00 0 110.0
24H1959-08 Bromofluorobenzene 4.94 123 50 1504.00
MBTEXN-GRO
24H1959-08 Toluene-d8 0.129 103 83.3 1220.125
CtF WO#: 24H1959
www.ChemtechFord.com Page 22 of 22
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H1665
Project: Former Sommers Auto Wrecking
8/21/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 30
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H1665-01 EXC-4-West 4
24H1665-02 EXC-4- NE
24H1665-03 EXC-4- East 2
24H1665-04 EXC-4- Floor 4
24H1665-05 EXC-4- Floor 40
24H1665-06 EXC-4- Floor 5
24H1665-07 EXC-4-GW1
24H1665-08 EXC-4-GW2
24H1665-09 Trip Blank
24H1665-10 Equipment Blank
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
Page 2 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-West 4
Lab ID: 24H1665-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 9:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/20/248/19/2463EPA 8015 C3640Diesel Range Organics
Inorganic
%8/20/248/20/240.1 CTF800078.8Total Solids
BETX Compounds
mg/kg dry 8/20/248/20/2431.7 EPA 8260D/5035A229C5-C6 Aliphatic hydrocarbons
mg/kg dry 8/20/248/20/2431.7 EPA 8260D/5035A313C7-C8 Aliphatic hydrocarbons
mg/kg dry 8/20/248/20/2431.7 EPA 8260D/5035A453C9-C10 Aliphatic hydrocarbons
mg/kg dry 8/20/248/20/2431.7 EPA 8260D/5035A1420C9-C10 Alkyl Benzenes
MBTEXn
mg/kg dry 8/20/248/20/241.27 EPA 8260D/5035A4.41Benzene
mg/kg dry 8/20/248/20/243.17 EPA 8260D/5035A103Ethylbenzene
mg/kg dry 8/20/248/20/241.90 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/20/248/20/243.17 EPA 8260D/5035A28.1Naphthalene
mg/kg dry 8/20/248/20/243.17 EPA 8260D/5035ANDToluene
mg/kg dry 8/20/248/20/249.52 EPA 8260D/5035A604Xylenes, total
Gasoline Range
mg/kg dry 8/20/248/20/2431.7 EPA 8260B/C 5035A/[CALC]3150Gasoline Range Organics
Semi-Volatile Compounds
mg/kg dry 8/20/248/20/240.76 EPA 8270E/3570165C11-12 Aliphatic hydrocarbons
mg/kg dry 8/20/248/20/240.76 EPA 8270E/357046.6C13-C16 Aliphatic hydrocarbons
mg/kg dry 8/20/248/20/240.76 EPA 8270E/357035.0C17-C21 Aliphatic hydrocarbons
mg/kg dry 8/20/248/20/240.76 EPA 8270E/357035.8C22-C35 Aliphatic hydrocarbons
mg/kg dry 8/20/248/20/240.76 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 8/20/248/20/240.76 EPA 8270E/35701.92Total C12-C22 PAH
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDAcenaphthene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDAnthracene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDChrysene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDFluoranthene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDFluorene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDPhenanthrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 3 of 30Page 3 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-West 4 (cont.)
Lab ID: 24H1665-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 9:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Semi-Volatile Compounds (cont.)
mg/kg dry 8/20/248/20/241.52 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 4 of 30Page 4 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4- NE
Lab ID: 24H1665-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 10:15
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/20/248/19/2463EPA 8015 C10000Diesel Range Organics
Inorganic
%8/20/248/20/240.1 CTF800079.0Total Solids
MBTEXn
mg/kg dry 8/19/248/19/240.13 EPA 8260D/5035ANDBenzene
mg/kg dry 8/19/248/19/240.32 EPA 8260D/5035ANDEthylbenzene
mg/kg dry J-LOW-C8/19/248/19/240.19 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/19/248/19/240.32 EPA 8260D/5035A0.61Naphthalene
mg/kg dry 8/19/248/19/240.32 EPA 8260D/5035ANDToluene
mg/kg dry 8/19/248/19/240.95 EPA 8260D/5035ANDXylenes, total
Gasoline Range
mg/kg dry 8/19/248/19/243.16 EPA 8260B/C 5035A/[CALC]19.5Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 5 of 30Page 5 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4- East 2
Lab ID: 24H1665-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 10:30
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/20/248/19/2464EPA 8015 CNDDiesel Range Organics
Inorganic
%8/20/248/20/240.1 CTF800078.5Total Solids
MBTEXn
mg/kg dry 8/20/248/20/240.002 EPA 8260D/5035ANDBenzene
mg/kg dry 8/20/248/20/240.006 EPA 8260D/5035ANDEthylbenzene
mg/kg dry J-LOW-C8/20/248/20/240.004 EPA 8260D/5035A0.007Methyl tert-Butyl Ether (MTBE)
mg/kg dry 8/20/248/20/240.006 EPA 8260D/5035ANDNaphthalene
mg/kg dry 8/20/248/20/240.006 EPA 8260D/5035ANDToluene
mg/kg dry 8/20/248/20/240.02 EPA 8260D/5035ANDXylenes, total
Gasoline Range
mg/kg dry 8/20/248/20/240.0599 EPA 8260B/C 5035A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 6 of 30Page 6 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4- Floor 4
Lab ID: 24H1665-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 10:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/20/248/19/2463EPA 8015 CNDDiesel Range Organics
Inorganic
%8/20/248/20/240.1 CTF800078.8Total Solids
MBTEXn
mg/kg dry 8/21/248/21/240.002 EPA 8260D/5035ANDBenzene
mg/kg dry 8/21/248/21/240.006 EPA 8260D/5035A0.008Ethylbenzene
mg/kg dry J-LOW-C8/21/248/21/240.003 EPA 8260D/5035A0.004Methyl tert-Butyl Ether (MTBE)
mg/kg dry 8/21/248/21/240.006 EPA 8260D/5035A0.01Naphthalene
mg/kg dry 8/21/248/21/240.006 EPA 8260D/5035ANDToluene
mg/kg dry 8/21/248/21/240.02 EPA 8260D/5035A0.07Xylenes, total
Gasoline Range
mg/kg dry 8/21/248/21/240.0558 EPA 8260B/C 5035A/[CALC]0.889Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 7 of 30Page 7 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4- Floor 40
Lab ID: 24H1665-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/20/248/19/2463EPA 8015 CNDDiesel Range Organics
Inorganic
%8/20/248/20/240.1 CTF800079.8Total Solids
MBTEXn
mg/kg dry ISTD-018/21/248/21/240.002 EPA 8260D/5035ANDBenzene
mg/kg dry ISTD-018/21/248/21/240.005 EPA 8260D/5035ANDEthylbenzene
mg/kg dry ISTD-01,
J-LOW-C
8/21/248/21/240.003 EPA 8260D/5035A0.005Methyl tert-Butyl Ether (MTBE)
mg/kg dry ISTD-018/21/248/21/240.005 EPA 8260D/5035ANDNaphthalene
mg/kg dry ISTD-018/21/248/21/240.005 EPA 8260D/5035ANDToluene
mg/kg dry ISTD-018/21/248/21/240.02 EPA 8260D/5035A0.02Xylenes, total
Gasoline Range
mg/kg dry 8/21/248/21/240.0500 EPA 8260B/C 5035A/[CALC]0.154Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 8 of 30Page 8 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4- Floor 5
Lab ID: 24H1665-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 11:20
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/20/248/19/2462EPA 8015 CNDDiesel Range Organics
Inorganic
%8/20/248/20/240.1 CTF800081.2Total Solids
MBTEXn
mg/kg dry 8/20/248/20/240.002 EPA 8260D/5035A0.01Benzene
mg/kg dry 8/20/248/20/240.006 EPA 8260D/5035A0.06Ethylbenzene
mg/kg dry 8/20/248/20/240.004 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/20/248/20/240.006 EPA 8260D/5035A0.07Naphthalene
mg/kg dry 8/20/248/20/240.006 EPA 8260D/5035A0.08Toluene
mg/kg dry 8/20/248/20/240.02 EPA 8260D/5035A0.66Xylenes, total
Gasoline Range
mg/kg dry 8/20/248/20/240.0610 EPA 8260B/C 5035A/[CALC]4.38Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 9 of 30Page 9 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-GW1
Lab ID: 24H1665-07Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 13:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 8/21/248/20/241.0 EPA 8015 CNDDiesel Range Organics
MBTEXn
mg/L 8/19/248/19/240.005 EPA 8260D/5030B0.008Benzene
mg/L 8/19/248/19/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L 8/19/248/19/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 8/19/248/19/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 8/19/248/19/240.012 EPA 8260D/5030B0.014Toluene
mg/L 8/19/248/19/240.038 EPA 8260D/5030B0.115Xylenes, total
Gasoline Range
mg/L 8/19/248/19/240.125 EPA 8260B/C 5030A/[CALC]0.345Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 10 of 30Page 10 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-GW2
Lab ID: 24H1665-08Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 13:20
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 8/21/248/20/241.0 EPA 8015 CNDDiesel Range Organics
MBTEXn
mg/L 8/19/248/19/240.005 EPA 8260D/5030B0.008Benzene
mg/L 8/19/248/19/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L 8/19/248/19/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 8/19/248/19/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 8/19/248/19/240.012 EPA 8260D/5030B0.014Toluene
mg/L 8/19/248/19/240.038 EPA 8260D/5030B0.118Xylenes, total
Gasoline Range
mg/L 8/19/248/19/240.125 EPA 8260B/C 5030A/[CALC]0.351Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 11 of 30Page 11 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24H1665-09Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 8/20/248/20/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L J-LOW-L8/20/248/20/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 8/20/248/20/2420.0 EPA 8260D/5030BNDAcetone
ug/L 8/20/248/20/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 8/20/248/20/240.4 EPA 8260D/5030BNDBenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDBromodichloromethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDBromoform
ug/L J-LOW-L8/20/248/20/242.0 EPA 8260D/5030BNDBromomethane
ug/L J-LOW-L8/20/248/20/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 12 of 30Page 12 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24H1665-09Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BNDChloroethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDChloroform
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BNDChloromethane
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L 8/20/248/20/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDDibromochloromethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDDibromomethane
ug/L J-LOW-C8/20/248/20/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 8/20/248/20/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 8/20/248/20/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 8/20/248/20/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 8/20/248/20/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L J-LOW-C8/20/248/20/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDNaphthalene
ug/L 8/20/248/20/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDStyrene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDToluene
ug/L J-LOW-L8/20/248/20/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 8/20/248/20/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L J-LOW-C8/20/248/20/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L J-LOW-C8/20/248/20/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 8/20/248/20/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 13 of 30Page 13 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Sample ID: Equipment Blank
Lab ID: 24H1665-10Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/19/24 13:30
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 8/21/248/20/241.0 EPA 8015 CNDDiesel Range Organics
MBTEXn
mg/L 8/19/248/19/240.005 EPA 8260D/5030BNDBenzene
mg/L 8/19/248/19/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L 8/19/248/19/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 8/19/248/19/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 8/19/248/19/240.012 EPA 8260D/5030BNDToluene
mg/L 8/19/248/19/240.038 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/L 8/19/248/19/240.125 EPA 8260B/C 5030A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 14 of 30Page 14 of 30
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-0026
8/19/24 15:19 @ 2.8 °C
8/21/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
ISTD-01 = Re-analysis confirms failing internal standard due to matrix interference.
J-LOW-C = Estimated low due to low recovery of CCV
J-LOW-L = Estimated low due to low recovery of LCS
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1665
www.ChemtechFord.com
Page 15 of 30Page 15 of 30
Page 16 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYH0971-DUP1 QC Source Sample: 24H1665-01Batch: BYH0971
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Total Solids 0.821 20 78.2 78.8 0.1 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 17 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH0914-BLK1 Batch: BYH0914
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Diesel Range Organics ND 50 1.00
QC Sample ID: BYH0992-BLK1 Batch: BYH0992
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Diesel Range Organics ND 1.0 1.00
LCS - EPA 8015 C
QC Sample ID: BYH0914-BS1 Batch: BYH0914
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Diesel Range Organics 100 50 - 150 2000 2000 50 1.00
QC Sample ID: BYH0992-BS1 Batch: BYH0992
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Diesel Range Organics 107 50 - 150 43 40.0 1.0 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH0914-MS1 QC Source Sample: 24H1665-01Batch: BYH0914
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Diesel Range Organics 9.88 50 - 150 3890 3640 2540 63 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
QC Sample ID: BYH0992-MS1 QC Source Sample: 24H1665-07Batch: BYH0992
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Diesel Range Organics 100 50 - 150 40 ND 40.0 1.0 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH0914-MSD1 QC Source Sample: 24H1665-01Batch: BYH0914
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Diesel Range Organics -5.29 10.4 50 - 150 20 3510 3640 2540 63 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
QC Sample ID: BYH0992-MSD1 QC Source Sample: 24H1665-07Batch: BYH0992
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Diesel Range Organics 98.8 1.59 50 - 150 20 40 ND 40.0 1.0 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 18 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH0909-BLK1 Batch: BYH0909
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH0932-BLK1 Batch: BYH0932
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH0980-BLK1 Batch: BYH0980
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.4 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 19 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYH0980-BLK1 Batch: BYH0980
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 1.0 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 1.0 1.00
n-Butyl Alcohol ND 50.0 1.00
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 1.0 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 3.0 1.00
QC Sample ID: BYH0981-BLK1 Batch: BYH0981
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Benzene ND 0.0004 1.00
C5-C6 Aliphatic hydrocarbons ND 0.01 1.00
C7-C8 Aliphatic hydrocarbons ND 0.01 1.00
C9-C10 Aliphatic hydrocarbons ND 0.01 1.00
C9-C10 Alkyl Benzenes ND 0.01 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 20 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYH0981-BLK1 Batch: BYH0981
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH1035-BLK1 Batch: BYH1035
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYH0909-BS1 Batch: BYH0909
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Benzene 104 70 - 130 0.010 0.0100 0.0004 1.00
Ethylbenzene 112 70 - 130 0.011 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)110 70 - 130 0.011 0.0100 0.0006 1.00
Naphthalene 109 70 - 130 0.011 0.0100 0.001 1.00
Toluene 106 70 - 130 0.011 0.0100 0.001 1.00
Xylenes, total 116 70 - 130 0.035 0.0300 0.003 1.00
QC Sample ID: BYH0932-BS1 Batch: BYH0932
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Benzene 99.6 70 - 130 0.01 0.0100 0.0004 1.00
Ethylbenzene 100 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)40.1 70 - 130 0.004 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 108 70 - 130 0.01 0.0100 0.001 1.00
Toluene 96.0 70 - 130 0.01 0.0100 0.001 1.00
Xylenes, total 108 70 - 130 0.03 0.0300 0.003 1.00
QC Sample ID: BYH0980-BS1 Batch: BYH0980
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
1,1,1,2-Tetrachloroethane 93.4 70 - 130 9.34 10.0 1.0 1.00
1,1,1-Trichloroethane 74.1 70 - 130 7.41 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 95.8 70 - 130 9.58 10.0 1.0 1.00
1,1,2-Trichloroethane 90.8 70 - 130 9.08 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 62.7 70 - 130 6.27 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
1,1-Dichloroethane 74.5 70 - 130 7.45 10.0 1.0 1.00
1,1-Dichloroethene 55.8 70 - 130 5.58 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
1,1-Dichloropropene 64.6 70 - 130 6.46 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
1,2,3-Trichlorobenzene 103 70 - 130 10.3 10.0 1.0 1.00
1,2,3-Trichloropropane 92.8 70 - 130 9.28 10.0 1.0 1.00
1,2,4-Trichlorobenzene 102 70 - 130 10.2 10.0 1.0 1.00
1,2,4-Trimethylbenzene 88.0 70 - 130 8.80 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 94.2 70 - 130 9.42 10.0 1.0 1.00
1,2-Dibromoethane (EDB)87.1 70 - 130 8.71 10.0 1.0 1.00
1,2-Dichlorobenzene 92.8 70 - 130 9.28 10.0 1.0 1.00
1,2-Dichloroethane 76.5 70 - 130 7.65 10.0 1.0 1.00
1,2-Dichloropropane 78.6 70 - 130 7.86 10.0 1.0 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 21 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH0980-BS1 Batch: BYH0980
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
1,3,5-Trimethylbenzene 84.6 70 - 130 8.46 10.0 1.0 1.00
1,3-Dichlorobenzene 93.4 70 - 130 9.34 10.0 1.0 1.00
1,3-Dichloropropane 87.0 70 - 130 8.70 10.0 1.0 1.00
1,4-Dichlorobenzene 92.5 70 - 130 9.25 10.0 1.0 1.00
2,2-Dichloropropane 54.6 70 - 130 5.46 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
2-Chlorotoluene 79.9 70 - 130 7.99 10.0 1.0 1.00
2-Hexanone 97.5 70 - 130 9.75 10.0 10.0 1.00
J - Detected but below the Reporting Limit; therefore, result is an estimated concentration (CLP J-Flag).
2-Nitropropane 63.2 70 - 130 19.0 30.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
4-Chlorotoluene 80.6 70 - 130 8.06 10.0 1.0 1.00
Acetone 90.2 70 - 130 90.2 100 20.0 1.00
Acrylonitrile 86.5 70 - 130 43.3 50.0 5.0 1.00
Benzene 78.1 70 - 130 7.81 10.0 0.4 1.00
Bromobenzene 85.8 70 - 130 8.58 10.0 1.0 1.00
Bromochloromethane 80.0 70 - 130 8.00 10.0 1.0 1.00
Bromodichloromethane 82.2 70 - 130 8.22 10.0 1.0 1.00
Bromoform 89.2 70 - 130 8.92 10.0 1.0 1.00
Bromomethane 51.0 70 - 130 5.10 10.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Carbon Disulfide 50.6 70 - 130 5.06 10.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Carbon Tetrachloride 76.7 70 - 130 7.67 10.0 1.0 1.00
Chlorobenzene 85.2 70 - 130 8.52 10.0 1.0 1.00
Chloroethane 67.2 70 - 130 6.72 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Chloroform 70.2 70 - 130 7.02 10.0 1.0 1.00
Chloromethane 54.2 70 - 130 5.42 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
cis-1,2-Dichloroethene 64.2 70 - 130 6.42 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
cis-1,3-Dichloropropene 87.6 70 - 130 8.76 10.0 1.0 1.00
Cyclohexanone 109 70 - 130 109 100 10.0 1.00
Dibromochloromethane 86.6 70 - 130 8.66 10.0 1.0 1.00
Dibromomethane 93.5 70 - 130 9.35 10.0 1.0 1.00
Dichlorodifluoromethane 12.8 70 - 130 1.28 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Ethyl Acetate 88.8 70 - 130 17.8 20.0 2.0 1.00
Ethyl Ether 74.7 70 - 130 7.47 10.0 1.0 1.00
Ethylbenzene 77.5 70 - 130 7.75 10.0 1.0 1.00
Hexachlorobutadiene 89.9 70 - 130 8.99 10.0 1.0 1.00
Isobutanol 87.8 70 - 130 176 200 20.0 1.00
Isopropylbenzene 80.5 70 - 130 8.05 10.0 1.0 1.00
Methyl Ethyl Ketone 82.1 70 - 130 8.21 10.0 2.0 1.00
Methyl Isobutyl Ketone 97.2 70 - 130 9.72 10.0 5.0 1.00
Methylene Chloride 61.0 70 - 130 6.10 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)34.2 70 - 130 3.42 10.0 0.6 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 98.4 70 - 130 9.84 10.0 1.0 1.00
n-Butyl Alcohol 88.0 70 - 130 88.0 100 50.0 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 22 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH0980-BS1 Batch: BYH0980
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
n-Butylbenzene 77.8 70 - 130 7.78 10.0 1.0 1.00
n-Propyl Benzene 77.5 70 - 130 7.75 10.0 1.0 1.00
Pentachloroethane 34.6 70 - 130 3.46 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
p-Isopropyltoluene 79.1 70 - 130 7.91 10.0 1.0 1.00
sec-Butyl Benzene 77.4 70 - 130 7.74 10.0 1.0 1.00
Styrene 90.2 70 - 130 9.02 10.0 1.0 1.00
tert-Butylbenzene 82.4 70 - 130 8.24 10.0 1.0 1.00
Tetrachloroethene 76.7 70 - 130 7.67 10.0 1.0 1.00
Toluene 74.6 70 - 130 7.46 10.0 1.0 1.00
trans-1,2-Dichloroethene 59.2 70 - 130 5.92 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
trans-1,3-Dichloropropene 87.7 70 - 130 8.77 10.0 1.0 1.00
Trichloroethene 77.9 70 - 130 7.79 10.0 1.0 1.00
Trichlorofluoromethane 44.4 70 - 130 4.44 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Vinyl Chloride 44.3 70 - 130 4.43 10.0 0.8 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Xylenes, total 84.7 70 - 130 25.4 30.0 3.0 1.00
QC Sample ID: BYH0981-BS1 Batch: BYH0981
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Benzene 86.3 70 - 130 0.009 0.0100 0.0004 1.00
Ethylbenzene 102 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)89.7 70 - 130 0.009 0.0100 0.0006 1.00
Naphthalene 115 70 - 130 0.01 0.0100 0.001 1.00
Toluene 89.4 70 - 130 0.009 0.0100 0.001 1.00
Xylenes, total 103 70 - 130 0.03 0.0300 0.003 1.00
QC Sample ID: BYH1035-BS1 Batch: BYH1035
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 97.5 70 - 130 0.01 0.0100 0.0004 1.00
Ethylbenzene 91.5 70 - 130 0.009 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)42.4 70 - 130 0.004 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 96.4 70 - 130 0.01 0.0100 0.001 1.00
Toluene 92.0 70 - 130 0.009 0.0100 0.001 1.00
Xylenes, total 99.6 70 - 130 0.03 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH0909-MS2 QC Source Sample: 24H1665-07Batch: BYH0909
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Benzene 73.7 70 - 130 0.100 0.008 0.125 0.005 1.00
Ethylbenzene 77.9 70 - 130 0.097 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)94.1 70 - 130 0.118 ND 0.125 0.008 1.00
Naphthalene 99.6 70 - 130 0.124 ND 0.125 0.012 1.00
Toluene 70.3 70 - 130 0.102 0.014 0.125 0.012 1.00
Xylenes, total 79.2 70 - 130 0.412 0.115 0.375 0.038 1.00
QC Sample ID: BYH0981-MS1 QC Source Sample: 24H1665-01Batch: BYH0981
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Benzene 73.7 70 - 130 27.8 4.41 31.7 1.27 1.00
Ethylbenzene 55.9 50 - 150 121 103 31.7 3.17 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 23 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH0981-MS1 QC Source Sample: 24H1665-01Batch: BYH0981
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Methyl tert-Butyl Ether (MTBE)82.0 50 - 150 26.0 ND 31.7 1.90 1.00
Naphthalene 103 50 - 150 60.8 28.1 31.7 3.17 1.00
Toluene 85.4 70 - 130 30.0 2.95 31.7 3.17 1.00
Xylenes, total 54.2 70 - 130 655 604 95.2 9.52 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH0909-MSD2 QC Source Sample: 24H1665-07Batch: BYH0909
Date Prepared: 08/19/2024 Date Analyzed: 08/19/2024
Benzene 77.8 4.99 70 - 130 20 0.105 0.008 0.125 0.005 1.00
Ethylbenzene 77.3 0.773 70 - 130 25 0.097 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)90.4 4.01 70 - 130 25 0.113 ND 0.125 0.008 1.00
Naphthalene 92.0 7.93 70 - 130 25 0.115 ND 0.125 0.012 1.00
Toluene 78.5 9.57 70 - 130 20 0.112 0.014 0.125 0.012 1.00
Xylenes, total 77.3 1.75 70 - 130 20 0.404 0.115 0.375 0.038 1.00
QC Sample ID: BYH0981-MSD1 QC Source Sample: 24H1665-01Batch: BYH0981
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Benzene 75.6 2.15 70 - 130 20 28.4 4.41 31.7 1.27 1.00
Ethylbenzene 72.3 4.22 50 - 150 25 126 103 31.7 3.17 1.00
Methyl tert-Butyl Ether (MTBE)86.2 4.99 50 - 150 25 27.3 ND 31.7 1.90 1.00
Naphthalene 96.8 3.45 50 - 150 25 58.8 28.1 31.7 3.17 1.00
Toluene 80.1 5.76 70 - 130 20 28.4 2.95 31.7 3.17 1.00
Xylenes, total 70.9 2.40 70 - 130 20 671 604 95.2 9.52 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 24 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8270E
QC Sample ID: BYH0943-BLK1 Batch: BYH0943
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Acenaphthene ND 0.40 1.00
Acenaphthylene ND 0.40 1.00
Anthracene ND 0.40 1.00
Benzo (a) anthracene ND 0.40 1.00
Benzo (a) pyrene ND 0.40 1.00
Benzo (b) fluoranthene ND 0.40 1.00
Benzo (g,h,i) perylene ND 0.40 1.00
Benzo (k) fluoranthene ND 0.40 1.00
C11-12 Aliphatic hydrocarbons ND 0.20 1.00
C11-C13 Alkyl Naphthalenes ND 0.20 1.00
C13-C16 Aliphatic hydrocarbons ND 0.20 1.00
C17-C21 Aliphatic hydrocarbons ND 0.20 1.00
C22-C35 Aliphatic hydrocarbons ND 0.20 1.00
Chrysene ND 0.40 1.00
Fluoranthene ND 0.40 1.00
Fluorene ND 0.40 1.00
Indeno (1,2,3-cd) pyrene ND 0.40 1.00
Phenanthrene ND 0.40 1.00
Pyrene ND 0.40 1.00
Total C12-C22 PAH ND 0.20 1.00
LCS - EPA 8270E
QC Sample ID: BYH0943-BS1 Batch: BYH0943
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Acenaphthene 66.7 47 - 145 0.4 0.667 0.40 1.00
Acenaphthylene 72.5 65 - 135 0.5 0.667 0.40 1.00
Anthracene 78.2 65 - 135 0.5 0.667 0.40 1.00
Benzo (a) anthracene 81.4 65 - 135 0.5 0.667 0.40 1.00
Benzo (a) pyrene 82.1 65 - 135 0.5 0.667 0.40 1.00
Benzo (b) fluoranthene 90.9 65 - 135 0.6 0.667 0.40 1.00
Benzo (g,h,i) perylene 89.8 65 - 135 0.6 0.667 0.40 1.00
Benzo (k) fluoranthene 99.8 65 - 135 0.7 0.667 0.40 1.00
Chrysene 86.9 65 - 135 0.6 0.667 0.40 1.00
Fluoranthene 86.6 65 - 135 0.6 0.667 0.40 1.00
Fluorene 70.5 65 - 135 0.5 0.667 0.40 1.00
Indeno (1,2,3-cd) pyrene 76.5 65 - 135 0.5 0.667 0.40 1.00
Phenanthrene 81.3 65 - 135 0.5 0.667 0.40 1.00
Pyrene 94.1 33 - 130 0.6 0.667 0.40 1.00
Matrix Spike - EPA 8270E
QC Sample ID: BYH0943-MS1 QC Source Sample: 24H1665-01Batch: BYH0943
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Acenaphthene 43.8 47 - 145 0.6 0.3 0.846 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Acenaphthylene 72.2 50 - 150 0.6 ND 0.846 0.51 1.00
Anthracene 88.8 50 - 150 0.8 ND 0.846 0.51 1.00
Benzo (a) anthracene 85.8 50 - 150 0.7 ND 0.846 0.51 1.00
Benzo (a) pyrene 87.9 50 - 150 0.7 ND 0.846 0.51 1.00
Benzo (b) fluoranthene 95.1 50 - 150 0.8 ND 0.846 0.51 1.00
Benzo (g,h,i) perylene 102 50 - 150 0.9 ND 0.846 0.51 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 25 of 30
QC Report for Work Order (WO) - 24H1665
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8270E (cont.)
QC Sample ID: BYH0943-MS1 QC Source Sample: 24H1665-01Batch: BYH0943
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Benzo (k) fluoranthene 96.3 50 - 150 0.8 ND 0.846 0.51 1.00
Chrysene 91.7 50 - 150 0.8 ND 0.846 0.51 1.00
Fluoranthene 88.2 50 - 150 0.9 0.2 0.846 0.51 1.00
Fluorene 41.5 50 - 150 0.7 0.4 0.846 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Indeno (1,2,3-cd) pyrene 85.5 50 - 150 0.7 ND 0.846 0.51 1.00
Phenanthrene 31.6 50 - 150 1 0.8 0.846 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Pyrene 66.0 33 - 130 0.9 0.3 0.846 0.51 1.00
Matrix Spike Dup - EPA 8270E
QC Sample ID: BYH0943-MSD1 QC Source Sample: 24H1665-01Batch: BYH0943
Date Prepared: 08/20/2024 Date Analyzed: 08/20/2024
Acenaphthene 39.2 6.29 47 - 145 200 0.6 0.3 0.846 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Acenaphthylene 68.4 5.40 50 - 150 200 0.6 ND 0.846 0.51 1.00
Anthracene 79.3 11.3 50 - 150 200 0.7 ND 0.846 0.51 1.00
Benzo (a) anthracene 77.0 10.9 50 - 150 200 0.7 ND 0.846 0.51 1.00
Benzo (a) pyrene 76.9 13.4 50 - 150 200 0.7 ND 0.846 0.51 1.00
Benzo (b) fluoranthene 84.7 11.6 50 - 150 200 0.7 ND 0.846 0.51 1.00
Benzo (g,h,i) perylene 83.3 20.2 50 - 150 200 0.7 ND 0.846 0.51 1.00
Benzo (k) fluoranthene 87.7 9.37 50 - 150 200 0.7 ND 0.846 0.51 1.00
Chrysene 84.2 8.50 50 - 150 200 0.7 ND 0.846 0.51 1.00
Fluoranthene 75.9 12.0 50 - 150 200 0.8 0.2 0.846 0.51 1.00
Fluorene 33.0 10.3 50 - 150 200 0.7 0.4 0.846 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Indeno (1,2,3-cd) pyrene 69.7 20.4 50 - 150 200 0.6 ND 0.846 0.51 1.00
Phenanthrene 18.8 10.6 50 - 150 200 1 0.8 0.846 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Pyrene 59.8 6.32 33 - 130 200 0.8 0.3 0.846 0.51 1.00
CtF WO#: 24H1665
www.ChemtechFord.com Page 26 of 30
Surrogates Report for Work Order (WO) - 24H1665
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH0914-BLK1 Bromofluorobenzene 103 50 BYH0914 1.00150 206 200
BYH0914-BLK1 Capric Acid 0 BYH0914 1.0010.00 500
BYH0992-BLK1 Bromofluorobenzene 83.8 50 BYH0992 1.001503.35 4.00
BYH0992-BLK1 Capric Acid 0 BYH0992 1.0010.00 10.0
LCS - EPA 8015 C
BYH0914-BS1 Bromofluorobenzene 116 50 BYH0914 1.00150 232 200
BYH0914-BS1 Capric Acid 0 BYH0914 1.0010.00 500
BYH0992-BS1 Bromofluorobenzene 88.9 50 BYH0992 1.001503.56 4.00
BYH0992-BS1 Capric Acid 0 BYH0992 1.0010.00 10.0
Matrix Spike - EPA 8015 C
BYH0914-MS1 Bromofluorobenzene 102 50 BYH0914 1.00150 259 254
BYH0914-MS1 Capric Acid 0 BYH0914 1.0010.00 634
BYH0992-MS1 Bromofluorobenzene 97.3 50 BYH0992 1.001503.89 4.00
BYH0992-MS1 Capric Acid 0 BYH0992 1.0010.00 10.0
Matrix Spike Dup - EPA 8015 C
BYH0914-MSD1 Bromofluorobenzene 98.3 50 BYH0914 1.00150 249 254
BYH0914-MSD1 Capric Acid 0 BYH0914 1.0010.00 634
BYH0992-MSD1 Bromofluorobenzene 96.0 50 BYH0992 1.001503.84 4.00
BYH0992-MSD1 Capric Acid 0 BYH0992 1.0010.00 10.0
Blank - EPA 8260D
BYH0909-BLK1 Toluene-d8 101 83.3 BYH0909 1.001220.0101 0.0100
BYH0932-BLK1 Toluene-d8 99.3 82 BYH0932 1.001260.00993 0.0100
BYH0980-BLK1 1,2-Dichloroethane-d4 95.6 64.2 BYH0980 1.001269.56 10.0
BYH0980-BLK1 4-Bromofluorobenzene 92.5 71.4 BYH0980 1.001259.25 10.0
BYH0980-BLK1 Toluene-d8 100 63.2 BYH0980 1.0012910.0 10.0
BYH0981-BLK1 1,2-Dichloroethane-d4 112 70 BYH0981 1.001300.0112 0.0100
BYH0981-BLK1 Toluene-d8 100 82 BYH0981 1.001260.0100 0.0100
BYH0981-BLK1 Toluene-d8 100 70 BYH0981 1.001300.0100 0.0100
BYH0981-BLK1 4-Bromofluorobenzene 102 70 BYH0981 1.001300.0102 0.0100
BYH1035-BLK1 Toluene-d8 100 82 BYH1035 1.001260.0100 0.0100
LCS - EPA 8260D
BYH0909-BS1 Toluene-d8 98.8 83.3 BYH0909 1.001220.00988 0.0100
BYH0932-BS1 Toluene-d8 101 82 BYH0932 1.001260.0101 0.0100
BYH0980-BS1 1,2-Dichloroethane-d4 95.2 64.2 BYH0980 1.001269.52 10.0
BYH0980-BS1 4-Bromofluorobenzene 95.3 71.4 BYH0980 1.001259.53 10.0
BYH0980-BS1 Toluene-d8 101 63.2 BYH0980 1.0012910.1 10.0
BYH0981-BS1 1,2-Dichloroethane-d4 101 70 BYH0981 1.001300.0101 0.0100
BYH0981-BS1 Toluene-d8 99.7 70 BYH0981 1.001300.00997 0.0100
BYH0981-BS1 Toluene-d8 99.7 82 BYH0981 1.001260.00997 0.0100
BYH0981-BS1 4-Bromofluorobenzene 99.6 70 BYH0981 1.001300.00996 0.0100
BYH1035-BS1 Toluene-d8 101 82 BYH1035 1.001260.0101 0.0100
Matrix Spike - EPA 8260D
BYH0909-MS2 Toluene-d8 98.4 83.3 BYH0909 1.001220.123 0.125
BYH0909-MS1 Toluene-d8 102 83.3 BYH0909 1.001220.0508 0.0500
BYH0932-MS1 Toluene-d8 100 82 BYH0932 1.001261.70 1.69
CtF WO#: 24H1665
www.ChemtechFord.com Page 27 of 30
Matrix Spike - EPA 8260D (cont.)
BYH0980-MS1 1,2-Dichloroethane-d4 93.2 64.2 BYH0980 1.001262330 2500
BYH0980-MS1 4-Bromofluorobenzene 94.3 71.4 BYH0980 1.001252360 2500
BYH0980-MS1 Toluene-d8 100 63.2 BYH0980 1.001292500 2500
BYH0981-MS1 1,2-Dichloroethane-d4 101 70 BYH0981 1.0013032.1 31.7
BYH0981-MS1 Toluene-d8 101 82 BYH0981 1.0012632.1 31.7
BYH0981-MS1 Toluene-d8 101 70 BYH0981 1.0013032.1 31.7
BYH0981-MS1 4-Bromofluorobenzene 103 70 BYH0981 1.0013032.8 31.7
BYH1035-MS1 Toluene-d8 100 82 BYH1035 1.001260.0594 0.0593
Matrix Spike Dup - EPA 8260D
BYH0909-MSD1 Toluene-d8 101 83.3 BYH0909 1.001220.0506 0.0500
BYH0909-MSD2 Toluene-d8 100 83.3 BYH0909 1.001220.125 0.125
BYH0932-MSD1 Toluene-d8 101 82 BYH0932 1.001261.60 1.59
BYH0980-MSD1 1,2-Dichloroethane-d4 93.7 64.2 BYH0980 1.001262340 2500
BYH0980-MSD1 4-Bromofluorobenzene 96.0 71.4 BYH0980 1.001252400 2500
BYH0980-MSD1 Toluene-d8 99.4 63.2 BYH0980 1.001292480 2500
BYH0981-MSD1 1,2-Dichloroethane-d4 101 70 BYH0981 1.0013032.2 31.7
BYH0981-MSD1 Toluene-d8 103 70 BYH0981 1.0013032.6 31.7
BYH0981-MSD1 Toluene-d8 103 82 BYH0981 1.0012632.6 31.7
BYH0981-MSD1 4-Bromofluorobenzene 102 70 BYH0981 1.0013032.4 31.7
BYH1035-MSD1 Toluene-d8 99.3 82 BYH1035 1.001260.0589 0.0593
Blank - EPA 8270E
BYH0943-BLK1 2-Fluorobiphenyl 43.5 37 BYH0943 1.001400.145 0.333
BYH0943-BLK1 Terphenyl-dl4 45.1 31 BYH0943 1.001400.150 0.333
LCS - EPA 8270E
BYH0943-BS1 2-Fluorobiphenyl 48.2 37 BYH0943 1.001400.161 0.333
BYH0943-BS1 Terphenyl-dl4 45.9 31 BYH0943 1.001400.153 0.333
Matrix Spike - EPA 8270E
BYH0943-MS1 2-Fluorobiphenyl 38.5 37 BYH0943 1.001400.163 0.423
BYH0943-MS1 Terphenyl-dl4 36.3 31 BYH0943 1.001400.153 0.423
Matrix Spike Dup - EPA 8270E
BYH0943-MSD1 2-Fluorobiphenyl 37.4 37 BYH0943 1.001400.158 0.423
BYH0943-MSD1 Terphenyl-dl4 34.4 31 BYH0943 1.001400.145 0.423
CtF WO#: 24H1665
www.ChemtechFord.com Page 28 of 30
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
8270 TPH Fractionation
24H1665-01 2-Fluorobiphenyl 0.719 56.7 37 1401.27
24H1665-01 Terphenyl-dl4 0.551 43.5 31 1401.27
DRO with silica gel cleanup
24H1665-01 Bromofluorobenzene 282 111 50 150254
24H1665-01 Capric Acid 0.00 0 1634
MBTEXN-GRO
24H1665-01 Toluene-d8 33.2 105 82 12631.7
DRO with silica gel cleanup
24H1665-02 Bromofluorobenzene 261 103 50 150253
24H1665-02 Capric Acid 0.00 0 1633
MBTEXN-GRO
24H1665-02 Toluene-d8 3.15 99.7 82 1263.16
DRO with silica gel cleanup
24H1665-03 Bromofluorobenzene 219 86.1 50 150255
24H1665-03 Capric Acid 0.00 0 1637
MBTEXN-GRO
24H1665-03 Toluene-d8 0.0603 101 82 1260.0599
DRO with silica gel cleanup
24H1665-04 Capric Acid 0.00 0 1634
24H1665-04 Bromofluorobenzene 213 84.0 50 150254
MBTEXN-GRO
24H1665-04 Toluene-d8 0.0564 101 82 1260.0558
DRO with silica gel cleanup
24H1665-05 Capric Acid 0.00 0 1626
24H1665-05 Bromofluorobenzene 220 87.7 50 150250
MBTEXN-GRO
24H1665-05 Toluene-d8 0.0506 101 82 1260.0500 ISTD-01
DRO with silica gel cleanup
24H1665-06 Capric Acid 0.00 0 1616
24H1665-06 Bromofluorobenzene 203 82.4 50 150246
MBTEXN-GRO
24H1665-06 Toluene-d8 0.0623 102 82 1260.0610
DRO with silica gel cleanup
24H1665-07 Bromofluorobenzene 4.14 104 50 1504.00
24H1665-07 Capric Acid 0.00 0 110.0
MBTEXN-GRO
24H1665-07 Toluene-d8 0.124 99.1 83.3 1220.125
DRO with silica gel cleanup
CtF WO#: 24H1665
www.ChemtechFord.com Page 29 of 30
24H1665-08 Capric Acid 0.00 0 110.0
24H1665-08 Bromofluorobenzene 4.31 108 50 1504.00
MBTEXN-GRO
24H1665-08 Toluene-d8 0.124 99.4 83.3 1220.125
8260 Low Level Volatiles
24H1665-09 1,2-Dichloroethane-d4 9.58 95.8 64.2 12610.0
24H1665-09 4-Bromofluorobenzene 9.25 92.5 71.4 12510.0
24H1665-09 Toluene-d8 9.94 99.4 63.2 12910.0
DRO with silica gel cleanup
24H1665-10 Capric Acid 0.00 0 110.0
24H1665-10 Bromofluorobenzene 3.89 97.2 50 1504.00
MBTEXN-GRO
24H1665-10 Toluene-d8 0.124 99.3 83.3 1220.125
CtF WO#: 24H1665
www.ChemtechFord.com Page 30 of 30
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H0986
Project: Former Sommers Auto Wrecking
10/28/2024
Amended
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 20
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H0986-01 EXC-4-SW
24H0986-02 EXC-4-SE
24H0986-03 EXC-4-West 1
24H0986-04 Trip Blank
______________________________________________________________________________________________
Work Order Report Narrative
Amended: This case narrative and the surrogate recovery reports have been added to this report.
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
Page 2 of 20
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Amended Amended
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
10/28/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-SW
Lab ID: 24H0986-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/7/24 9:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/13/248/13/2464EPA 8015 CNDDiesel Range Organics
Inorganic
%8/13/248/13/240.1 CTF800078.1Total Solids
MBTEXn
mg/kg dry 8/13/248/13/240.003 EPA 8260D/5035ANDBenzene
mg/kg dry 8/13/248/13/240.007 EPA 8260D/5035ANDEthylbenzene
mg/kg dry 8/13/248/13/240.004 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/13/248/13/240.007 EPA 8260D/5035A0.03Naphthalene
mg/kg dry 8/13/248/13/240.007 EPA 8260D/5035ANDToluene
mg/kg dry 8/13/248/13/240.02 EPA 8260D/5035ANDXylenes, total
Gasoline Range
mg/kg dry 8/13/248/13/240.0713 EPA 8260B/C 5035A/[CALC]0.644Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 3 of 20Page 3 of 20
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Amended Amended
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
10/28/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-SE
Lab ID: 24H0986-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/12/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/13/248/13/2462EPA 8015 CNDDiesel Range Organics
Inorganic
%8/13/248/13/240.1 CTF800080.5Total Solids
MBTEXn
mg/kg dry 8/12/248/12/240.003 EPA 8260D/5035ANDBenzene
mg/kg dry 8/12/248/12/240.007 EPA 8260D/5035ANDEthylbenzene
mg/kg dry J-LOW-L8/12/248/12/240.004 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/12/248/12/240.007 EPA 8260D/5035ANDNaphthalene
mg/kg dry 8/12/248/12/240.007 EPA 8260D/5035ANDToluene
mg/kg dry 8/12/248/12/240.02 EPA 8260D/5035ANDXylenes, total
Gasoline Range
mg/kg dry 8/12/248/12/240.0698 EPA 8260B/C 5035A/[CALC]0.0716Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 4 of 20Page 4 of 20
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Amended Amended
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
10/28/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-West 1
Lab ID: 24H0986-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/12/24 12:40
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/13/248/13/2463EPA 8015 CNDDiesel Range Organics
Inorganic
%8/13/248/13/240.1 CTF800079.1Total Solids
MBTEXn
mg/kg dry 8/12/248/12/240.002 EPA 8260D/5035A0.04Benzene
mg/kg dry 8/12/248/12/240.006 EPA 8260D/5035A0.01Ethylbenzene
mg/kg dry J-LOW-L8/12/248/12/240.004 EPA 8260D/5035ANDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/12/248/12/240.006 EPA 8260D/5035A0.007Naphthalene
mg/kg dry 8/12/248/12/240.006 EPA 8260D/5035ANDToluene
mg/kg dry 8/12/248/12/240.02 EPA 8260D/5035A0.04Xylenes, total
Gasoline Range
mg/kg dry 8/12/248/12/240.0585 EPA 8260B/C 5035A/[CALC]0.651Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 5 of 20Page 5 of 20
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Amended Amended
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
10/28/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24H0986-04Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/7/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 8/12/248/12/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L 8/12/248/12/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 8/12/248/12/2420.0 EPA 8260D/5030BNDAcetone
ug/L 8/12/248/12/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 8/12/248/12/240.4 EPA 8260D/5030BNDBenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDBromodichloromethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDBromoform
ug/L J-LOW-L8/12/248/12/242.0 EPA 8260D/5030BNDBromomethane
ug/L 8/12/248/12/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 6 of 20Page 6 of 20
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Amended Amended
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
10/28/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24H0986-04Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/7/24 8:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDChloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDChloroform
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDChloromethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L 8/12/248/12/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDDibromochloromethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDDibromomethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 8/12/248/12/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 8/12/248/12/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 8/12/248/12/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 8/12/248/12/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L J-LOW-L8/12/248/12/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDNaphthalene
ug/L 8/12/248/12/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDStyrene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDToluene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L 8/12/248/12/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 8/12/248/12/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 8/12/248/12/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 7 of 20Page 7 of 20
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Amended Amended
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/12/24 15:20 @ 3.4 °C
10/28/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-L = Estimated low due to low recovery of LCS
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H0986
www.ChemtechFord.com
Page 8 of 20Page 8 of 20
Page 9 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH0591-BLK1 Batch: BYH0591
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Diesel Range Organics ND 50 1.00
LCS - EPA 8015 C
QC Sample ID: BYH0591-BS1 Batch: BYH0591
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Diesel Range Organics 107 50 - 150 2150 2000 50 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH0591-MS1 QC Source Sample: 24H0986-01Batch: BYH0591
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Diesel Range Organics 101 50 - 150 2590 ND 2560 64 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH0591-MSD1 QC Source Sample: 24H0986-01Batch: BYH0591
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Diesel Range Organics 102 0.852 50 - 150 20 2610 ND 2560 64 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 10 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH0548-BLK1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.4 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 1.0 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 11 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYH0548-BLK1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 1.0 1.00
n-Butyl Alcohol ND 50.0 1.00
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 1.0 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 3.0 1.00
QC Sample ID: BYH0558-BLK1 Batch: BYH0558
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH0617-BLK1 Batch: BYH0617
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYH0548-BS1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,1,1,2-Tetrachloroethane 108 70 - 130 10.8 10.0 1.0 1.00
1,1,1-Trichloroethane 99.9 70 - 130 9.99 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 105 70 - 130 10.5 10.0 1.0 1.00
1,1,2-Trichloroethane 101 70 - 130 10.1 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 104 70 - 130 10.4 10.0 1.0 1.00
1,1-Dichloroethane 107 70 - 130 10.7 10.0 1.0 1.00
1,1-Dichloroethene 91.7 70 - 130 9.17 10.0 1.0 1.00
1,1-Dichloropropene 93.4 70 - 130 9.34 10.0 1.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 12 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH0548-BS1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,2,3-Trichlorobenzene 113 70 - 130 11.3 10.0 1.0 1.00
1,2,3-Trichloropropane 103 70 - 130 10.3 10.0 1.0 1.00
1,2,4-Trichlorobenzene 116 70 - 130 11.6 10.0 1.0 1.00
1,2,4-Trimethylbenzene 101 70 - 130 10.1 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dibromoethane (EDB)105 70 - 130 10.5 10.0 1.0 1.00
1,2-Dichlorobenzene 106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dichloroethane 99.9 70 - 130 9.99 10.0 1.0 1.00
1,2-Dichloropropane 99.7 70 - 130 9.97 10.0 1.0 1.00
1,3,5-Trimethylbenzene 102 70 - 130 10.2 10.0 1.0 1.00
1,3-Dichlorobenzene 108 70 - 130 10.8 10.0 1.0 1.00
1,3-Dichloropropane 101 70 - 130 10.1 10.0 1.0 1.00
1,4-Dichlorobenzene 108 70 - 130 10.8 10.0 1.0 1.00
2,2-Dichloropropane 93.2 70 - 130 9.32 10.0 1.0 1.00
2-Chlorotoluene 98.2 70 - 130 9.82 10.0 1.0 1.00
2-Hexanone 117 70 - 130 11.7 10.0 10.0 1.00
2-Nitropropane 84.5 70 - 130 25.4 30.0 2.0 1.00
4-Chlorotoluene 97.9 70 - 130 9.79 10.0 1.0 1.00
Acetone 99.6 70 - 130 99.6 100 20.0 1.00
Acrylonitrile 91.3 70 - 130 45.7 50.0 5.0 1.00
Benzene 102 70 - 130 10.2 10.0 0.4 1.00
Bromobenzene 98.8 70 - 130 9.88 10.0 1.0 1.00
Bromochloromethane 103 70 - 130 10.3 10.0 1.0 1.00
Bromodichloromethane 101 70 - 130 10.1 10.0 1.0 1.00
Bromoform 97.3 70 - 130 9.73 10.0 1.0 1.00
Bromomethane 54.0 70 - 130 5.40 10.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Carbon Disulfide 97.4 70 - 130 9.74 10.0 2.0 1.00
Carbon Tetrachloride 106 70 - 130 10.6 10.0 1.0 1.00
Chlorobenzene 103 70 - 130 10.3 10.0 1.0 1.00
Chloroethane 87.8 70 - 130 8.78 10.0 1.0 1.00
Chloroform 92.5 70 - 130 9.25 10.0 1.0 1.00
Chloromethane 79.9 70 - 130 7.99 10.0 1.0 1.00
cis-1,2-Dichloroethene 90.4 70 - 130 9.04 10.0 1.0 1.00
cis-1,3-Dichloropropene 110 70 - 130 11.0 10.0 1.0 1.00
Cyclohexanone 109 70 - 130 109 100 10.0 1.00
Dibromochloromethane 103 70 - 130 10.3 10.0 1.0 1.00
Dibromomethane 108 70 - 130 10.8 10.0 1.0 1.00
Dichlorodifluoromethane 84.8 70 - 130 8.48 10.0 1.0 1.00
Ethyl Acetate 96.1 70 - 130 19.2 20.0 2.0 1.00
Ethyl Ether 89.0 70 - 130 8.90 10.0 1.0 1.00
Ethylbenzene 95.1 70 - 130 9.51 10.0 1.0 1.00
Hexachlorobutadiene 108 70 - 130 10.8 10.0 1.0 1.00
Isobutanol 127 70 - 130 255 200 20.0 1.00
Isopropylbenzene 98.8 70 - 130 9.88 10.0 1.0 1.00
Methyl Ethyl Ketone 88.6 70 - 130 8.86 10.0 2.0 1.00
Methyl Isobutyl Ketone 101 70 - 130 10.1 10.0 5.0 1.00
Methylene Chloride 101 70 - 130 10.1 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)66.0 70 - 130 6.60 10.0 0.6 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 105 70 - 130 10.5 10.0 1.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 13 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH0548-BS1 Batch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
n-Butyl Alcohol 93.2 70 - 130 93.2 100 50.0 1.00
n-Butylbenzene 99.9 70 - 130 9.99 10.0 1.0 1.00
n-Propyl Benzene 99.8 70 - 130 9.98 10.0 1.0 1.00
Pentachloroethane 111 70 - 130 11.1 10.0 1.0 1.00
p-Isopropyltoluene 97.9 70 - 130 9.79 10.0 1.0 1.00
sec-Butyl Benzene 97.3 70 - 130 9.73 10.0 1.0 1.00
Styrene 107 70 - 130 10.7 10.0 1.0 1.00
tert-Butylbenzene 98.0 70 - 130 9.80 10.0 1.0 1.00
Tetrachloroethene 90.3 70 - 130 9.03 10.0 1.0 1.00
Toluene 94.6 70 - 130 9.46 10.0 1.0 1.00
trans-1,2-Dichloroethene 91.3 70 - 130 9.13 10.0 1.0 1.00
trans-1,3-Dichloropropene 111 70 - 130 11.1 10.0 1.0 1.00
Trichloroethene 100 70 - 130 10.0 10.0 1.0 1.00
Trichlorofluoromethane 85.0 70 - 130 8.50 10.0 1.0 1.00
Vinyl Chloride 78.2 70 - 130 7.82 10.0 0.8 1.00
Xylenes, total 103 70 - 130 30.9 30.0 3.0 1.00
QC Sample ID: BYH0558-BS1 Batch: BYH0558
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Benzene 85.1 70 - 130 0.009 0.0100 0.0004 1.00
Ethylbenzene 81.6 70 - 130 0.008 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)67.8 70 - 130 0.007 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 95.7 70 - 130 0.01 0.0100 0.001 1.00
Toluene 78.3 70 - 130 0.008 0.0100 0.001 1.00
Xylenes, total 89.0 70 - 130 0.03 0.0300 0.003 1.00
QC Sample ID: BYH0617-BS1 Batch: BYH0617
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Benzene 85.3 70 - 130 0.009 0.0100 0.0004 1.00
Ethylbenzene 98.0 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)95.4 70 - 130 0.01 0.0100 0.0006 1.00
Naphthalene 88.7 70 - 130 0.009 0.0100 0.001 1.00
Toluene 86.8 70 - 130 0.009 0.0100 0.001 1.00
Xylenes, total 97.4 70 - 130 0.03 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH0548-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,1,1,2-Tetrachloroethane 96.5 70 - 130 48.2 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 100 70 - 130 50.1 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 93.4 70 - 130 46.7 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 95.1 70 - 130 47.6 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 92.0 70 - 130 46.0 ND 50.0 5.0 1.00
1,1-Dichloroethane 99.1 70 - 130 49.6 ND 50.0 5.0 1.00
1,1-Dichloroethene 86.1 70 - 130 43.0 ND 50.0 5.0 1.00
1,1-Dichloropropene 87.5 70 - 130 43.8 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 95.0 70 - 130 47.5 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 92.6 70 - 130 46.3 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 98.2 70 - 130 49.1 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 95.7 70 - 130 47.8 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 87.2 70 - 130 43.6 ND 50.0 5.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 14 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH0548-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,2-Dibromoethane (EDB)93.4 70 - 130 46.7 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 96.0 70 - 130 48.0 ND 50.0 5.0 1.00
1,2-Dichloroethane 91.4 70 - 130 45.7 ND 50.0 5.0 1.00
1,2-Dichloropropane 94.1 70 - 130 47.0 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 97.5 70 - 130 48.8 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 99.8 70 - 130 49.9 ND 50.0 5.0 1.00
1,3-Dichloropropane 95.0 70 - 130 47.5 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 98.4 70 - 130 49.2 ND 50.0 5.0 1.00
2,2-Dichloropropane 71.0 70 - 130 35.5 ND 50.0 5.0 1.00
2-Chlorotoluene 94.3 70 - 130 47.2 ND 50.0 5.0 1.00
2-Hexanone 117 70 - 130 58.4 ND 50.0 50.0 1.00
2-Nitropropane 81.6 70 - 130 122 ND 150 10.0 1.00
4-Chlorotoluene 92.0 70 - 130 46.0 ND 50.0 5.0 1.00
Acetone 94.6 70 - 130 473 ND 500 100 1.00
Acrylonitrile 86.2 70 - 130 215 ND 250 25.0 1.00
Benzene 97.6 70 - 130 48.8 ND 50.0 2.0 1.00
Bromobenzene 93.3 70 - 130 46.6 ND 50.0 5.0 1.00
Bromochloromethane 94.4 70 - 130 47.2 ND 50.0 5.0 1.00
Bromodichloromethane 95.6 70 - 130 47.8 ND 50.0 5.0 1.00
Bromoform 90.5 70 - 130 45.2 ND 50.0 5.0 1.00
Bromomethane 46.5 70 - 130 23.2 ND 50.0 10.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Disulfide 77.4 70 - 130 38.7 ND 50.0 10.0 1.00
Carbon Tetrachloride 101 70 - 130 50.4 ND 50.0 5.0 1.00
Chlorobenzene 98.1 70 - 130 49.0 ND 50.0 5.0 1.00
Chloroethane 87.8 70 - 130 43.9 ND 50.0 5.0 1.00
Chloroform 89.2 70 - 130 44.6 ND 50.0 5.0 1.00
Chloromethane 68.2 70 - 130 34.1 ND 50.0 5.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
cis-1,2-Dichloroethene 88.4 70 - 130 44.2 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 101 70 - 130 50.4 ND 50.0 5.0 1.00
Cyclohexanone 112 70 - 130 560 ND 500 50.0 1.00
Dibromochloromethane 91.6 70 - 130 45.8 ND 50.0 5.0 1.00
Dibromomethane 104 70 - 130 51.8 ND 50.0 5.0 1.00
Dichlorodifluoromethane 56.9 70 - 130 28.4 ND 50.0 5.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Ethyl Acetate 89.8 70 - 130 89.8 ND 100 10.0 1.00
Ethyl Ether 79.2 70 - 130 39.6 ND 50.0 5.0 1.00
Ethylbenzene 91.9 70 - 130 46.0 ND 50.0 5.0 1.00
Hexachlorobutadiene 98.0 70 - 130 49.0 ND 50.0 5.0 1.00
Isobutanol 117 70 - 130 1170 ND 1000 100 1.00
Isopropylbenzene 94.7 70 - 130 47.4 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 83.1 70 - 130 41.6 ND 50.0 10.0 1.00
Methyl Isobutyl Ketone 98.8 70 - 130 49.4 ND 50.0 25.0 1.00
Methylene Chloride 88.3 70 - 130 44.2 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)57.8 70 - 130 28.9 ND 50.0 3.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 15 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH0548-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Naphthalene 85.4 70 - 130 42.7 ND 50.0 5.0 1.00
n-Butyl Alcohol 87.6 70 - 130 438 ND 500 250 1.00
n-Butylbenzene 91.2 70 - 130 45.6 ND 50.0 5.0 1.00
n-Propyl Benzene 94.4 70 - 130 47.2 ND 50.0 5.0 1.00
Pentachloroethane 90.4 70 - 130 45.2 ND 50.0 5.0 1.00
p-Isopropyltoluene 87.9 70 - 130 44.0 ND 50.0 5.0 1.00
sec-Butyl Benzene 94.1 70 - 130 47.0 ND 50.0 5.0 1.00
Styrene 99.2 70 - 130 49.6 ND 50.0 5.0 1.00
tert-Butylbenzene 93.5 70 - 130 46.8 ND 50.0 5.0 1.00
Tetrachloroethene 85.2 70 - 130 42.6 ND 50.0 5.0 1.00
Toluene 92.5 70 - 130 46.2 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 85.6 70 - 130 42.8 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 95.5 70 - 130 47.8 ND 50.0 5.0 1.00
Trichloroethene 97.6 70 - 130 48.8 ND 50.0 5.0 1.00
Trichlorofluoromethane 84.5 70 - 130 42.2 ND 50.0 5.0 1.00
Vinyl Chloride 73.1 70 - 130 36.6 ND 50.0 4.0 1.00
Xylenes, total 99.3 70 - 130 149 ND 150 15.0 1.00
QC Sample ID: BYH0558-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH0558
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Benzene 109 70 - 130 3.27 ND 3.01 0.12 1.00
Ethylbenzene 104 50 - 150 3.12 ND 3.01 0.30 1.00
Methyl tert-Butyl Ether (MTBE)92.6 50 - 150 2.78 ND 3.01 0.18 1.00
Naphthalene 108 50 - 150 3.26 ND 3.01 0.30 1.00
Toluene 104 70 - 130 3.12 ND 3.01 0.30 1.00
Xylenes, total 110 70 - 130 9.96 ND 9.02 0.90 1.00
QC Sample ID: BYH0617-MS1 QC Source Sample: 24H0986-01Batch: BYH0617
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Benzene 86.9 70 - 130 2.78 ND 3.20 0.13 1.00
Ethylbenzene 90.0 50 - 150 2.88 ND 3.20 0.32 1.00
Methyl tert-Butyl Ether (MTBE)88.0 50 - 150 2.82 ND 3.20 0.19 1.00
Naphthalene 101 50 - 150 3.22 ND 3.20 0.32 1.00
Toluene 89.5 70 - 130 2.87 ND 3.20 0.32 1.00
Xylenes, total 87.3 70 - 130 8.38 ND 9.61 0.96 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH0548-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,1,1,2-Tetrachloroethane 98.5 2.05 70 - 130 20 49.2 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 95.8 4.49 70 - 130 20 47.9 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 95.9 2.64 70 - 130 20 48.0 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 93.7 1.48 70 - 130 20 46.8 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 86.4 6.28 70 - 130 20 43.2 ND 50.0 5.0 1.00
1,1-Dichloroethane 97.4 1.73 70 - 130 20 48.7 ND 50.0 5.0 1.00
1,1-Dichloroethene 79.4 8.10 70 - 130 20 39.7 ND 50.0 5.0 1.00
1,1-Dichloropropene 83.8 4.32 70 - 130 20 41.9 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 101 6.42 70 - 130 20 50.6 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 94.1 1.61 70 - 130 20 47.0 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 103 4.58 70 - 130 20 51.4 ND 50.0 5.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 16 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH0548-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
1,2,4-Trimethylbenzene 92.8 3.08 70 - 130 20 46.4 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 86.9 0.345 70 - 130 20 43.4 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)96.1 2.85 70 - 130 20 48.0 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 96.7 0.727 70 - 130 20 48.4 ND 50.0 5.0 1.00
1,2-Dichloroethane 91.6 0.219 70 - 130 20 45.8 ND 50.0 5.0 1.00
1,2-Dichloropropane 90.8 3.57 70 - 130 20 45.4 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 94.2 3.44 70 - 130 20 47.1 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 99.0 0.805 70 - 130 20 49.5 ND 50.0 5.0 1.00
1,3-Dichloropropane 93.8 1.27 70 - 130 20 46.9 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 98.3 0.102 70 - 130 20 49.2 ND 50.0 5.0 1.00
2,2-Dichloropropane 78.9 10.5 70 - 130 20 39.4 ND 50.0 5.0 1.00
2-Chlorotoluene 91.2 3.34 70 - 130 20 45.6 ND 50.0 5.0 1.00
2-Hexanone 108 7.93 70 - 130 20 53.9 ND 50.0 50.0 1.00
2-Nitropropane 77.9 4.60 70 - 130 20 117 ND 150 10.0 1.00
4-Chlorotoluene 90.2 1.98 70 - 130 20 45.1 ND 50.0 5.0 1.00
Acetone 97.0 2.60 70 - 130 20 485 ND 500 100 1.00
Acrylonitrile 87.8 1.89 70 - 130 20 220 ND 250 25.0 1.00
Benzene 94.2 3.55 70 - 130 20 47.1 ND 50.0 2.0 1.00
Bromobenzene 91.8 1.62 70 - 130 20 45.9 ND 50.0 5.0 1.00
Bromochloromethane 92.5 2.03 70 - 130 20 46.2 ND 50.0 5.0 1.00
Bromodichloromethane 93.4 2.33 70 - 130 20 46.7 ND 50.0 5.0 1.00
Bromoform 89.6 0.999 70 - 130 20 44.8 ND 50.0 5.0 1.00
Bromomethane 55.2 17.1 70 - 130 20 27.6 ND 50.0 10.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Disulfide 74.8 3.42 70 - 130 20 37.4 ND 50.0 10.0 1.00
Carbon Tetrachloride 96.8 4.15 70 - 130 20 48.4 ND 50.0 5.0 1.00
Chlorobenzene 95.8 2.37 70 - 130 20 47.9 ND 50.0 5.0 1.00
Chloroethane 80.9 8.18 70 - 130 20 40.4 ND 50.0 5.0 1.00
Chloroform 86.6 2.96 70 - 130 20 43.3 ND 50.0 5.0 1.00
Chloromethane 66.3 2.83 70 - 130 20 33.2 ND 50.0 5.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
cis-1,2-Dichloroethene 84.7 4.27 70 - 130 20 42.4 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 100 0.398 70 - 130 20 50.2 ND 50.0 5.0 1.00
Cyclohexanone 109 2.36 70 - 130 20 547 ND 500 50.0 1.00
Dibromochloromethane 92.6 1.09 70 - 130 20 46.3 ND 50.0 5.0 1.00
Dibromomethane 103 0.581 70 - 130 20 51.4 ND 50.0 5.0 1.00
Dichlorodifluoromethane 53.1 6.91 70 - 130 20 26.6 ND 50.0 5.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Ethyl Acetate 89.8 0.111 70 - 130 20 89.8 ND 100 10.0 1.00
Ethyl Ether 85.5 7.65 70 - 130 20 42.8 ND 50.0 5.0 1.00
Ethylbenzene 89.8 2.31 70 - 130 20 44.9 ND 50.0 5.0 1.00
Hexachlorobutadiene 97.1 0.923 70 - 130 20 48.6 ND 50.0 5.0 1.00
Isobutanol 113 3.27 70 - 130 20 1130 ND 1000 100 1.00
Isopropylbenzene 91.7 3.22 70 - 130 20 45.8 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 94.7 13.0 70 - 130 20 47.4 ND 50.0 10.0 1.00
Methyl Isobutyl Ketone 114 14.4 70 - 130 20 57.0 ND 50.0 25.0 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 17 of 20
QC Report for Work Order (WO) - 24H0986
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH0548-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0548
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Methylene Chloride 86.1 2.52 70 - 130 20 43.0 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)62.8 8.29 70 - 130 20 31.4 ND 50.0 3.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Naphthalene 94.2 9.80 70 - 130 20 47.1 ND 50.0 5.0 1.00
n-Butyl Alcohol 94.7 7.81 70 - 130 20 474 ND 500 250 1.00
n-Butylbenzene 88.8 2.67 70 - 130 20 44.4 ND 50.0 5.0 1.00
n-Propyl Benzene 87.7 7.36 70 - 130 20 43.8 ND 50.0 5.0 1.00
Pentachloroethane 67.8 28.6 70 - 130 20 33.9 ND 50.0 5.0 1.00
RPD-MSOut - The RPD between MS and MSD is outside established control limits.
p-Isopropyltoluene 88.7 0.906 70 - 130 20 44.4 ND 50.0 5.0 1.00
sec-Butyl Benzene 88.2 6.47 70 - 130 20 44.1 ND 50.0 5.0 1.00
Styrene 98.6 0.607 70 - 130 20 49.3 ND 50.0 5.0 1.00
tert-Butylbenzene 92.3 1.29 70 - 130 20 46.2 ND 50.0 5.0 1.00
Tetrachloroethene 81.9 3.95 70 - 130 20 41.0 ND 50.0 5.0 1.00
Toluene 89.3 3.52 70 - 130 20 44.6 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 80.4 6.27 70 - 130 20 40.2 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 98.1 2.69 70 - 130 20 49.0 ND 50.0 5.0 1.00
Trichloroethene 94.2 3.55 70 - 130 20 47.1 ND 50.0 5.0 1.00
Trichlorofluoromethane 82.1 2.88 70 - 130 20 41.0 ND 50.0 5.0 1.00
Vinyl Chloride 69.8 4.62 70 - 130 20 34.9 ND 50.0 4.0 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Xylenes, total 96.4 2.93 70 - 130 20 145 ND 150 15.0 1.00
QC Sample ID: BYH0558-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH0558
Date Prepared: 08/12/2024 Date Analyzed: 08/12/2024
Benzene 107 2.13 70 - 130 20 3.21 ND 3.01 0.12 1.00
Ethylbenzene 101 2.93 50 - 150 25 3.03 ND 3.01 0.30 1.00
Methyl tert-Butyl Ether (MTBE)95.6 3.19 50 - 150 25 2.87 ND 3.01 0.18 1.00
Naphthalene 107 1.67 50 - 150 25 3.21 ND 3.01 0.30 1.00
Toluene 101 2.54 70 - 130 20 3.04 ND 3.01 0.30 1.00
Xylenes, total 109 1.37 70 - 130 20 9.83 ND 9.02 0.90 1.00
QC Sample ID: BYH0617-MSD1 QC Source Sample: 24H0986-01Batch: BYH0617
Date Prepared: 08/13/2024 Date Analyzed: 08/13/2024
Benzene 84.5 2.80 70 - 130 20 2.71 ND 3.20 0.13 1.00
Ethylbenzene 84.2 6.66 50 - 150 25 2.70 ND 3.20 0.32 1.00
Methyl tert-Butyl Ether (MTBE)88.9 1.02 50 - 150 25 2.85 ND 3.20 0.19 1.00
Naphthalene 93.8 7.00 50 - 150 25 3.00 ND 3.20 0.32 1.00
Toluene 84.1 6.22 70 - 130 20 2.69 ND 3.20 0.32 1.00
Xylenes, total 90.9 4.04 70 - 130 20 8.73 ND 9.61 0.96 1.00
CtF WO#: 24H0986
www.ChemtechFord.com Page 18 of 20
Surrogates Report for Work Order (WO) - 24H0986
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH0591-BLK1 Bromofluorobenzene 107 50 BYH0591 1.00150 215 200
BYH0591-BLK1 Capric Acid 0 BYH0591 1.0010.00 500
LCS - EPA 8015 C
BYH0591-BS1 Bromofluorobenzene 113 50 BYH0591 1.00150 226 200
BYH0591-BS1 Capric Acid 0 BYH0591 1.0010.00 500
Matrix Spike - EPA 8015 C
BYH0591-MS1 Bromofluorobenzene 97.9 50 BYH0591 1.00150 251 256
BYH0591-MS1 Capric Acid 0 BYH0591 1.0010.00 641
Matrix Spike Dup - EPA 8015 C
BYH0591-MSD1 Bromofluorobenzene 101 50 BYH0591 1.00150 259 256
BYH0591-MSD1 Capric Acid 0 BYH0591 1.0010.00 641
Blank - EPA 8260D
BYH0548-BLK1 1,2-Dichloroethane-d4 98.4 64.2 BYH0548 1.001269.84 10.0
BYH0548-BLK1 4-Bromofluorobenzene 97.9 71.4 BYH0548 1.001259.79 10.0
BYH0548-BLK1 Toluene-d8 100 63.2 BYH0548 1.0012910.0 10.0
BYH0558-BLK1 Toluene-d8 100 82 BYH0558 1.001260.0100 0.0100
BYH0617-BLK1 Toluene-d8 102 82 BYH0617 1.001260.0102 0.0100
LCS - EPA 8260D
BYH0548-BS1 1,2-Dichloroethane-d4 98.6 64.2 BYH0548 1.001269.86 10.0
BYH0548-BS1 4-Bromofluorobenzene 98.9 71.4 BYH0548 1.001259.89 10.0
BYH0548-BS1 Toluene-d8 101 63.2 BYH0548 1.0012910.1 10.0
BYH0558-BS1 Toluene-d8 101 82 BYH0558 1.001260.0101 0.0100
BYH0617-BS1 Toluene-d8 96.1 82 BYH0617 1.001260.00961 0.0100
Matrix Spike - EPA 8260D
BYH0548-MS1 1,2-Dichloroethane-d4 99.1 64.2 BYH0548 1.0012649.6 50.0
BYH0548-MS1 4-Bromofluorobenzene 98.5 71.4 BYH0548 1.0012549.2 50.0
BYH0548-MS1 Toluene-d8 101 63.2 BYH0548 1.0012950.6 50.0
BYH0558-MS1 Toluene-d8 101 82 BYH0558 1.001263.03 3.01
BYH0617-MS1 Toluene-d8 98.5 82 BYH0617 1.001263.15 3.20
Matrix Spike Dup - EPA 8260D
BYH0548-MSD1 1,2-Dichloroethane-d4 98.6 64.2 BYH0548 1.0012649.3 50.0
BYH0548-MSD1 4-Bromofluorobenzene 97.1 71.4 BYH0548 1.0012548.6 50.0
BYH0548-MSD1 Toluene-d8 101 63.2 BYH0548 1.0012950.5 50.0
BYH0558-MSD1 Toluene-d8 101 82 BYH0558 1.001263.03 3.01
BYH0617-MSD1 Toluene-d8 97.1 82 BYH0617 1.001263.11 3.20
CtF WO#: 24H0986
www.ChemtechFord.com Page 19 of 20
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24H0986-01 Capric Acid 0.00 0 1641
24H0986-01 Bromofluorobenzene 221 86.2 50 150256
MBTEXN-GRO
24H0986-01 Toluene-d8 0.0710 99.6 82 1260.0713
DRO with silica gel cleanup
24H0986-02 Capric Acid 0.00 0 1621
24H0986-02 Bromofluorobenzene 209 84.1 50 150249
MBTEXN-GRO
24H0986-02 Toluene-d8 0.0704 101 82 1260.0698
DRO with silica gel cleanup
24H0986-03 Capric Acid 0.00 0 1632
24H0986-03 Bromofluorobenzene 219 86.6 50 150253
MBTEXN-GRO
24H0986-03 Toluene-d8 0.0590 101 82 1260.0585
8260 Low Level Volatiles
24H0986-04 Toluene-d8 9.97 99.7 63.2 12910.0
24H0986-04 4-Bromofluorobenzene 9.60 96.0 71.4 12510.0
24H0986-04 1,2-Dichloroethane-d4 9.84 98.4 64.2 12610.0
CtF WO#: 24H0986
www.ChemtechFord.com Page 20 of 20
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24F1419
Project: Former Sommers Auto Wrecking
6/28/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 47
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24F1419-01 TP - 1 (2'-3')
24F1419-02 TP - 2 ( 5'-6')
24F1419-03 TP - 3 ( 2'-3')
24F1419-04 TP - 4 ( 2'-3')
24F1419-05 TP - 5 ( 4'-5')
24F1419-06 TP - 6 ( 4'-5')
24F1419-07 TP - 60 ( 4'-5')
24F1419-08 DU-1
24F1419-09 DU-2
24F1419-10 DU-10
24F1419-11 Test Pit WCS
24F1419-12 EXC 1-3 WCS
24F1419-13 Trip Blank
24F1419-14 Equipment Blank
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
Page 2 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 1 (2'-3')
Lab ID: 24F1419-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 9:10
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800081.7Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.29 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.29 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.29 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.29 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDEthylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDNaphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.24 EPA 8270E/35700.53C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/357011.2C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/35702.46C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/357014.3C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.24 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 3 of 46Page 3 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 2 ( 5'-6')
Lab ID: 24F1419-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 10:25
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800079.9Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B3.63C5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B13.2C7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B5.85C9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B13.0C9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030B0.75Benzene
mg/kg dry MS-Low6/18/246/18/240.03 EPA 8260D/5030B0.18Ethylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030B1.88Naphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030B0.36Xylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.75 EPA 8270E/35702.91C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.75 EPA 8270E/35701330C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.75 EPA 8270E/357081.9C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.75 EPA 8270E/357044.7C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.75 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.75 EPA 8270E/35705.14Total C12-C22 PAH
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/35703.44Phenanthrene
mg/kg dry 6/21/246/21/241.50 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 4 of 46Page 4 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 3 ( 2'-3')
Lab ID: 24F1419-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 11:10
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800091.4Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/242.10 EPA 8260D/5030B5.08C5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/242.10 EPA 8260D/5030B6.93C7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/242.10 EPA 8260D/5030B3.64C9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/242.10 EPA 8260D/5030B29.3C9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.08 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.21 EPA 8260D/5030B2.48Ethylbenzene
mg/kg dry 6/18/246/18/240.21 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.21 EPA 8260D/5030B0.81Naphthalene
mg/kg dry 6/18/246/18/240.21 EPA 8260D/5030B5.28Toluene
mg/kg dry 6/18/246/18/240.63 EPA 8260D/5030B17.0Xylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/357026.8C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/3570859C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/3570320C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/35701400C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/2413.1 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/2426.3 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 5 of 46Page 5 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 4 ( 2'-3')
Lab ID: 24F1419-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 11:35
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800074.0Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.32 EPA 8260D/5030B1.04C5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.32 EPA 8260D/5030B3.49C7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.32 EPA 8260D/5030B1.51C9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.32 EPA 8260D/5030B13.6C9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030B0.10Benzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030B0.73Ethylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030B0.44Naphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030B0.14Toluene
mg/kg dry 6/18/246/18/240.10 EPA 8260D/5030B3.50Xylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/245.40 EPA 8270E/357011.2C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570530C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570112C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570588C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/245.40 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/2410.8 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 6 of 46Page 6 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 5 ( 4'-5')
Lab ID: 24F1419-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 11:50
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800078.1Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDEthylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDNaphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.26 EPA 8270E/35700.65C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/357020.6C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/35707.11C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/357028.6C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.26 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/240.51 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 7 of 46Page 7 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 6 ( 4'-5')
Lab ID: 24F1419-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:05
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800075.6Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDEthylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDNaphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.26 EPA 8270E/35700.67C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/357013.7C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/35701.66C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/357012.1C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.26 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.26 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/240.53 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 8 of 46Page 8 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: TP - 60 ( 4'-5')
Lab ID: 24F1419-07Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:10
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800082.4Total Solids
BETX Compounds
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/kg dry 6/18/246/18/240.30 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/kg dry 6/18/246/18/240.01 EPA 8260D/5030BNDBenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDEthylbenzene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDNaphthalene
mg/kg dry 6/18/246/18/240.03 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.09 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/240.24 EPA 8270E/35700.57C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/357013.7C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/35707.07C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/357031.8C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/240.24 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/240.24 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/240.49 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 9 of 46Page 9 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: DU-1
Lab ID: 24F1419-08Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 13:20
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800099.8Total Solids
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/244.00 EPA 8270E/35705.11C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570149C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/357044.5C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570262C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 10 of 46Page 10 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: DU-2
Lab ID: 24F1419-09Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 13:00
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800098.6Total Solids
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/244.00 EPA 8270E/35705.96C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570223C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570644C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/35702270C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 11 of 46Page 11 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: DU-10
Lab ID: 24F1419-10Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 13:25
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF8000100Total Solids
Semi-Volatile Compounds
mg/kg dry 6/21/246/21/244.00 EPA 8270E/35705.79C11-12 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570167C13-C16 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570121C17-C21 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570695C22-C35 Aliphatic hydrocarbons
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDC11-C13 Alkyl Naphthalenes
mg/kg dry 6/21/246/21/244.00 EPA 8270E/3570NDTotal C12-C22 PAH
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAcenaphthylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDAnthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) anthracene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (a) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (b) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (g,h,i) perylene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDBenzo (k) fluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDChrysene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluoranthene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDFluorene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDIndeno (1,2,3-cd) pyrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPhenanthrene
mg/kg dry 6/21/246/21/248.00 EPA 8270E/3570NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 12 of 46Page 12 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Test Pit WCS
Lab ID: 24F1419-11Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:45
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
°F 6/25/246/25/2480.0 EPA 1010MOD>200Flashpoint
mg/kg dry 6/19/246/19/24308EPA 1664BModNDOil & Grease (HEM)
%6/19/246/19/240.1 EPA 1311/1311NDPercent Pass
pH Units 6/19/24 10:356/19/24 8:590.1 EPA 9040C/9045D10.5pH
%6/19/246/18/240.1 CTF800080.9Total Solids
Metals
mg/kg dry 6/20/246/19/241.05 EPA 6010D/3050B15.2Arsenic, Total
mg/kg dry 6/20/246/19/240.210 EPA 6010D/3050B129Barium, Total
mg/kg dry 6/20/246/19/240.105 EPA 6010D/3050B0.536Cadmium, Total
mg/kg dry 6/20/246/19/240.105 EPA 6010D/3050B9.37Chromium, Total
mg/kg dry 6/20/246/19/242.10 EPA 6010D/3050B171Lead, Total
mg/kg dry 6/19/246/19/240.017 EPA 7471A0.075Mercury, Total
mg/kg dry 6/20/246/19/241.26 EPA 6010D/3050BNDSelenium, Total
mg/kg dry 6/20/246/19/240.105 EPA 6010D/3050BNDSilver, Total
TCLP Metals
mg/L 6/28/246/28/240.20 EPA 6010D/3010A0.42Lead, TCLP
Volatile Organic Compounds
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,1,1-Trichloroethane
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,1,2-Trichloroethane
mg/kg dry J-LOW-L6/18/246/18/240.28 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,1-Dichloroethene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,2-Dichlorobenzene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,2-Dichloroethane
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BND1,4-Dichlorobenzene
mg/kg dry J-LOW-C6/18/246/18/240.56 EPA 8260D/5030BND2-Nitropropane
mg/kg dry 6/18/246/18/245.62 EPA 8260D/5030BNDAcetone
mg/kg dry 6/18/246/18/240.11 EPA 8260D/5030B0.12Benzene
mg/kg dry J-LOW-L6/18/246/18/240.56 EPA 8260D/5030BNDCarbon Disulfide
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDCarbon Tetrachloride
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDChlorobenzene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDChloroform
mg/kg dry MS-Low6/18/246/18/242.81 EPA 8260D/5030BNDCyclohexanone
mg/kg dry 6/18/246/18/240.56 EPA 8260D/5030BNDEthyl Acetate
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDEthyl Ether
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030B0.43Ethylbenzene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDHexachlorobutadiene
mg/kg dry 6/18/246/18/245.62 EPA 8260D/5030BNDIsobutanol
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 13 of 46Page 13 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Test Pit WCS (cont.)
Lab ID: 24F1419-11Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:45
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
mg/kg dry 6/18/246/18/240.56 EPA 8260D/5030BNDMethyl Ethyl Ketone
mg/kg dry 6/18/246/18/241.40 EPA 8260D/5030BNDMethyl Isobutyl Ketone
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDMethylene Chloride
mg/kg dry 6/18/246/18/2414.0 EPA 8260D/5030BNDn-Butyl Alcohol
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDTetrachloroethene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDToluene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDTrichloroethene
mg/kg dry 6/18/246/18/240.28 EPA 8260D/5030BNDTrichlorofluoromethane
mg/kg dry 6/18/246/18/240.22 EPA 8260D/5030BNDVinyl Chloride
mg/kg dry 6/18/246/18/240.84 EPA 8260D/5030B2.32Xylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 14 of 46Page 14 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: EXC 1-3 WCS
Lab ID: 24F1419-12Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:30
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Inorganic
%6/19/246/18/240.1 CTF800096.0Total Solids
Metals
mg/kg dry 6/20/246/19/244.57 EPA 6010D/3050B10.3Arsenic, Total
mg/kg dry 6/20/246/19/244.57 EPA 6010D/3050B274Lead, Total
TCLP Metals
mg/L 6/20/246/20/240.50 EPA 6010D/3010ANDArsenic, TCLP
mg/L 6/20/246/20/240.20 EPA 6010D/3010A1.27Lead, TCLP
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 15 of 46Page 15 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24F1419-13Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 8:00
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 6/19/246/19/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L 6/19/246/19/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 6/19/246/19/2420.0 EPA 8260D/5030BNDAcetone
ug/L 6/19/246/19/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 6/19/246/19/240.4 EPA 8260D/5030BNDBenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030B10.7Bromodichloromethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDBromoform
ug/L 6/19/246/19/242.0 EPA 8260D/5030BNDBromomethane
ug/L 6/19/246/19/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 16 of 46Page 16 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24F1419-13Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 8:00
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDChloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030B40.2Chloroform
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDChloromethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L 6/19/246/19/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 6/19/246/19/241.0 EPA 8260D/5030B2.2Dibromochloromethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDDibromomethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 6/19/246/19/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 6/19/246/19/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 6/19/246/19/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 6/19/246/19/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L J-LOW-L6/19/246/19/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDNaphthalene
ug/L 6/19/246/19/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDStyrene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDToluene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L 6/19/246/19/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 6/19/246/19/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 6/19/246/19/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 17 of 46Page 17 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Sample ID: Equipment Blank
Lab ID: 24F1419-14Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/17/24 12:20
Preparation
Date/Time
Sampled By: client
Minimum
Reporting
Limit MethodResult
BETX Compounds
mg/L 6/19/246/19/240.125 EPA 8260D/5030BNDC5-C6 Aliphatic hydrocarbons
mg/L 6/19/246/19/240.125 EPA 8260D/5030BNDC7-C8 Aliphatic hydrocarbons
mg/L 6/19/246/19/240.125 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/L 6/19/246/19/240.125 EPA 8260D/5030BNDC9-C10 Alkyl Benzenes
mg/L 6/19/246/19/240.005 EPA 8260D/5030BNDBenzene
mg/L 6/19/246/19/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L 6/19/246/19/240.012 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 6/19/246/19/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 6/19/246/19/240.012 EPA 8260D/5030BNDToluene
mg/L 6/19/246/19/240.038 EPA 8260D/5030BNDXylenes, total
Semi-Volatile Compounds
ug/L 6/20/246/20/2410EPA 8270E/351154C11-12 Aliphatic hydrocarbons
ug/L 6/20/246/20/2410EPA 8270E/3511655C13-C16 Aliphatic hydrocarbons
ug/L 6/20/246/20/2410EPA 8270E/351160C17-C21 Aliphatic hydrocarbons
ug/L 6/20/246/20/2410EPA 8270E/3511596C22-C35 Aliphatic hydrocarbons
ug/L 6/20/246/20/2410EPA 8270E/3511NDC11-C13 Alkyl Naphthalenes
ug/L 6/20/246/20/2410EPA 8270E/3511NDTotal C12-C22 PAH
ug/L 6/20/246/20/2410EPA 8270E/3511NDAcenaphthene
ug/L 6/20/246/20/2410EPA 8270E/3511NDAcenaphthylene
ug/L 6/20/246/20/2410EPA 8270E/3511NDAnthracene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (a) anthracene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (a) pyrene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (b) fluoranthene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (g,h,i) perylene
ug/L 6/20/246/20/2410EPA 8270E/3511NDBenzo (k) fluoranthene
ug/L 6/20/246/20/2410EPA 8270E/3511NDChrysene
ug/L 6/20/246/20/2410EPA 8270E/3511NDDibenzo (a,h) anthracene
ug/L 6/20/246/20/2410EPA 8270E/3511NDFluoranthene
ug/L 6/20/246/20/2410EPA 8270E/3511NDFluorene
ug/L 6/20/246/20/2410EPA 8270E/3511NDIndeno (1,2,3-cd) pyrene
ug/L 6/20/246/20/2410EPA 8270E/3511NDPhenanthrene
ug/L 6/20/246/20/2410EPA 8270E/3511NDPyrene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 18 of 46Page 18 of 47
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/18/24 11:08 @ 4.5 °C
6/28/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-C = Estimated low due to low recovery of CCV
J-LOW-L = Estimated low due to low recovery of LCS
MS-Low = Estimated low due to Matrix Spike recovery.
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F1419
www.ChemtechFord.com
Page 19 of 46Page 19 of 47
Page 20 of 47
Page 21 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYF0795-DUP1 QC Source Sample: 24F1419-02Batch: BYF0795
Date Prepared: 06/18/2024 Date Analyzed: 06/19/2024
Total Solids 1.24 20 80.9 79.9 0.1 1.00
QC Sample ID: BYF0795-DUP2 QC Source Sample: 24F1419-11Batch: BYF0795
Date Prepared: 06/18/2024 Date Analyzed: 06/19/2024
Total Solids 1.83 20 82.4 80.9 0.1 1.00
QC Sample ID: BYF0795-DUP3 QC Source Sample: 24F1419-12Batch: BYF0795
Date Prepared: 06/18/2024 Date Analyzed: 06/19/2024
Total Solids 2.04 20 94.1 96.0 0.1 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 22 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - EPA 1010MOD
QC Sample ID: BYF1146-DUP1 QC Source Sample: 24F1419-11Batch: BYF1146
Date Prepared: 06/25/2024 Date Analyzed: 06/25/2024
Flashpoint 0.00 200 >200 >200 80.0 1.00
Z-01 - >200
Reference - EPA 1010MOD
QC Sample ID: BYF1146-SRM1 Batch: BYF1146
Date Prepared: 06/25/2024 Date Analyzed: 06/25/2024
Flashpoint 98.4 96.06 - 103.7 125 127 80.0 1.00
QC Sample ID: BYF1146-SRM2 Batch: BYF1146
Date Prepared: 06/25/2024 Date Analyzed: 06/25/2024
Flashpoint 100 96.06 - 103.7 127 127 80.0 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 23 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 1311
QC Sample ID: BYF0886-BLK1 Batch: BYF0886
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Percent Pass ND 0.1 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 24 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
QC Sample ID: BYF0896-DUP1 QC Source Sample: 24F1419-11Batch: BYF0896
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Oil & Grease (HEM)200 ND 185 307 1.00
Blank - EPA 1664BMod
QC Sample ID: BYF0896-BLK1 Batch: BYF0896
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Oil & Grease (HEM)ND 250 1.00
LCS - EPA 1664BMod
QC Sample ID: BYF0896-BS1 Batch: BYF0896
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Oil & Grease (HEM)96.5 78 - 114 1930 2000 250 1.00
LCS Dup - EPA 1664BMod
QC Sample ID: BYF0896-BSD1 Batch: BYF0896
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Oil & Grease (HEM)94.5 2.09 78 - 114 18 1890 2000 250 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 25 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6010D
QC Sample ID: BYF0847-BLK1 Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total ND 5.00 1.00
Barium, Total ND 0.500 1.00
Cadmium, Total ND 0.500 1.00
Chromium, Total ND 0.500 1.00
Lead, Total ND 5.00 1.00
Selenium, Total ND 3.00 1.00
Silver, Total ND 0.500 1.00
QC Sample ID: BYF0954-BLK1 Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP ND 0.50 1.00
Lead, TCLP ND 0.20 1.00
QC Sample ID: BYF0954-BLK2 Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP ND 0.50 1.00
Lead, TCLP ND 0.20 1.00
QC Sample ID: BYF1385-BLK1 Batch: BYF1385
Date Prepared: 06/28/2024 Date Analyzed: 06/28/2024
Lead, TCLP ND 0.20 1.00
LCS - EPA 6010D
QC Sample ID: BYF0847-BS1 Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total 105 85 - 115 210 200 5.00 1.00
Barium, Total 101 85 - 115 25.2 24.9 0.500 1.00
Cadmium, Total 107 85 - 115 213 200 0.500 1.00
Chromium, Total 103 85 - 115 206 200 0.500 1.00
Lead, Total 102 85 - 115 205 200 5.00 1.00
Selenium, Total 82.8 85 - 115 166 200 3.00 1.00
NR - No analyte requiring this QC element is included in this analytical bracket.
Silver, Total 104 85 - 115 10.3 9.95 0.500 1.00
QC Sample ID: BYF0954-BS1 Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP 118 85 - 115 2.36 2.00 0.50 1.00
QM-11 - The Laboratory Control Sample recovery was outside acceptance limits. The analytical batch was accepted based on
the recovery of the Method Spike.
Lead, TCLP 106 85 - 115 2.11 2.00 0.20 1.00
QC Sample ID: BYF1385-BS1 Batch: BYF1385
Date Prepared: 06/28/2024 Date Analyzed: 06/28/2024
Lead, TCLP 99.5 85 - 115 1.99 2.00 0.20 1.00
Matrix Spike - EPA 6010D
QC Sample ID: BYF0847-MS2 QC Source Sample: 24F1419-11Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total 81.6 75 - 125 72.4 15.2 70.1 1.75 1.00
Barium, Total 81.3 75 - 125 136 129 8.72 0.175 1.00
Cadmium, Total 78.4 75 - 125 55.5 0.536 70.1 0.175 1.00
Chromium, Total 85.8 75 - 125 69.5 9.37 70.1 0.175 1.00
Lead, Total 72.8 75 - 125 222 171 70.1 1.75 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 26 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 6010D (cont.)
QC Sample ID: BYF0847-MS2 QC Source Sample: 24F1419-11Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Selenium, Total 67.8 75 - 125 47.5 ND 70.1 1.05 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Silver, Total 95.9 75 - 125 3.34 ND 3.49 0.175 1.00
QC Sample ID: BYF0954-MS1 QC Source Sample: 24F1419-12Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP 89.4 75 - 125 2.07 0.28 2.00 0.50 1.00
Lead, TCLP 111 75 - 125 3.50 1.27 2.00 0.20 1.00
QC Sample ID: BYF1385-MS1 QC Source Sample: 24F1419-11Batch: BYF1385
Date Prepared: 06/28/2024 Date Analyzed: 06/28/2024
Lead, TCLP 103 75 - 125 2.48 0.42 2.00 0.20 1.00
Matrix Spike Dup - EPA 6010D
QC Sample ID: BYF0847-MSD2 QC Source Sample: 24F1419-11Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total 83.6 3.39 75 - 125 20 74.9 15.2 71.4 1.78 1.00
Barium, Total 44.6 2.33 75 - 125 20 133 129 8.88 0.178 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Cadmium, Total 81.3 5.41 75 - 125 25 58.5 0.536 71.4 0.178 1.00
Chromium, Total 92.0 7.69 75 - 125 20 75.0 9.37 71.4 0.178 1.00
Lead, Total 108 11.2 75 - 125 20 248 171 71.4 1.78 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Selenium, Total 68.5 2.90 75 - 125 20 48.9 ND 71.4 1.07 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Silver, Total 95.8 1.74 75 - 125 20 3.40 ND 3.55 0.178 1.00
QC Sample ID: BYF0954-MSD1 QC Source Sample: 24F1419-12Batch: BYF0954
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Arsenic, TCLP 92.4 2.90 75 - 125 20 2.13 0.28 2.00 0.50 1.00
Lead, TCLP 105 4.03 75 - 125 20 3.36 1.27 2.00 0.20 1.00
QC Sample ID: BYF1385-MSD1 QC Source Sample: 24F1419-11Batch: BYF1385
Date Prepared: 06/28/2024 Date Analyzed: 06/28/2024
Lead, TCLP 99.7 2.37 75 - 125 20 2.42 0.42 2.00 0.20 1.00
Reference - EPA 6010D
QC Sample ID: BYF0847-SRM1 Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Arsenic, Total 83.6 60.07 - 111.31 237 283 10.8 1.00
Barium, Total 94.7 67.8 - 113.2 309 326 1.08 1.00
Cadmium, Total 93.3 65.97 - 109.6 89.4 95.8 1.08 1.00
Chromium, Total 91.5 62.34 - 115.9 219 239 1.08 1.00
Lead, Total 92.0 67.62 - 117.14 193 210 10.8 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 27 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Reference - EPA 6010D (cont.)
QC Sample ID: BYF0847-SRM1 Batch: BYF0847
Date Prepared: 06/19/2024 Date Analyzed: 06/20/2024
Selenium, Total 84.4 67.26 - 126.33 237 281 6.47 1.00
Silver, Total 91.5 65.78 - 119.83 75.7 82.7 1.08 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 28 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 7471A
QC Sample ID: BYF0833-BLK1 Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total ND 0.030 1.00
Duplicate - EPA 7471A
QC Sample ID: BYF0833-DUP1 QC Source Sample: 24F1419-11Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total 17.2 20 0.089 0.075 0.017 1.00
Matrix Spike - EPA 7471A
QC Sample ID: BYF0833-MS1 QC Source Sample: 24F1419-11Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total 139 70 - 130 1.24 0.075 0.839 0.030 1.00
QM-010 - The MS recovery was outside acceptance limits but passed Duplicate Spike acceptance limits. The batch was
accepted based on the acceptability of the MSD as the batch Spike.
Matrix Spike Dup - EPA 7471A
QC Sample ID: BYF0833-MSD1 QC Source Sample: 24F1419-11Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total 101 19.1 70 - 130 20 1.02 0.075 0.944 0.034 1.00
Reference - EPA 7471A
QC Sample ID: BYF0833-SRM1 Batch: BYF0833
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Mercury, Total 57.8 54.636 - 127.27 6.36 11.0 0.688 10.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 29 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYF0810-BLK1 Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane ND 0.001 1.00
1,1,2-Trichloroethane ND 0.001 1.00
1,1,2-Trichlorotrifluoroethane ND 0.001 1.00
1,1-Dichloroethene ND 0.001 1.00
1,2-Dichlorobenzene ND 0.001 1.00
1,2-Dichloroethane ND 0.001 1.00
1,4-Dichlorobenzene ND 0.001 1.00
2-Nitropropane ND 0.002 1.00
Acetone ND 0.02 1.00
Benzene ND 0.0004 1.00
C5-C6 Aliphatic hydrocarbons ND 0.01 1.00
C7-C8 Aliphatic hydrocarbons ND 0.01 1.00
C9-C10 Aliphatic hydrocarbons ND 0.01 1.00
C9-C10 Alkyl Benzenes ND 0.01 1.00
Carbon Disulfide ND 0.002 1.00
Carbon Tetrachloride ND 0.001 1.00
Chlorobenzene ND 0.001 1.00
Chloroform ND 0.001 1.00
Cyclohexanone ND 0.01 1.00
Ethyl Acetate ND 0.002 1.00
Ethyl Ether ND 0.001 1.00
Ethylbenzene ND 0.001 1.00
Hexachlorobutadiene ND 0.001 1.00
Isobutanol ND 0.02 1.00
Methyl Ethyl Ketone ND 0.002 1.00
Methyl Isobutyl Ketone ND 0.005 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.001 1.00
Methylene Chloride ND 0.001 1.00
Naphthalene ND 0.001 1.00
n-Butyl Alcohol ND 0.05 1.00
Tetrachloroethene ND 0.001 1.00
Toluene ND 0.001 1.00
Trichloroethene ND 0.001 1.00
Trichlorofluoromethane ND 0.001 1.00
Vinyl Chloride ND 0.0008 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYF0881-BLK1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 30 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYF0881-BLK1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.0004 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
C5-C6 Aliphatic hydrocarbons ND 0.010 1.00
C7-C8 Aliphatic hydrocarbons ND 0.010 1.00
C9-C10 Aliphatic hydrocarbons ND 0.010 1.00
C9-C10 Alkyl Benzenes ND 0.010 1.00
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 0.001 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.001 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 0.001 1.00
n-Butyl Alcohol ND 50.0 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 31 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYF0881-BLK1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 0.001 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYF0810-BS1 Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 88.4 70 - 130 0.009 0.0100 0.001 1.00
1,1,2-Trichloroethane 98.0 70 - 130 0.01 0.0100 0.001 1.00
1,1,2-Trichlorotrifluoroethane 52.9 70 - 130 0.005 0.0100 0.001 1.00
J-LOW-L - Estimated low due to low recovery of LCS
1,1-Dichloroethene 78.9 70 - 130 0.008 0.0100 0.001 1.00
1,2-Dichlorobenzene 110 70 - 130 0.01 0.0100 0.001 1.00
1,2-Dichloroethane 97.4 70 - 130 0.01 0.0100 0.001 1.00
1,4-Dichlorobenzene 114 70 - 130 0.01 0.0100 0.001 1.00
2-Nitropropane 49.4 70 - 130 0.01 0.0300 0.002 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Acetone 97.3 70 - 130 0.1 0.100 0.02 1.00
Benzene 94.2 70 - 130 0.009 0.0100 0.0004 1.00
Carbon Disulfide 41.4 70 - 130 0.004 0.0100 0.002 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Carbon Tetrachloride 80.2 70 - 130 0.008 0.0100 0.001 1.00
Chlorobenzene 97.7 70 - 130 0.01 0.0100 0.001 1.00
Chloroform 92.4 70 - 130 0.009 0.0100 0.001 1.00
Cyclohexanone 137 70 - 130 0.1 0.100 0.01 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Acetate 90.1 70 - 130 0.02 0.0200 0.002 1.00
Ethyl Ether 89.8 70 - 130 0.009 0.0100 0.001 1.00
Ethylbenzene 94.3 70 - 130 0.009 0.0100 0.001 1.00
Hexachlorobutadiene 101 70 - 130 0.01 0.0100 0.001 1.00
Isobutanol 95.6 70 - 130 0.2 0.200 0.02 1.00
Methyl Ethyl Ketone 95.6 70 - 130 0.01 0.0100 0.002 1.00
Methyl Isobutyl Ketone 113 70 - 130 0.01 0.0100 0.005 1.00
Methylene Chloride 88.7 70 - 130 0.009 0.0100 0.001 1.00
n-Butyl Alcohol 100 70 - 130 0.1 0.100 0.05 1.00
Tetrachloroethene 93.2 70 - 130 0.009 0.0100 0.001 1.00
Toluene 89.2 70 - 130 0.009 0.0100 0.001 1.00
Trichloroethene 97.4 70 - 130 0.01 0.0100 0.001 1.00
Trichlorofluoromethane 78.5 70 - 130 0.008 0.0100 0.001 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 32 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYF0810-BS1 Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
Vinyl Chloride 116 70 - 130 0.01 0.0100 0.0008 1.00
Xylenes, total 95.4 70 - 130 0.03 0.0300 0.003 1.00
QC Sample ID: BYF0881-BS1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
1,1,1,2-Tetrachloroethane 107 70 - 130 10.7 10.0 1.0 1.00
1,1,1-Trichloroethane 99.7 70 - 130 9.97 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 116 70 - 130 11.6 10.0 1.0 1.00
1,1,2-Trichloroethane 104 70 - 130 10.4 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 98.5 70 - 130 9.85 10.0 1.0 1.00
1,1-Dichloroethane 74.8 70 - 130 7.48 10.0 1.0 1.00
1,1-Dichloroethene 98.8 70 - 130 9.88 10.0 1.0 1.00
1,1-Dichloropropene 101 70 - 130 10.1 10.0 1.0 1.00
1,2,3-Trichlorobenzene 118 70 - 130 11.8 10.0 1.0 1.00
1,2,3-Trichloropropane 113 70 - 130 11.3 10.0 1.0 1.00
1,2,4-Trichlorobenzene 122 70 - 130 12.2 10.0 1.0 1.00
1,2,4-Trimethylbenzene 113 70 - 130 11.3 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 113 70 - 130 11.3 10.0 1.0 1.00
1,2-Dibromoethane (EDB)107 70 - 130 10.7 10.0 1.0 1.00
1,2-Dichlorobenzene 114 70 - 130 11.4 10.0 1.0 1.00
1,2-Dichloroethane 96.2 70 - 130 9.62 10.0 1.0 1.00
1,2-Dichloropropane 99.2 70 - 130 9.92 10.0 1.0 1.00
1,3,5-Trimethylbenzene 113 70 - 130 11.3 10.0 1.0 1.00
1,3-Dichlorobenzene 115 70 - 130 11.5 10.0 1.0 1.00
1,3-Dichloropropane 102 70 - 130 10.2 10.0 1.0 1.00
1,4-Dichlorobenzene 113 70 - 130 11.3 10.0 1.0 1.00
2,2-Dichloropropane 84.8 70 - 130 8.48 10.0 1.0 1.00
2-Chlorotoluene 108 70 - 130 10.8 10.0 1.0 1.00
2-Hexanone 113 70 - 130 11.3 10.0 10.0 1.00
2-Nitropropane 70.2 70 - 130 21.0 30.0 2.0 1.00
4-Chlorotoluene 109 70 - 130 10.9 10.0 1.0 1.00
Acetone 92.9 70 - 130 92.9 100 20.0 1.00
Acrylonitrile 91.3 70 - 130 45.6 50.0 5.0 1.00
Benzene 102 70 - 130 0.010 0.0100 0.0004 1.00
Bromobenzene 108 70 - 130 10.8 10.0 1.0 1.00
Bromochloromethane 95.4 70 - 130 9.54 10.0 1.0 1.00
Bromodichloromethane 101 70 - 130 10.1 10.0 1.0 1.00
Bromoform 110 70 - 130 11.0 10.0 1.0 1.00
Bromomethane 77.2 70 - 130 7.72 10.0 2.0 1.00
Carbon Disulfide 80.2 70 - 130 8.02 10.0 2.0 1.00
Carbon Tetrachloride 105 70 - 130 10.5 10.0 1.0 1.00
Chlorobenzene 104 70 - 130 10.4 10.0 1.0 1.00
Chloroethane 89.3 70 - 130 8.93 10.0 1.0 1.00
Chloroform 95.5 70 - 130 9.55 10.0 1.0 1.00
Chloromethane 79.2 70 - 130 7.92 10.0 1.0 1.00
cis-1,2-Dichloroethene 97.1 70 - 130 9.71 10.0 1.0 1.00
cis-1,3-Dichloropropene 104 70 - 130 10.4 10.0 1.0 1.00
Cyclohexanone 336 70 - 130 336 100 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Dibromochloromethane 107 70 - 130 10.7 10.0 1.0 1.00
Dibromomethane 108 70 - 130 10.8 10.0 1.0 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 33 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYF0881-BS1 Batch: BYF0881
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
Dichlorodifluoromethane 78.4 70 - 130 7.84 10.0 1.0 1.00
Ethyl Acetate 93.8 70 - 130 18.8 20.0 2.0 1.00
Ethyl Ether 89.1 70 - 130 8.91 10.0 1.0 1.00
Ethylbenzene 105 70 - 130 10.5 10.0 1.0 1.00
Hexachlorobutadiene 116 70 - 130 11.6 10.0 1.0 1.00
Isobutanol 88.8 70 - 130 178 200 20.0 1.00
Isopropylbenzene 112 70 - 130 11.2 10.0 1.0 1.00
Methyl Ethyl Ketone 117 70 - 130 11.7 10.0 2.0 1.00
Methyl Isobutyl Ketone 97.5 70 - 130 9.75 10.0 5.0 1.00
Methylene Chloride 90.6 70 - 130 9.06 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)65.9 70 - 130 6.59 10.0 0.6 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 118 70 - 130 11.8 10.0 1.0 1.00
n-Butyl Alcohol 93.3 70 - 130 93.3 100 50.0 1.00
n-Butylbenzene 118 70 - 130 11.8 10.0 1.0 1.00
n-Propyl Benzene 111 70 - 130 11.1 10.0 1.0 1.00
Pentachloroethane 112 70 - 130 11.2 10.0 1.0 1.00
p-Isopropyltoluene 117 70 - 130 11.7 10.0 1.0 1.00
sec-Butyl Benzene 115 70 - 130 11.5 10.0 1.0 1.00
Styrene 111 70 - 130 11.1 10.0 1.0 1.00
tert-Butylbenzene 115 70 - 130 11.5 10.0 1.0 1.00
Tetrachloroethene 98.2 70 - 130 9.82 10.0 1.0 1.00
Toluene 100 70 - 130 0.010 0.0100 0.001 1.00
trans-1,2-Dichloroethene 95.3 70 - 130 9.53 10.0 1.0 1.00
trans-1,3-Dichloropropene 104 70 - 130 10.4 10.0 1.0 1.00
Trichloroethene 102 70 - 130 10.2 10.0 1.0 1.00
Trichlorofluoromethane 95.2 70 - 130 9.52 10.0 1.0 1.00
Vinyl Chloride 93.2 70 - 130 9.32 10.0 0.8 1.00
Xylenes, total 109 70 - 130 32.8 30.0 3.0 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYF0810-MS1 QC Source Sample: 24F1419-02Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 86.9 70 - 130 0.2 ND 0.282 0.03 1.00
1,1,2-Trichloroethane 125 70 - 130 0.4 ND 0.282 0.03 1.00
1,1,2-Trichlorotrifluoroethane 55.5 70 - 130 0.2 ND 0.282 0.03 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1-Dichloroethene 78.7 70 - 130 0.2 ND 0.282 0.03 1.00
1,2-Dichlorobenzene 99.9 70 - 130 0.3 ND 0.282 0.03 1.00
1,2-Dichloroethane 102 70 - 130 0.3 ND 0.282 0.03 1.00
1,4-Dichlorobenzene 108 70 - 130 0.3 ND 0.282 0.03 1.00
2-Nitropropane 120 70 - 130 1 ND 0.845 0.06 1.00
Acetone 118 70 - 130 3 ND 2.82 0.56 1.00
Benzene -30.0 70 - 130 0.67 0.75 0.282 0.01 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Disulfide 40.8 70 - 130 0.1 ND 0.282 0.06 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 34 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYF0810-MS1 QC Source Sample: 24F1419-02Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Tetrachloride 82.4 70 - 130 0.2 ND 0.282 0.03 1.00
Chlorobenzene 93.2 70 - 130 0.3 ND 0.282 0.03 1.00
Chloroform 94.3 70 - 130 0.3 ND 0.282 0.03 1.00
Cyclohexanone 62.2 70 - 130 2 ND 2.82 0.28 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Ethyl Acetate 306 70 - 130 2 ND 0.563 0.06 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Ether 89.7 70 - 130 0.3 ND 0.282 0.03 1.00
Ethylbenzene 39.1 70 - 130 0.3 0.2 0.282 0.03 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Hexachlorobutadiene 38.7 70 - 130 0.1 ND 0.282 0.03 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Isobutanol 189 70 - 130 11 ND 5.63 0.56 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Methyl Ethyl Ketone 105 70 - 130 0.3 ND 0.282 0.06 1.00
Methyl Isobutyl Ketone 101 70 - 130 0.3 ND 0.282 0.14 1.00
Methylene Chloride 90.4 70 - 130 0.3 ND 0.282 0.03 1.00
n-Butyl Alcohol 245 70 - 130 7 ND 2.82 1.41 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Tetrachloroethene 156 70 - 130 0.4 ND 0.282 0.03 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Toluene 91.3 70 - 130 0.26 ND 0.282 0.03 1.00
Trichloroethene 75.5 70 - 130 0.2 ND 0.282 0.03 1.00
Trichlorofluoromethane 84.1 70 - 130 0.2 ND 0.282 0.03 1.00
Vinyl Chloride 118 70 - 130 0.3 ND 0.282 0.02 1.00
Xylenes, total 53.3 70 - 130 0.8 0.4 0.845 0.08 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
QC Sample ID: BYF0810-MS2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 55.5 70 - 130 1 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1,2-Trichloroethane 92.2 70 - 130 2 ND 2.21 0.22 1.00
1,1,2-Trichlorotrifluoroethane 32.3 70 - 130 0.7 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1-Dichloroethene 48.5 70 - 130 1 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,2-Dichlorobenzene 86.3 70 - 130 2 ND 2.21 0.22 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 35 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYF0810-MS2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,2-Dichloroethane 84.6 70 - 130 2 ND 2.21 0.22 1.00
1,4-Dichlorobenzene 80.4 70 - 130 2 ND 2.21 0.22 1.00
2-Nitropropane 29.4 70 - 130 2 ND 6.62 0.44 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Acetone 94.5 70 - 130 21 ND 22.1 4.41 1.00
Benzene 76.2 70 - 130 1.80 0.12 2.21 0.09 1.00
Carbon Disulfide 26.1 70 - 130 0.6 ND 2.21 0.44 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Tetrachloride 50.2 70 - 130 1 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Chlorobenzene 76.4 70 - 130 2 ND 2.21 0.22 1.00
Chloroform 68.2 70 - 130 2 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Cyclohexanone 24.0 70 - 130 5 ND 22.1 2.21 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Ethyl Acetate 91.1 70 - 130 4 ND 4.41 0.44 1.00
Ethyl Ether 79.3 70 - 130 2 ND 2.21 0.22 1.00
Ethylbenzene 73.1 70 - 130 2 0.4 2.21 0.22 1.00
Hexachlorobutadiene 39.7 70 - 130 0.9 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Isobutanol 31.1 70 - 130 14 ND 44.1 4.41 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Methyl Ethyl Ketone 114 70 - 130 3 ND 2.21 0.44 1.00
Methyl Isobutyl Ketone 103 70 - 130 2 ND 2.21 1.10 1.00
Methylene Chloride 69.8 70 - 130 2 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
n-Butyl Alcohol 119 70 - 130 26 ND 22.1 11.0 1.00
Tetrachloroethene 120 70 - 130 3 ND 2.21 0.22 1.00
Toluene 84.1 70 - 130 1.86 ND 2.21 0.22 1.00
Trichloroethene 134 70 - 130 3 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Trichlorofluoromethane 43.7 70 - 130 1 ND 2.21 0.22 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Vinyl Chloride 63.2 70 - 130 1 ND 2.21 0.18 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 36 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYF0810-MS2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Xylenes, total 77.7 70 - 130 7 2 6.62 0.66 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYF0810-MSD1 QC Source Sample: 24F1419-02Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 80.8 13.7 70 - 130 20 0.3 ND 0.347 0.03 1.00
1,1,2-Trichloroethane 111 9.50 70 - 130 20 0.4 ND 0.347 0.03 1.00
1,1,2-Trichlorotrifluoroethane 51.4 13.3 70 - 130 20 0.2 ND 0.347 0.03 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1-Dichloroethene 74.2 15.1 70 - 130 20 0.3 ND 0.347 0.03 1.00
1,2-Dichlorobenzene 102 22.7 70 - 130 20 0.4 ND 0.347 0.03 1.00
RPD-01 - RPD between MS and MSD is outside established limits. Data is acceptable based on MS and MSD being within
acceptable recovery limits.
1,2-Dichloroethane 91.2 9.38 70 - 130 20 0.3 ND 0.347 0.03 1.00
1,4-Dichlorobenzene 94.8 7.84 70 - 130 20 0.3 ND 0.347 0.03 1.00
2-Nitropropane 88.8 9.41 70 - 130 20 0.9 ND 1.04 0.07 1.00
Acetone 110 13.8 70 - 130 20 4 ND 3.47 0.69 1.00
Benzene -31.2 3.61 70 - 130 20 0.65 0.75 0.347 0.01 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Disulfide 39.3 17.2 70 - 130 20 0.1 ND 0.347 0.07 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Tetrachloride 72.7 8.44 70 - 130 20 0.3 ND 0.347 0.03 1.00
Chlorobenzene 86.5 13.5 70 - 130 20 0.3 ND 0.347 0.03 1.00
Chloroform 86.3 12.1 70 - 130 20 0.3 ND 0.347 0.03 1.00
Cyclohexanone 76.1 40.5 70 - 130 20 3 ND 3.47 0.35 1.00
RPD-MSOut - The RPD between MS and MSD is outside established control limits.
Ethyl Acetate 228 8.53 70 - 130 20 2 ND 0.695 0.07 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Ether 88.3 19.3 70 - 130 20 0.3 ND 0.347 0.03 1.00
Ethylbenzene 60.3 29.1 70 - 130 20 0.4 0.2 0.347 0.03 1.00
RPD-MSOut - The RPD between MS and MSD is outside established control limits.
Hexachlorobutadiene 40.2 24.6 70 - 130 20 0.1 ND 0.347 0.03 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Isobutanol 151 1.49 70 - 130 20 10 ND 6.95 0.69 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Methyl Ethyl Ketone 83.1 2.70 70 - 130 20 0.3 ND 0.347 0.07 1.00
Methyl Isobutyl Ketone 92.5 11.8 70 - 130 20 0.3 ND 0.347 0.17 1.00
Methylene Chloride 85.1 14.9 70 - 130 20 0.3 ND 0.347 0.03 1.00
n-Butyl Alcohol 170 15.6 70 - 130 20 6 ND 3.47 1.74 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
CtF WO#: 24F1419
www.ChemtechFord.com Page 37 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYF0810-MSD1 QC Source Sample: 24F1419-02Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
Tetrachloroethene 149 15.9 70 - 130 20 0.5 ND 0.347 0.03 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Toluene 82.9 11.3 70 - 130 20 0.29 ND 0.347 0.03 1.00
Trichloroethene 105 53.0 70 - 130 20 0.4 ND 0.347 0.03 1.00
RPD-01 - RPD between MS and MSD is outside established limits. Data is acceptable based on MS and MSD being within
acceptable recovery limits.
Trichlorofluoromethane 77.5 12.8 70 - 130 20 0.3 ND 0.347 0.03 1.00
Vinyl Chloride 111 14.6 70 - 130 20 0.4 ND 0.347 0.03 1.00
Xylenes, total 75.4 34.2 70 - 130 20 1 0.4 1.04 0.10 1.00
RPD-MSOut - The RPD between MS and MSD is outside established control limits.
QC Sample ID: BYF0810-MSD2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
1,1,1-Trichloroethane 52.8 10.4 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1,2-Trichloroethane 90.1 13.1 70 - 130 20 2 ND 2.57 0.26 1.00
1,1,2-Trichlorotrifluoroethane 28.9 4.29 70 - 130 20 0.7 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,1-Dichloroethene 44.2 6.13 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
1,2-Dichlorobenzene 84.7 13.5 70 - 130 20 2 ND 2.57 0.26 1.00
1,2-Dichloroethane 81.7 11.9 70 - 130 20 2 ND 2.57 0.26 1.00
1,4-Dichlorobenzene 72.3 4.80 70 - 130 20 2 ND 2.57 0.26 1.00
2-Nitropropane 26.7 5.78 70 - 130 20 2 ND 7.72 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Acetone 91.9 12.5 70 - 130 20 24 ND 25.7 5.15 1.00
Benzene 73.5 11.1 70 - 130 20 2.01 0.12 2.57 0.10 1.00
Carbon Disulfide 23.3 4.07 70 - 130 20 0.6 ND 2.57 0.51 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Carbon Tetrachloride 46.7 8.18 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Chlorobenzene 72.6 10.3 70 - 130 20 2 ND 2.57 0.26 1.00
Chloroform 65.3 11.1 70 - 130 20 2 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Cyclohexanone 26.2 24.1 70 - 130 20 7 ND 25.7 2.57 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Ethyl Acetate 82.8 5.87 70 - 130 20 4 ND 5.15 0.51 1.00
Ethyl Ether 77.6 13.2 70 - 130 20 2 ND 2.57 0.26 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 38 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYF0810-MSD2 QC Source Sample: 24F1419-11Batch: BYF0810
Date Prepared: 06/18/2024 Date Analyzed: 06/18/2024
Ethylbenzene 73.9 13.3 70 - 130 20 2 0.4 2.57 0.26 1.00
Hexachlorobutadiene 39.5 14.9 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Isobutanol 24.1 10.1 70 - 130 20 12 ND 51.5 5.15 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Methyl Ethyl Ketone 115 16.0 70 - 130 20 3 ND 2.57 0.51 1.00
Methyl Isobutyl Ketone 97.9 10.3 70 - 130 20 3 ND 2.57 1.29 1.00
Methylene Chloride 66.8 11.0 70 - 130 20 2 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
n-Butyl Alcohol 113 10.4 70 - 130 20 29 ND 25.7 12.9 1.00
Tetrachloroethene 120 15.2 70 - 130 20 3 ND 2.57 0.26 1.00
Toluene 80.1 10.5 70 - 130 20 2.06 ND 2.57 0.26 1.00
Trichloroethene 139 19.2 70 - 130 20 4 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Trichlorofluoromethane 40.2 7.06 70 - 130 20 1 ND 2.57 0.26 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Vinyl Chloride 57.7 6.31 70 - 130 20 1 ND 2.57 0.21 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Xylenes, total 89.4 21.1 70 - 130 20 9 2 7.72 0.77 1.00
RPD-01 - RPD between MS and MSD is outside established limits. Data is acceptable based on MS and MSD being within
acceptable recovery limits.
CtF WO#: 24F1419
www.ChemtechFord.com Page 39 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8270E
QC Sample ID: BYF0957-BLK1 Batch: BYF0957
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Acenaphthene ND 10 1.00
Acenaphthylene ND 10 1.00
Anthracene ND 10 1.00
Benzo (a) anthracene ND 10 1.00
Benzo (a) pyrene ND 10 1.00
Benzo (b) fluoranthene ND 10 1.00
Benzo (g,h,i) perylene ND 10 1.00
Benzo (k) fluoranthene ND 10 1.00
C11-12 Aliphatic hydrocarbons ND 10 1.00
C11-C13 Alkyl Naphthalenes ND 10 1.00
C13-C16 Aliphatic hydrocarbons ND 10 1.00
C17-C21 Aliphatic hydrocarbons ND 10 1.00
C22-C35 Aliphatic hydrocarbons ND 10 1.00
Chrysene ND 10 1.00
Dibenzo (a,h) anthracene ND 10 1.00
Fluoranthene ND 10 1.00
Fluorene ND 10 1.00
Indeno (1,2,3-cd) pyrene ND 10 1.00
Phenanthrene ND 10 1.00
Pyrene ND 10 1.00
Total C12-C22 PAH ND 10 1.00
QC Sample ID: BYF0957-BLK2 Batch: BYF0957
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Acenaphthene ND 10 1.00
Acenaphthylene ND 10 1.00
Anthracene ND 10 1.00
Benzo (a) anthracene ND 10 1.00
Benzo (a) pyrene ND 10 1.00
Benzo (b) fluoranthene ND 10 1.00
Benzo (g,h,i) perylene ND 10 1.00
Benzo (k) fluoranthene ND 10 1.00
C11-12 Aliphatic hydrocarbons ND 10 1.00
C11-C13 Alkyl Naphthalenes ND 10 1.00
C13-C16 Aliphatic hydrocarbons ND 10 1.00
C17-C21 Aliphatic hydrocarbons ND 10 1.00
C22-C35 Aliphatic hydrocarbons ND 10 1.00
Chrysene ND 10 1.00
Dibenzo (a,h) anthracene ND 10 1.00
Fluoranthene ND 10 1.00
Fluorene ND 10 1.00
Indeno (1,2,3-cd) pyrene ND 10 1.00
Phenanthrene ND 10 1.00
Pyrene ND 10 1.00
Total C12-C22 PAH ND 10 1.00
QC Sample ID: BYF1007-BLK1 Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Acenaphthene ND 0.40 1.00
Acenaphthylene ND 0.40 1.00
Anthracene ND 0.40 1.00
Benzo (a) anthracene ND 0.40 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 40 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8270E (cont.)
QC Sample ID: BYF1007-BLK1 Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Benzo (a) pyrene ND 0.40 1.00
Benzo (b) fluoranthene ND 0.40 1.00
Benzo (g,h,i) perylene ND 0.40 1.00
Benzo (k) fluoranthene ND 0.40 1.00
Chrysene ND 0.40 1.00
Fluoranthene ND 0.40 1.00
Fluorene ND 0.40 1.00
Indeno (1,2,3-cd) pyrene ND 0.40 1.00
Phenanthrene ND 0.40 1.00
Pyrene ND 0.40 1.00
LCS - EPA 8270E
QC Sample ID: BYF0957-BS1 Batch: BYF0957
Date Prepared: 06/20/2024 Date Analyzed: 06/20/2024
Acenaphthene 89.4 65 - 135 45 50.0 10 1.00
Acenaphthylene 96.2 65 - 135 48 50.0 10 1.00
Anthracene 95.5 65 - 135 48 50.0 10 1.00
Benzo (a) anthracene 99.3 65 - 135 50 50.0 10 1.00
Benzo (a) pyrene 108 65 - 135 54 50.0 10 1.00
Benzo (b) fluoranthene 104 65 - 135 52 50.0 10 1.00
Benzo (g,h,i) perylene 113 65 - 135 56 50.0 10 1.00
Benzo (k) fluoranthene 95.6 65 - 135 48 50.0 10 1.00
Chrysene 129 65 - 135 64 50.0 10 1.00
Dibenzo (a,h) anthracene 111 65 - 135 56 50.0 10 1.00
Fluoranthene 104 65 - 135 52 50.0 10 1.00
Fluorene 88.4 65 - 135 44 50.0 10 1.00
Indeno (1,2,3-cd) pyrene 114 65 - 135 57 50.0 10 1.00
Phenanthrene 100 65 - 135 50 50.0 10 1.00
Pyrene 103 65 - 135 51 50.0 10 1.00
QC Sample ID: BYF1007-BS1 Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Acenaphthene 68.9 47 - 145 0.5 0.667 0.40 1.00
Acenaphthylene 74.6 65 - 135 0.5 0.667 0.40 1.00
Anthracene 80.3 65 - 135 0.5 0.667 0.40 1.00
Benzo (a) anthracene 92.6 65 - 135 0.6 0.667 0.40 1.00
Benzo (a) pyrene 103 65 - 135 0.7 0.667 0.40 1.00
Benzo (b) fluoranthene 101 65 - 135 0.7 0.667 0.40 1.00
Benzo (g,h,i) perylene 106 65 - 135 0.7 0.667 0.40 1.00
Benzo (k) fluoranthene 99.8 65 - 135 0.7 0.667 0.40 1.00
Chrysene 120 65 - 135 0.8 0.667 0.40 1.00
Fluoranthene 99.9 65 - 135 0.7 0.667 0.40 1.00
Fluorene 67.4 65 - 135 0.4 0.667 0.40 1.00
Indeno (1,2,3-cd) pyrene 109 65 - 135 0.7 0.667 0.40 1.00
Phenanthrene 82.3 65 - 135 0.5 0.667 0.40 1.00
Pyrene 90.2 33 - 130 0.6 0.667 0.40 1.00
Matrix Spike - EPA 8270E
QC Sample ID: BYF1007-MS1 QC Source Sample: 24F1419-02Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Acenaphthene 75.4 47 - 145 2 ND 2.50 1.50 1.00
Acenaphthylene 80.0 50 - 150 2 ND 2.50 1.50 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 41 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8270E (cont.)
QC Sample ID: BYF1007-MS1 QC Source Sample: 24F1419-02Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Anthracene 84.1 50 - 150 2 ND 2.50 1.50 1.00
Benzo (a) anthracene 88.5 50 - 150 2 ND 2.50 1.50 1.00
Benzo (a) pyrene 97.9 50 - 150 2 ND 2.50 1.50 1.00
Benzo (b) fluoranthene 94.7 50 - 150 2 ND 2.50 1.50 1.00
Benzo (g,h,i) perylene 99.1 50 - 150 2 ND 2.50 1.50 1.00
Benzo (k) fluoranthene 92.8 50 - 150 2 ND 2.50 1.50 1.00
Chrysene 111 50 - 150 3 ND 2.50 1.50 1.00
Fluoranthene 109 50 - 150 3 ND 2.50 1.50 1.00
Fluorene 46.3 50 - 150 2 1 2.50 1.50 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Indeno (1,2,3-cd) pyrene 101 50 - 150 3 ND 2.50 1.50 1.00
Phenanthrene 44.8 50 - 150 5 3 2.50 1.50 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Pyrene 79.2 33 - 130 2 ND 2.50 1.50 1.00
Matrix Spike Dup - EPA 8270E
QC Sample ID: BYF1007-MSD1 QC Source Sample: 24F1419-02Batch: BYF1007
Date Prepared: 06/21/2024 Date Analyzed: 06/21/2024
Acenaphthene 77.5 2.78 47 - 145 200 2 ND 2.50 1.50 1.00
Acenaphthylene 71.5 11.2 50 - 150 200 2 ND 2.50 1.50 1.00
Anthracene 88.2 4.75 50 - 150 200 2 ND 2.50 1.50 1.00
Benzo (a) anthracene 92.5 4.38 50 - 150 200 2 ND 2.50 1.50 1.00
Benzo (a) pyrene 102 3.86 50 - 150 200 3 ND 2.50 1.50 1.00
Benzo (b) fluoranthene 100 5.49 50 - 150 200 3 ND 2.50 1.50 1.00
Benzo (g,h,i) perylene 109 9.56 50 - 150 200 3 ND 2.50 1.50 1.00
Benzo (k) fluoranthene 91.4 1.57 50 - 150 200 2 ND 2.50 1.50 1.00
Chrysene 117 5.07 50 - 150 200 3 ND 2.50 1.50 1.00
Fluoranthene 105 3.27 50 - 150 200 3 ND 2.50 1.50 1.00
Fluorene 52.1 6.09 50 - 150 200 2 1 2.50 1.50 1.00
Indeno (1,2,3-cd) pyrene 110 8.40 50 - 150 200 3 ND 2.50 1.50 1.00
Phenanthrene 44.1 0.354 50 - 150 200 5 3 2.50 1.50 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Pyrene 100 23.5 33 - 130 200 3 ND 2.50 1.50 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 42 of 47
QC Report for Work Order (WO) - 24F1419
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - EPA 9040C/9045D
QC Sample ID: BYF0827-DUP1 QC Source Sample: 24F1419-11Batch: BYF0827
Date Prepared: 06/19/2024 Date Analyzed: 06/19/2024
pH 0.00 3 10.5 10.5 0.1 1.00
CtF WO#: 24F1419
www.ChemtechFord.com Page 43 of 47
Surrogates Report for Work Order (WO) - 24F1419
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8260D
BYF0810-BLK1 1,2-Dichloroethane-d4 99.4 70 BYF0810 1.001300.00994 0.0100
BYF0810-BLK1 1,2-Dichloroethane-d4 99.4 70 BYF0810 1.001300.00994 0.0100
BYF0810-BLK1 Toluene-d8 98.9 70 BYF0810 1.001300.00989 0.0100
BYF0810-BLK1 4-Bromofluorobenzene 104 70 BYF0810 1.001300.0104 0.0100
BYF0810-BLK1 4-Bromofluorobenzene 104 70 BYF0810 1.001300.0104 0.0100
BYF0810-BLK1 Toluene-d8 98.9 70 BYF0810 1.001300.00989 0.0100
BYF0881-BLK1 1,2-Dichloroethane-d4 97.1 64.2 BYF0881 1.001269.71 10.0
BYF0881-BLK1 1,2-Dichloroethane-d4 97.1 70 BYF0881 1.001300.00971 0.0100
BYF0881-BLK1 Toluene-d8 101 70 BYF0881 1.001300.0101 0.0100
BYF0881-BLK1 4-Bromofluorobenzene 98.5 71.4 BYF0881 1.001259.85 10.0
BYF0881-BLK1 4-Bromofluorobenzene 98.5 70 BYF0881 1.001300.00985 0.0100
BYF0881-BLK1 Toluene-d8 101 63.2 BYF0881 1.0012910.1 10.0
LCS - EPA 8260D
BYF0810-BS1 1,2-Dichloroethane-d4 95.6 70 BYF0810 1.001300.00956 0.0100
BYF0810-BS1 1,2-Dichloroethane-d4 95.6 70 BYF0810 1.001300.00956 0.0100
BYF0810-BS1 Toluene-d8 93.0 70 BYF0810 1.001300.00930 0.0100
BYF0810-BS1 4-Bromofluorobenzene 100 70 BYF0810 1.001300.0100 0.0100
BYF0810-BS1 4-Bromofluorobenzene 100 70 BYF0810 1.001300.0100 0.0100
BYF0810-BS1 Toluene-d8 93.0 70 BYF0810 1.001300.00930 0.0100
BYF0881-BS1 1,2-Dichloroethane-d4 98.5 64.2 BYF0881 1.001269.85 10.0
BYF0881-BS1 1,2-Dichloroethane-d4 98.5 70 BYF0881 1.001300.00985 0.0100
BYF0881-BS1 Toluene-d8 101 70 BYF0881 1.001300.0101 0.0100
BYF0881-BS1 4-Bromofluorobenzene 100 70 BYF0881 1.001300.0100 0.0100
BYF0881-BS1 4-Bromofluorobenzene 100 71.4 BYF0881 1.0012510.0 10.0
BYF0881-BS1 Toluene-d8 101 63.2 BYF0881 1.0012910.1 10.0
Matrix Spike - EPA 8260D
BYF0810-MS2 1,2-Dichloroethane-d4 99.8 70 BYF0810 1.001302.20 2.21
BYF0810-MS1 1,2-Dichloroethane-d4 108 70 BYF0810 1.001300.303 0.282
BYF0810-MS2 1,2-Dichloroethane-d4 99.8 70 BYF0810 1.001302.20 2.21
BYF0810-MS1 1,2-Dichloroethane-d4 108 70 BYF0810 1.001300.303 0.282
BYF0810-MS1 Toluene-d8 99.4 70 BYF0810 1.001300.280 0.282
BYF0810-MS2 Toluene-d8 95.6 70 BYF0810 1.001302.11 2.21
BYF0810-MS2 4-Bromofluorobenzene 97.8 70 BYF0810 1.001302.16 2.21
BYF0810-MS2 4-Bromofluorobenzene 97.8 70 BYF0810 1.001302.16 2.21
BYF0810-MS1 4-Bromofluorobenzene 104 70 BYF0810 1.001300.293 0.282
BYF0810-MS1 4-Bromofluorobenzene 104 70 BYF0810 1.001300.293 0.282
BYF0810-MS2 Toluene-d8 95.6 70 BYF0810 1.001302.11 2.21
BYF0810-MS1 Toluene-d8 99.4 70 BYF0810 1.001300.280 0.282
BYF0881-MS1 1,2-Dichloroethane-d4 99.4 70 BYF0881 1.001300.0497 0.0500
BYF0881-MS1 1,2-Dichloroethane-d4 99.4 64.2 BYF0881 1.0012649.7 50.0
BYF0881-MS1 Toluene-d8 101 70 BYF0881 1.001300.0506 0.0500
BYF0881-MS1 4-Bromofluorobenzene 100 71.4 BYF0881 1.0012550.1 50.0
BYF0881-MS1 4-Bromofluorobenzene 100 70 BYF0881 1.001300.0501 0.0500
BYF0881-MS1 Toluene-d8 101 63.2 BYF0881 1.0012950.6 50.0
Matrix Spike Dup - EPA 8260D
BYF0810-MSD2 1,2-Dichloroethane-d4 98.3 70 BYF0810 1.001302.53 2.57
CtF WO#: 24F1419
www.ChemtechFord.com Page 44 of 47
Matrix Spike Dup - EPA 8260D (cont.)
BYF0810-MSD2 1,2-Dichloroethane-d4 98.3 70 BYF0810 1.001302.53 2.57
BYF0810-MSD1 1,2-Dichloroethane-d4 100 70 BYF0810 1.001300.349 0.347
BYF0810-MSD1 1,2-Dichloroethane-d4 100 70 BYF0810 1.001300.349 0.347
BYF0810-MSD2 Toluene-d8 96.3 70 BYF0810 1.001302.48 2.57
BYF0810-MSD1 Toluene-d8 93.7 70 BYF0810 1.001300.326 0.347
BYF0810-MSD2 4-Bromofluorobenzene 96.1 70 BYF0810 1.001302.47 2.57
BYF0810-MSD1 4-Bromofluorobenzene 101 70 BYF0810 1.001300.351 0.347
BYF0810-MSD2 4-Bromofluorobenzene 96.1 70 BYF0810 1.001302.47 2.57
BYF0810-MSD1 4-Bromofluorobenzene 101 70 BYF0810 1.001300.351 0.347
BYF0810-MSD1 Toluene-d8 93.7 70 BYF0810 1.001300.326 0.347
BYF0810-MSD2 Toluene-d8 96.3 70 BYF0810 1.001302.48 2.57
BYF0881-MSD1 1,2-Dichloroethane-d4 98.7 64.2 BYF0881 1.0012649.4 50.0
BYF0881-MSD1 1,2-Dichloroethane-d4 98.7 70 BYF0881 1.001300.0494 0.0500
BYF0881-MSD1 Toluene-d8 100 70 BYF0881 1.001300.0502 0.0500
BYF0881-MSD1 4-Bromofluorobenzene 100 71.4 BYF0881 1.0012550.0 50.0
BYF0881-MSD1 4-Bromofluorobenzene 100 70 BYF0881 1.001300.0500 0.0500
BYF0881-MSD1 Toluene-d8 100 63.2 BYF0881 1.0012950.0 50.0
Blank - EPA 8270E
BYF0957-BLK1 2-Fluorobiphenyl 71.4 16 BYF0957 1.0015289.3 125
BYF0957-BLK2 2-Fluorobiphenyl 75.2 16 BYF0957 1.0015293.9 125
BYF0957-BLK2 Terphenyl-dl4 82.4 41 BYF0957 1.00174 103 125
BYF0957-BLK1 Terphenyl-dl4 77.5 41 BYF0957 1.0017496.8 125
BYF1007-BLK1 2-Fluorobiphenyl 101 37 BYF1007 1.001400.336 0.333
BYF1007-BLK1 Terphenyl-dl4 88.9 31 BYF1007 1.001400.296 0.333
LCS - EPA 8270E
BYF0957-BS1 2-Fluorobiphenyl 90.8 16 BYF0957 1.00152114125
BYF0957-BS1 Terphenyl-dl4 81.9 41 BYF0957 1.00174 102 125
BYF1007-BS1 2-Fluorobiphenyl 109 37 BYF1007 1.001400.362 0.333
BYF1007-BS1 Terphenyl-dl4 98.5 31 BYF1007 1.001400.328 0.333
Matrix Spike - EPA 8270E
BYF0957-MS1 2-Fluorobiphenyl 84.3 16 BYF0957 1.0015242200005000000
BYF0957-MS1 Terphenyl-dl4 81.4 41 BYF0957 1.0017440700005000000
BYF1007-MS1 2-Fluorobiphenyl 101 37 BYF1007 1.001401.26 1.25
BYF1007-MS1 Terphenyl-dl4 79.3 31 BYF1007 1.001400.991 1.25
Matrix Spike Dup - EPA 8270E
BYF0957-MSD1 2-Fluorobiphenyl 83.5 16 BYF0957 1.0015241700005000000
BYF0957-MSD1 Terphenyl-dl4 80.8 41 BYF0957 1.0017440400005000000
BYF1007-MSD1 2-Fluorobiphenyl 88.4 37 BYF1007 1.001401.11 1.25
BYF1007-MSD1 Terphenyl-dl4 90.2 31 BYF1007 1.001401.13 1.25
CtF WO#: 24F1419
www.ChemtechFord.com Page 45 of 47
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
8260 TPH Fractionation
24F1419-01 4-Bromofluorobenzene 0.280 95.2 70 1300.294
24F1419-01 Toluene-d8 0.288 98.0 70 1300.294
24F1419-01 1,2-Dichloroethane-d4 0.307 104 70 1300.294
8270 TPH Fractionation
24F1419-01 2-Fluorobiphenyl 0.365 89.4 37 1400.408
24F1419-01 Terphenyl-dl4 0.328 80.4 31 1400.408
8260 TPH Fractionation
24F1419-02 1,2-Dichloroethane-d4 0.302 106 70 1300.284
24F1419-02 4-Bromofluorobenzene 0.320 113 70 1300.284
24F1419-02 Toluene-d8 0.263 92.6 70 1300.284
8270 TPH Fractionation
24F1419-02 2-Fluorobiphenyl 1.23 98.3 37 1401.25
24F1419-02 Terphenyl-dl4 1.10 88.3 31 1401.25
8260 TPH Fractionation
24F1419-03 Toluene-d8 2.01 95.7 70 1302.10
24F1419-03 1,2-Dichloroethane-d4 2.10 99.9 70 1302.10
24F1419-03 4-Bromofluorobenzene 2.00 95.0 70 1302.10
8270 TPH Fractionation
24F1419-03 2-Fluorobiphenyl 0.889 81.3 37 1401.09
24F1419-03 Terphenyl-dl4 0.815 74.5 31 1401.09
8260 TPH Fractionation
24F1419-04 1,2-Dichloroethane-d4 0.331 102 70 1300.325
24F1419-04 4-Bromofluorobenzene 0.315 97.0 70 1300.325
24F1419-04 Toluene-d8 0.302 93.0 70 1300.325
8270 TPH Fractionation
24F1419-04 2-Fluorobiphenyl 0.378 84.0 37 1400.450
24F1419-04 Terphenyl-dl4 0.381 84.5 31 1400.450
8260 TPH Fractionation
24F1419-05 1,2-Dichloroethane-d4 0.306 103 70 1300.297
24F1419-05 4-Bromofluorobenzene 0.285 96.0 70 1300.297
24F1419-05 Toluene-d8 0.284 95.7 70 1300.297
8270 TPH Fractionation
24F1419-05 2-Fluorobiphenyl 0.389 91.0 37 1400.427
24F1419-05 Terphenyl-dl4 0.364 85.3 31 1400.427
8260 TPH Fractionation
24F1419-06 4-Bromofluorobenzene 0.294 97.8 70 1300.300
24F1419-06 Toluene-d8 0.291 97.0 70 1300.300
24F1419-06 1,2-Dichloroethane-d4 0.310 103 70 1300.300
CtF WO#: 24F1419
www.ChemtechFord.com Page 46 of 47
8270 TPH Fractionation
24F1419-06 Terphenyl-dl4 0.358 81.3 31 1400.441
24F1419-06 2-Fluorobiphenyl 0.442 100 37 1400.441
8260 TPH Fractionation
24F1419-07 1,2-Dichloroethane-d4 0.311 102 70 1300.303
24F1419-07 4-Bromofluorobenzene 0.293 96.6 70 1300.303
24F1419-07 Toluene-d8 0.296 97.7 70 1300.303
8270 TPH Fractionation
24F1419-07 2-Fluorobiphenyl 0.351 86.8 37 1400.405
24F1419-07 Terphenyl-dl4 0.335 82.9 31 1400.405
8270 TPH Fractionation
24F1419-08 2-Fluorobiphenyl 0.320 95.8 37 1400.334
24F1419-08 Terphenyl-dl4 0.244 73.1 31 1400.334
8270 TPH Fractionation
24F1419-09 Terphenyl-dl4 0.298 88.1 31 1400.338
24F1419-09 2-Fluorobiphenyl 0.351 104 37 1400.338
8270 TPH Fractionation
24F1419-10 2-Fluorobiphenyl 0.282 84.9 37 1400.333
24F1419-10 Terphenyl-dl4 0.233 70.1 31 1400.333
8260 F&D Volatiles
24F1419-11 Toluene-d8 2.73 97.2 70 1302.81
24F1419-11 1,2-Dichloroethane-d4 2.82 101 70 1302.81
24F1419-11 4-Bromofluorobenzene 2.80 99.6 70 1302.81
8260 Low Level Volatiles
24F1419-13 Toluene-d8 10.0 100 63.2 12910.0
24F1419-13 1,2-Dichloroethane-d4 10.0 100 64.2 12610.0
24F1419-13 4-Bromofluorobenzene 9.85 98.5 71.4 12510.0
8260 TPH Fractionation
24F1419-14 1,2-Dichloroethane-d4 0.124 99.1 70 1300.125
24F1419-14 4-Bromofluorobenzene 0.125 99.9 70 1300.125
24F1419-14 Toluene-d8 0.126 101 70 1300.125
8270 TPH Fractionation
24F1419-14 Terphenyl-dl4 111 89.1 41 174125
24F1419-14 2-Fluorobiphenyl 99.1 79.3 16 152125
CtF WO#: 24F1419
www.ChemtechFord.com Page 47 of 47
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24J0550
Project: Former Sommers Auto Wrecking
10/29/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 17
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24J0550-01 MW-6
24J0550-02 MW-7
24J0550-03 MW-70
24J0550-04 Trip Blank
24J0550-05 Equipment Blank
______________________________________________________________________________________________
Work Order Report Narrative
Amended Report
GRO Fractionation analytes were added to samples 24J0550-02 and -03.
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24J0550
Page 2 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002H
10/7/24 12:07 @ 8.0 °C
10/29/2024
Former Sommers Auto Wrecking
Sample ID: MW-6
Lab ID: 24J0550-01Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 10/7/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 10/15/2410/15/241.0 EPA 8015 CNDDiesel Range Organics
MBTEXn
mg/L 10/11/2410/11/240.005 EPA 8260D/5030BNDBenzene
mg/L 10/11/2410/11/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L 10/11/2410/11/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 10/11/2410/11/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 10/11/2410/11/240.012 EPA 8260D/5030BNDToluene
mg/L 10/11/2410/11/240.038 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/L 10/11/2410/11/240.125 EPA 8260B/C 5030A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24J0550
www.ChemtechFord.com
Page 3 of 17Page 3 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002H
10/7/24 12:07 @ 8.0 °C
10/29/2024
Former Sommers Auto Wrecking
Sample ID: MW-7
Lab ID: 24J0550-02Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 10/7/24 11:40
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 10/15/2410/15/241.0 EPA 8015 C1.4Diesel Range Organics
MBTEXn
mg/L 10/11/2410/11/240.005 EPA 8260D/5030BNDBenzene
mg/L 10/11/2410/11/240.012 EPA 8260D/5030B0.055Ethylbenzene
mg/L 10/11/2410/11/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 10/11/2410/11/240.012 EPA 8260D/5030B0.048Naphthalene
mg/L 10/11/2410/11/240.012 EPA 8260D/5030BNDToluene
mg/L 10/11/2410/11/240.038 EPA 8260D/5030B0.190Xylenes, total
mg/L 10/11/2410/11/240.125 EPA 8260D/5030B0.142C5-C6 Aliphatic hydrocarbons
mg/L 10/11/2410/11/240.125 EPA 8260D/5030B0.139C7-C8 Aliphatic hydrocarbons
mg/L 10/11/2410/11/240.125 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/L 10/11/2410/11/240.125 EPA 8260D/5030B1.20C9-C10 Alkyl Benzenes
Gasoline Range
mg/L 10/11/2410/11/240.125 EPA 8260B/C 5030A/[CALC]1.78Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24J0550
www.ChemtechFord.com
Page 4 of 17Page 4 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002H
10/7/24 12:07 @ 8.0 °C
10/29/2024
Former Sommers Auto Wrecking
Sample ID: MW-70
Lab ID: 24J0550-03Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 10/7/24 11:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 10/15/2410/15/241.0 EPA 8015 C1.2Diesel Range Organics
MBTEXn
mg/L 10/11/2410/11/240.005 EPA 8260D/5030BNDBenzene
mg/L 10/11/2410/11/240.012 EPA 8260D/5030B0.055Ethylbenzene
mg/L 10/11/2410/11/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 10/11/2410/11/240.012 EPA 8260D/5030B0.041Naphthalene
mg/L 10/11/2410/11/240.012 EPA 8260D/5030BNDToluene
mg/L 10/11/2410/11/240.038 EPA 8260D/5030B0.168Xylenes, total
mg/L 10/11/2410/11/240.125 EPA 8260D/5030B0.131C5-C6 Aliphatic hydrocarbons
mg/L 10/11/2410/11/240.125 EPA 8260D/5030B0.147C7-C8 Aliphatic hydrocarbons
mg/L 10/11/2410/11/240.125 EPA 8260D/5030BNDC9-C10 Aliphatic hydrocarbons
mg/L 10/11/2410/11/240.125 EPA 8260D/5030B1.19C9-C10 Alkyl Benzenes
Gasoline Range
mg/L 10/11/2410/11/240.125 EPA 8260B/C 5030A/[CALC]1.73Gasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24J0550
www.ChemtechFord.com
Page 5 of 17Page 5 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002H
10/7/24 12:07 @ 8.0 °C
10/29/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24J0550-04Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 10/7/24 11:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L J-LOW-L10/11/2410/11/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 10/11/2410/11/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L J-LOW-C10/11/2410/11/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L 10/11/2410/11/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 10/11/2410/11/2420.0 EPA 8260D/5030BNDAcetone
ug/L 10/11/2410/11/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 10/11/2410/11/240.4 EPA 8260D/5030BNDBenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDBromodichloromethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDBromoform
ug/L J-LOW-L10/11/2410/11/242.0 EPA 8260D/5030BNDBromomethane
ug/L 10/11/2410/11/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24J0550
www.ChemtechFord.com
Page 6 of 17Page 6 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002H
10/7/24 12:07 @ 8.0 °C
10/29/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24J0550-04Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 10/7/24 11:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDChloroethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDChloroform
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDChloromethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L 10/11/2410/11/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDDibromochloromethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDDibromomethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 10/11/2410/11/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 10/11/2410/11/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 10/11/2410/11/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 10/11/2410/11/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L J-LOW-C10/11/2410/11/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDNaphthalene
ug/L J-LOW-L10/11/2410/11/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDStyrene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDToluene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 10/11/2410/11/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L J-LOW-L10/11/2410/11/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 10/11/2410/11/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 10/11/2410/11/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24J0550
www.ChemtechFord.com
Page 7 of 17Page 7 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002H
10/7/24 12:07 @ 8.0 °C
10/29/2024
Former Sommers Auto Wrecking
Sample ID: Equipment Blank
Lab ID: 24J0550-05Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 10/7/24 10:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 10/15/2410/15/241.0 EPA 8015 CNDDiesel Range Organics
MBTEXn
mg/L 10/11/2410/11/240.005 EPA 8260D/5030BNDBenzene
mg/L 10/11/2410/11/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L 10/11/2410/11/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 10/11/2410/11/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 10/11/2410/11/240.012 EPA 8260D/5030BNDToluene
mg/L 10/11/2410/11/240.038 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/L 10/11/2410/11/240.125 EPA 8260B/C 5030A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24J0550
www.ChemtechFord.com
Page 8 of 17Page 8 of 17
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002H
10/7/24 12:07 @ 8.0 °C
10/29/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-C = Estimated low due to low recovery of CCV
J-LOW-L = Estimated low due to low recovery of LCS
Project Name: Former Sommers Auto Wrecking CtF WO#: 24J0550
www.ChemtechFord.com
Page 9 of 17Page 9 of 17
Report GRO Fractionation on samples -02 and -03,per
Blake 10/29/24
Page 10 of 17
QC Report for Work Order (WO) - 24J0550
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYJ0714-BLK1 Batch: BYJ0714
Date Prepared: 10/15/2024 Date Analyzed: 10/15/2024
Diesel Range Organics ND 1.0 1.00
LCS - EPA 8015 C
QC Sample ID: BYJ0714-BS1 Batch: BYJ0714
Date Prepared: 10/15/2024 Date Analyzed: 10/15/2024
Diesel Range Organics 94.1 50 - 150 38 40.0 1.0 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYJ0714-MS1 QC Source Sample: 24J0550-01Batch: BYJ0714
Date Prepared: 10/15/2024 Date Analyzed: 10/15/2024
Diesel Range Organics 70.6 50 - 150 28 ND 40.0 1.0 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYJ0714-MSD1 QC Source Sample: 24J0550-01Batch: BYJ0714
Date Prepared: 10/15/2024 Date Analyzed: 10/15/2024
Diesel Range Organics 57.8 19.9 50 - 150 20 23 ND 40.0 1.0 1.00
CtF WO#: 24J0550
www.ChemtechFord.com Page 11 of 17
QC Report for Work Order (WO) - 24J0550
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYJ0617-BLK1 Batch: BYJ0617
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.4 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 1.0 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
CtF WO#: 24J0550
www.ChemtechFord.com Page 12 of 17
QC Report for Work Order (WO) - 24J0550
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYJ0617-BLK1 Batch: BYJ0617
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 1.0 1.00
n-Butyl Alcohol ND 50.0 1.00
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 1.0 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 3.0 1.00
QC Sample ID: BYJ0619-BLK1 Batch: BYJ0619
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYJ0617-BS1 Batch: BYJ0617
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
1,1,1,2-Tetrachloroethane 89.5 70 - 130 8.95 10.0 1.0 1.00
1,1,1-Trichloroethane 74.6 70 - 130 7.46 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 90.0 70 - 130 9.00 10.0 1.0 1.00
1,1,2-Trichloroethane 94.6 70 - 130 9.46 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 69.6 70 - 130 6.96 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
1,1-Dichloroethane 78.6 70 - 130 7.86 10.0 1.0 1.00
1,1-Dichloroethene 78.1 70 - 130 7.81 10.0 1.0 1.00
1,1-Dichloropropene 84.7 70 - 130 8.47 10.0 1.0 1.00
1,2,3-Trichlorobenzene 97.0 70 - 130 9.70 10.0 1.0 1.00
1,2,3-Trichloropropane 86.3 70 - 130 8.63 10.0 1.0 1.00
1,2,4-Trichlorobenzene 94.4 70 - 130 9.44 10.0 1.0 1.00
1,2,4-Trimethylbenzene 80.9 70 - 130 8.09 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 75.1 70 - 130 7.51 10.0 1.0 1.00
1,2-Dibromoethane (EDB)98.9 70 - 130 9.89 10.0 1.0 1.00
1,2-Dichlorobenzene 84.8 70 - 130 8.48 10.0 1.0 1.00
1,2-Dichloroethane 89.3 70 - 130 8.93 10.0 1.0 1.00
CtF WO#: 24J0550
www.ChemtechFord.com Page 13 of 17
QC Report for Work Order (WO) - 24J0550
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYJ0617-BS1 Batch: BYJ0617
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
1,2-Dichloropropane 98.5 70 - 130 9.85 10.0 1.0 1.00
1,3,5-Trimethylbenzene 82.5 70 - 130 8.25 10.0 1.0 1.00
1,3-Dichlorobenzene 88.0 70 - 130 8.80 10.0 1.0 1.00
1,3-Dichloropropane 99.1 70 - 130 9.91 10.0 1.0 1.00
1,4-Dichlorobenzene 90.0 70 - 130 9.00 10.0 1.0 1.00
2,2-Dichloropropane 28.5 70 - 130 2.85 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
2-Chlorotoluene 79.4 70 - 130 7.94 10.0 1.0 1.00
2-Hexanone 89.2 70 - 130 8.92 10.0 10.0 1.00
J - Detected but below the Reporting Limit; therefore, result is an estimated concentration (CLP J-Flag).
2-Nitropropane 75.7 70 - 130 22.7 30.0 2.0 1.00
4-Chlorotoluene 77.6 70 - 130 7.76 10.0 1.0 1.00
Acetone 93.4 70 - 130 93.4 100 20.0 1.00
Acrylonitrile 89.7 70 - 130 44.8 50.0 5.0 1.00
Benzene 100 70 - 130 10.0 10.0 0.4 1.00
Bromobenzene 85.5 70 - 130 8.55 10.0 1.0 1.00
Bromochloromethane 92.6 70 - 130 9.26 10.0 1.0 1.00
Bromodichloromethane 86.2 70 - 130 8.62 10.0 1.0 1.00
Bromoform 87.4 70 - 130 8.74 10.0 1.0 1.00
Bromomethane 50.3 70 - 130 5.03 10.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Carbon Disulfide 70.7 70 - 130 7.07 10.0 2.0 1.00
Carbon Tetrachloride 85.8 70 - 130 8.58 10.0 1.0 1.00
Chlorobenzene 90.6 70 - 130 9.06 10.0 1.0 1.00
Chloroethane 83.4 70 - 130 8.34 10.0 1.0 1.00
Chloroform 76.1 70 - 130 7.61 10.0 1.0 1.00
Chloromethane 76.7 70 - 130 7.67 10.0 1.0 1.00
cis-1,2-Dichloroethene 78.6 70 - 130 7.86 10.0 1.0 1.00
cis-1,3-Dichloropropene 95.4 70 - 130 9.54 10.0 1.0 1.00
Cyclohexanone 101 70 - 130 101 100 10.0 1.00
Dibromochloromethane 87.6 70 - 130 8.76 10.0 1.0 1.00
Dibromomethane 116 70 - 130 11.6 10.0 1.0 1.00
Dichlorodifluoromethane 76.4 70 - 130 7.64 10.0 1.0 1.00
Ethyl Acetate 89.5 70 - 130 17.9 20.0 2.0 1.00
Ethyl Ether 85.1 70 - 130 8.51 10.0 1.0 1.00
Ethylbenzene 80.6 70 - 130 8.06 10.0 1.0 1.00
Hexachlorobutadiene 92.1 70 - 130 9.21 10.0 1.0 1.00
Isobutanol 110 70 - 130 219 200 20.0 1.00
Isopropylbenzene 73.6 70 - 130 7.36 10.0 1.0 1.00
Methyl Ethyl Ketone 85.5 70 - 130 8.55 10.0 2.0 1.00
Methyl Isobutyl Ketone 80.4 70 - 130 8.04 10.0 5.0 1.00
Methylene Chloride 80.5 70 - 130 8.05 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)70 - 130 ND 10.0 0.6 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 83.2 70 - 130 8.32 10.0 1.0 1.00
n-Butyl Alcohol 68.6 70 - 130 68.6 100 50.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
n-Butylbenzene 71.1 70 - 130 7.11 10.0 1.0 1.00
n-Propyl Benzene 75.6 70 - 130 7.56 10.0 1.0 1.00
Pentachloroethane 70.2 70 - 130 7.02 10.0 1.0 1.00
p-Isopropyltoluene 73.0 70 - 130 7.30 10.0 1.0 1.00
CtF WO#: 24J0550
www.ChemtechFord.com Page 14 of 17
QC Report for Work Order (WO) - 24J0550
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYJ0617-BS1 Batch: BYJ0617
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
sec-Butyl Benzene 72.1 70 - 130 7.21 10.0 1.0 1.00
Styrene 91.3 70 - 130 9.13 10.0 1.0 1.00
tert-Butylbenzene 76.9 70 - 130 7.69 10.0 1.0 1.00
Tetrachloroethene 81.6 70 - 130 8.16 10.0 1.0 1.00
Toluene 87.5 70 - 130 8.75 10.0 1.0 1.00
trans-1,2-Dichloroethene 80.3 70 - 130 8.03 10.0 1.0 1.00
trans-1,3-Dichloropropene 85.8 70 - 130 8.58 10.0 1.0 1.00
Trichloroethene 89.5 70 - 130 8.95 10.0 1.0 1.00
Trichlorofluoromethane 60.9 70 - 130 6.09 10.0 1.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Vinyl Chloride 72.7 70 - 130 7.27 10.0 0.8 1.00
Xylenes, total 87.6 70 - 130 26.3 30.0 3.0 1.00
QC Sample ID: BYJ0619-BS1 Batch: BYJ0619
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
Benzene 87.5 70 - 130 0.009 0.0100 0.0004 1.00
Ethylbenzene 81.4 70 - 130 0.008 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)70.1 70 - 130 0.007 0.0100 0.0006 1.00
Naphthalene 74.3 70 - 130 0.007 0.0100 0.001 1.00
Toluene 83.4 70 - 130 0.008 0.0100 0.001 1.00
Xylenes, total 81.9 70 - 130 0.025 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYJ0619-MS2 QC Source Sample: 24J0550-01Batch: BYJ0619
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
Benzene 131 70 - 130 0.164 ND 0.125 0.005 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Ethylbenzene 122 70 - 130 0.152 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)111 70 - 130 0.139 ND 0.125 0.008 1.00
Naphthalene 95.2 70 - 130 0.119 ND 0.125 0.012 1.00
Toluene 129 70 - 130 0.162 ND 0.125 0.012 1.00
Xylenes, total 120 70 - 130 0.450 ND 0.375 0.038 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYJ0619-MSD2 QC Source Sample: 24J0550-01Batch: BYJ0619
Date Prepared: 10/11/2024 Date Analyzed: 10/11/2024
Benzene 134 1.89 70 - 130 20 0.167 ND 0.125 0.005 1.00
QM-RPD - The recovery was outside acceptance limits for the MS and/or MSD. The RPD between the MS and MSD was
acceptable and indicates the recovery is due to matrix interference. The batch was accepted based on the acceptable
recovery of the LCS and the RPD.
Ethylbenzene 128 4.49 70 - 130 25 0.160 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)100 9.93 70 - 130 25 0.126 ND 0.125 0.008 1.00
Naphthalene 97.2 2.08 70 - 130 25 0.122 ND 0.125 0.012 1.00
Toluene 122 5.56 70 - 130 20 0.153 ND 0.125 0.012 1.00
Xylenes, total 121 0.857 70 - 130 20 0.454 ND 0.375 0.038 1.00
CtF WO#: 24J0550
www.ChemtechFord.com Page 15 of 17
Surrogates Report for Work Order (WO) - 24J0550
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYJ0714-BLK1 Bromofluorobenzene 65.3 50 BYJ0714 1.001502.61 4.00
BYJ0714-BLK1 Capric Acid 0 BYJ0714 1.0010.00 10.0
LCS - EPA 8015 C
BYJ0714-BS1 Bromofluorobenzene 88.9 50 BYJ0714 1.001503.55 4.00
BYJ0714-BS1 Capric Acid 0 BYJ0714 1.0010.00 10.0
Matrix Spike - EPA 8015 C
BYJ0714-MS2 Bromofluorobenzene 83.0 50 BYJ0714 1.001503.32 4.00
BYJ0714-MS1 Bromofluorobenzene 77.3 50 BYJ0714 1.001503.09 4.00
BYJ0714-MS2 Capric Acid 0 BYJ0714 1.0010.00 10.0
BYJ0714-MS1 Capric Acid 0 BYJ0714 1.0010.00 10.0
Matrix Spike Dup - EPA 8015 C
BYJ0714-MSD2 Bromofluorobenzene 75.7 50 BYJ0714 1.001503.03 4.00
BYJ0714-MSD1 Bromofluorobenzene 70.6 50 BYJ0714 1.001502.83 4.00
BYJ0714-MSD2 Capric Acid 0 BYJ0714 1.0010.00 10.0
BYJ0714-MSD1 Capric Acid 0 BYJ0714 1.0010.00 10.0
Blank - EPA 8260D
BYJ0617-BLK1 1,2-Dichloroethane-d4 98.3 64.2 BYJ0617 1.001269.83 10.0
BYJ0617-BLK1 4-Bromofluorobenzene 92.0 71.4 BYJ0617 1.001259.20 10.0
BYJ0617-BLK1 Toluene-d8 102 63.2 BYJ0617 1.0012910.2 10.0
BYJ0619-BLK1 Toluene-d8 103 83.3 BYJ0619 1.001220.0103 0.0100
LCS - EPA 8260D
BYJ0617-BS1 1,2-Dichloroethane-d4 93.6 64.2 BYJ0617 1.001269.36 10.0
BYJ0617-BS1 4-Bromofluorobenzene 94.8 71.4 BYJ0617 1.001259.48 10.0
BYJ0617-BS1 Toluene-d8 104 63.2 BYJ0617 1.0012910.4 10.0
BYJ0619-BS1 Toluene-d8 99.4 83.3 BYJ0619 1.001220.00994 0.0100
Matrix Spike - EPA 8260D
BYJ0617-MS1 1,2-Dichloroethane-d4 95.5 64.2 BYJ0617 1.001262390 2500
BYJ0617-MS1 4-Bromofluorobenzene 93.7 71.4 BYJ0617 1.001252340 2500
BYJ0617-MS1 Toluene-d8 103 63.2 BYJ0617 1.001292580 2500
BYJ0619-MS2 Toluene-d8 101 83.3 BYJ0619 1.001220.126 0.125
BYJ0619-MS1 Toluene-d8 107 83.3 BYJ0619 1.0012226.8 25.0
Matrix Spike Dup - EPA 8260D
BYJ0617-MSD1 1,2-Dichloroethane-d4 97.1 64.2 BYJ0617 1.001262430 2500
BYJ0617-MSD1 4-Bromofluorobenzene 93.7 71.4 BYJ0617 1.001252340 2500
BYJ0617-MSD1 Toluene-d8 103 63.2 BYJ0617 1.001292580 2500
BYJ0619-MSD2 Toluene-d8 103 83.3 BYJ0619 1.001220.129 0.125
BYJ0619-MSD1 Toluene-d8 101 83.3 BYJ0619 1.0012225.4 25.0
CtF WO#: 24J0550
www.ChemtechFord.com Page 16 of 17
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24J0550-01 Capric Acid 0.00 0 110.0
24J0550-01 Bromofluorobenzene 3.17 79.2 50 1504.00
MBTEXN-GRO
24J0550-01 Toluene-d8 0.116 92.7 83.3 1220.125
DRO with silica gel cleanup
24J0550-02 Capric Acid 0.00 0 110.0
24J0550-02 Bromofluorobenzene 2.79 69.8 50 1504.00
MBTEXN-GRO
24J0550-02 Toluene-d8 0.128 102 83.3 1220.125
DRO with silica gel cleanup
24J0550-03 Capric Acid 0.00 0 110.0
24J0550-03 Bromofluorobenzene 2.92 73.0 50 1504.00
MBTEXN-GRO
24J0550-03 Toluene-d8 0.124 99.5 83.3 1220.125
8260 Low Level Volatiles
24J0550-04 Toluene-d8 10.4 104 63.2 12910.0
24J0550-04 4-Bromofluorobenzene 9.25 92.5 71.4 12510.0
24J0550-04 1,2-Dichloroethane-d4 10.0 100 64.2 12610.0
DRO with silica gel cleanup
24J0550-05 Capric Acid 0.00 0 110.0
24J0550-05 Bromofluorobenzene 2.63 65.7 50 1504.00
MBTEXN-GRO
24J0550-05 Toluene-d8 0.127 102 83.3 1220.125
CtF WO#: 24J0550
www.ChemtechFord.com Page 17 of 17
ANALYTICAL REPORT
October 28, 2024
Wasatch Environmental
Sample Delivery Group:L1766673
Samples Received:08/13/2024
Project Number:SOMMERS AUTO
Description:Emergency Response and Remediation Split Samples
Report To:Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Entire Report Reviewed By:
October 28, 2024
[Preliminary Report]
John Hawkins
Project Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be
reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace
Analytical National is performed per guidance provided in laboratory standard operating procedures ENV-SOP-MTJL-0067 and
ENV-SOP-MTJL-0068. Where sampling conducted by the customer, results relate to the accuracy of the information provided,
and as the samples are received.
Pace Analytical National
12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 mydata.pacelabs.com
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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October 28, 2024
John Hawkins
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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TABLE OF CONTENTSTABLE OF CONTENTSTABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 5
Cn: Case Narrative 6
Su: Summary Results 7
2540 G-2011 Total Solids 7
Sample Result Inorganic Analysis Data Sheet 8
L1766673-01 08/14/24 09:50 LOGBAL1 8
L1766673-02 08/14/24 10:04 LOGBAL1 9
BLANK(R4107009-1) WG2342384 08/14/24 09:50 LOGBAL1 10
BLANK(R4107010-1) WG2342385 08/14/24 10:04 LOGBAL1 11
LCS(R4107009-2) WG2342384 08/14/24 09:50 LOGBAL1 12
LCS(R4107010-2) WG2342385 08/14/24 10:04 LOGBAL1 13
DUP(R4107009-3) WG2342384 08/14/24 09:50 LOGBAL1 14
DUP(R4107010-3) WG2342385 08/14/24 10:04 LOGBAL1 15
Blank 16
LOGBAL1 WG2342384 16
LOGBAL1 WG2342385 17
Laboratory Duplicate 18
WG2342384 DUP(R4107009-3) 18
WG2342385 DUP(R4107010-3) 19
Laboratory Control Sample / Duplicate 20
WG2342384 LCS(R4107009-2) 20
WG2342385 LCS(R4107010-2) 21
Detection Limit Summary 22
2540 G-2011 - Solid 22
Analysis Log 23
LOGBAL1 WG2342384 23
LOGBAL1 WG2342385 24
8260B Volatile Organic Compounds (GC/MS) 25
Surrogate Recovery 26
Solid Surrogate Summary 26
Laboratory Control Sample / Duplicate 27
WG2345308 LCS(R4108548-1) LCSD(R4108548-2) 27
WG2345308 LCS(R4108548-3) 28
WG2345938 LCS(R4109766-1) 29
WG2345938 LCS(R4109766-4) 30
Method Blank 31
WG2345938 R4109766-3 VOCMS28 08/20/24 12:48 31
WG2345308 R4108548-4 VOCMS52 08/18/24 13:09 32
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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GC/MS Performance Check 33
VOCMS28 080724B 08/07/24 23:20 33
VOCMS28 081524 08/15/24 09:55 34
VOCMS28 082024 08/20/24 08:32 35
VOCMS52 081524 08/15/24 22:50 36
VOCMS52 081524 08/16/24 10:31 37
VOCMS52 081824 08/18/24 10:29 38
Internal Standard & Retention Time 39
VOCMS28 08/20/24 09:17 39
VOCMS52 08/18/24 11:09 40
Sample Result Summary Organic Analysis Data Sheet 41
L1766673-01 08/18/24 21:50 VOCMS52 41
L1766673-02 08/20/24 16:09 VOCMS28 42
GC/MS Initial Calibration 43
VOCMS28 08/08/24 00:50 43
VOCMS52 08/16/24 00:11 44
GC/MS Calibration Verification 46
VOCMS28 08/08/24 04:56 46
VOCMS28 08/11/24 23:16 47
VOCMS28 08/20/24 09:17 48
VOCMS28 08/20/24 11:18 49
VOCMS52 08/16/24 03:52 50
VOCMS52 08/16/24 18:12 51
VOCMS52 08/18/24 11:09 52
VOCMS52 08/18/24 12:09 53
Analytical Sequence 54
VOCMS28 08/08/24 00:50 54
VOCMS52 08/16/24 00:11 55
Detection Limit Summary 57
8260B - Solid 57
QC Result Summary Organic Analysis Data Sheet 58
BLANK(R4108548-4) WG2345308 08/18/24 13:09 VOCMS52 58
BLANK(R4109766-3) WG2345938 08/20/24 12:48 VOCMS28 59
LCS(R4108548-1) WG2345308 08/18/24 11:29 VOCMS52 60
LCS(R4108548-3) WG2345308 08/18/24 12:29 VOCMS52 61
LCS(R4109766-1) WG2345938 08/20/24 09:39 VOCMS28 62
LCS(R4109766-4) WG2345938 08/20/24 13:10 VOCMS28 63
LCSD(R4108548-2) WG2345308 08/18/24 11:49 VOCMS52 64
Gl: Glossary of Terms 65
Al: Accreditations & Locations 66
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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Sc: Sample Chain of Custody 67 1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
EXC-4 L1766673-01 Solid Jacob Scott 08/12/24 12:24 08/13/24 12:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2342384 1 08/14/24 09:34 08/14/24 09:50 KDW Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B WG2345308 1 08/12/24 12:24 08/18/24 21:50 ACG Mt. Juliet, TN
Collected by Collected date/time Received date/time
EXC- L1766673-02 Solid Jacob Scott 08/12/24 12:30 08/13/24 12:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2342385 1 08/14/24 09:52 08/14/24 10:04 KDW Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B WG2345938 25 08/12/24 12:30 08/20/24 16:09 ADM Mt. Juliet, TN
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the
appropriate preservatives, and within method specified holding times, unless qualified or notated within
the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples
have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control
are within established criteria except where addressed in this case narrative, a non-conformance form
or properly qualified within the sample results. By my digital signature below, I affirm to the best of my
knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the
quality of the data have been identified by the laboratory, and no information or data have been
knowingly withheld that would affect the quality of the data.
[Preliminary Report]
John Hawkins
Project Manager
Report Revision History
Level II Report - Version 1: 08/22/24 08:32
Project Narrative
Reprint for QC 3 and EDD
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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John Hawkins
Project Manager
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2540 G-2011 Total Solids
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET EXC-4
Lab Sample ID:L1766673-01 SDG:L1766673
Client Sample ID:EXC-4 Collected Date/Time:08/12/24 12:24
Lab File ID:13 Received Date/Time:08/13/24 12:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/14/24 09:34
Analytical Batch:WG2342384 Analysis Date/Time:08/14/24 09:50
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:10.566 g
Total Solids (%):80.0 Final Wt/Vol:8.712 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 80.0
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET EXC-
Lab Sample ID:L1766673-02 SDG:L1766673
Client Sample ID:EXC-Collected Date/Time:08/12/24 12:30
Lab File ID:04 Received Date/Time:08/13/24 12:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/14/24 09:52
Analytical Batch:WG2342385 Analysis Date/Time:08/14/24 10:04
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:11.845 g
Total Solids (%):79.3 Final Wt/Vol:9.658 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 79.3
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4107009-1
Lab Sample ID:R4107009-1 SDG:L1766673
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:01 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/14/24 09:32
Analytical Batch:WG2342384 Analysis Date/Time:08/14/24 09:50
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:1.288 g
Total Solids (%):_______________Final Wt/Vol:1.288 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 0.000
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4107010-1
Lab Sample ID:R4107010-1 SDG:L1766673
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:01 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/14/24 09:51
Analytical Batch:WG2342385 Analysis Date/Time:08/14/24 10:04
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:1.283 g
Total Solids (%):_______________Final Wt/Vol:1.282 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 0.00100
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4107009-2
Lab Sample ID:R4107009-2 SDG:L1766673
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:03 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/14/24 09:32
Analytical Batch:WG2342384 Analysis Date/Time:08/14/24 09:50
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:11.298 g
Total Solids (%):_______________Final Wt/Vol:6.297 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 50.0
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4107010-2
Lab Sample ID:R4107010-2 SDG:L1766673
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:03 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/14/24 09:51
Analytical Batch:WG2342385 Analysis Date/Time:08/14/24 10:04
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:11.269 g
Total Solids (%):_______________Final Wt/Vol:6.267 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 50.0
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4107009-3
Lab Sample ID:R4107009-3 SDG:L1766673
Client Sample ID:DUP Collected Date/Time:08/12/24 10:40
Lab File ID:02 Received Date/Time:08/13/24 12:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/14/24 09:32
Analytical Batch:WG2342384 Analysis Date/Time:08/14/24 09:50
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:9.613 g
Total Solids (%):90.5 Final Wt/Vol:8.833 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 90.7
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4107010-3
Lab Sample ID:R4107010-3 SDG:L1766673
Client Sample ID:DUP Collected Date/Time:08/05/24 16:39
Lab File ID:02 Received Date/Time:08/13/24 09:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/14/24 09:52
Analytical Batch:WG2342385 Analysis Date/Time:08/14/24 10:04
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:6.401 g
Total Solids (%):88.9 Final Wt/Vol:5.847 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 89.2
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1766673 Calibration (begin) date/time:_______________
Instrument ID:LOGBAL1 Calibration (end) date/time:_______________
Analytical Method:2540 G-2011 Analytical Run:WG2342384
Sample ID:BLANK Result BLANK
Qual
File ID:01
Analyte %
TOTAL SOLIDS 0.000
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1766673 Calibration (begin) date/time:_______________
Instrument ID:LOGBAL1 Calibration (end) date/time:_______________
Analytical Method:2540 G-2011 Analytical Run:WG2342385
Sample ID:BLANK Result BLANK
Qual
File ID:01
Analyte %
TOTAL SOLIDS 0.00100
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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6-IN DUPLICATES SAMPLE NO.:
L1766673-01 R4107009-3
DUP Sample / File ID:R4107009-3 / 02 SDG:L1766673
OS Sample / File ID:L1766669-01 / 10 Analytical Batch:WG2342384
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte OS
Result
DUP
Result RPD RPD
Limits
%%%%
Total Solids 90.5 90.7 0.166 10
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
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6-IN DUPLICATES SAMPLE NO.:
L1766673-02 R4107010-3
DUP Sample / File ID:R4107010-3 / 02 SDG:L1766673
OS Sample / File ID:L1766684-01 / 05 Analytical Batch:WG2342385
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte OS
Result
DUP
Result RPD RPD
Limits
%%%%
Total Solids 88.9 89.2 0.266 10
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7-IN LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4107009-2
RECOVERY _______________
L1766673-01
LCS Sample / File ID:R4107009-2 / 03 SDG:L1766673
LCSD Sample / File ID:_______________Analytical Batch:WG2342384
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD
Rec.Rec. Limits RPD RPD Limits
%%%%%%%
Total Solids 50.0 50.0 100 90.0 - 110
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
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7-IN LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4107010-2
RECOVERY _______________
L1766673-02
LCS Sample / File ID:R4107010-2 / 03 SDG:L1766673
LCSD Sample / File ID:_______________Analytical Batch:WG2342385
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD
Rec.Rec. Limits RPD RPD Limits
%%%%%%%
Total Solids 50.0 50.0 100 90.0 - 110
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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9-IN DETECTION LIMIT SUMMARY
Lab Sample IDs:L1766673-01,02 Analytical Method:2540 G-2011
Matrix:Solid Prep Method:SM 2540 G
Analyte CAS Wavelength Mass MDL RDL
%%
Total Solids TSOLIDS
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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12-IN ANALYSIS LOG
SDG:L1766673 Analytical Method:2540 G-2011
Instrument ID:LOGBAL1 Calibration Start Date:_______________
Analytical Run:WG2342384 Calibration End Date:_______________
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
BLANK R4107009-1 01 08/14/24 09:50 1 WG2342384
DUP R4107009-3 02 08/14/24 09:50 1 WG2342384
LCS R4107009-2 03 08/14/24 09:50 1 WG2342384
OS L1766669-01 10 08/14/24 09:50
EXC-4 L1766673-01 13 08/14/24 09:50 1 WG2342384
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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12-IN ANALYSIS LOG
SDG:L1766673 Analytical Method:2540 G-2011
Instrument ID:LOGBAL1 Calibration Start Date:_______________
Analytical Run:WG2342385 Calibration End Date:_______________
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
BLANK R4107010-1 01 08/14/24 10:04 1 WG2342385
DUP R4107010-3 02 08/14/24 10:04 1 WG2342385
LCS R4107010-2 03 08/14/24 10:04 1 WG2342385
OS L1766684-01 05 08/14/24 10:04
EXC-L1766673-02 04 08/14/24 10:04 1 WG2342385
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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8260B Volatile Organic Compounds (GC/MS)
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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2A-OR SURROGATE RECOVERY
Analytical Method:8260B SDG:L1766673
Matrix:Solid
Sample ID Lab Sample ID Instrument File ID DMC-1 DMC-2 DMC-3 TOT Out
% Rec.% Rec.% Rec.
EXC-4 L1766673-01 VOCMS52 0818_30 103 94.8 115 0
EXC-L1766673-02 VOCMS28 0820_22 97.5 105 105 0
BLANK R4109766-3 VOCMS28 0820_13u 103 95.9 108 0
BLANK R4108548-4 VOCMS52 0818_09 107 98.6 99.0 0
LCS R4109766-1 VOCMS28 0820_05C 116 111 116 0
LCS R4109766-4 VOCMS28 0820_14 159* 117 110 1
LCS R4108548-1 VOCMS52 0818_04 105 96.7 112 0
LCS R4108548-3 VOCMS52 0818_07 105 102 102 0
LCSD R4108548-2 VOCMS52 0818_05 104 99.6 110 0
Parm Abbreviation Parameter QC LIMITS
DMC-1 Toluene-d8 75.0 - 131
DMC-2 4-Bromofluorobenzene 67.0 - 138
DMC-3 1,2-Dichloroethane-d4 70.0 - 130
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
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3B-OR LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4108548-1
RECOVERY R4108548-2
L1766673-01
LCS Sample / File ID:R4108548-1 / 0818_04 SDG:L1766673
LCSD Sample / File ID:R4108548-2 / 0818_05 Analytical Batch:WG2345308
Instrument ID:VOCMS52 Dilution Factor:1
Analytical Method:8260B Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD Rec.Rec. Limits RPD RPD
Limit
mg/kg mg/kg mg/kg %%%%%
Benzene 0.0250 0.0256 0.0238 102 95.2 70.0 - 123 7.29 20
Ethylbenzene 0.0250 0.0254 0.0244 102 97.6 74.0 - 126 4.02 20
Methyl tert-butyl ether 0.0250 0.0255 0.0237 102 94.8 66.0 - 132 7.32 20
Naphthalene 0.0250 0.0290 0.0242 116 96.8 59.0 - 130 18.0 20
Toluene 0.0250 0.0252 0.0235 101 94.0 75.0 - 121 6.98 20
Xylenes, Total 0.0750 0.0786 0.0735 105 98.0 72.0 - 127 6.71 20
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3B-OR LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4108548-3
RECOVERY _______________
L1766673-01
LCS Sample / File ID:R4108548-3 / 0818_07 SDG:L1766673
LCSD Sample / File ID:_______________Analytical Batch:WG2345308
Instrument ID:VOCMS52 Dilution Factor:1
Analytical Method:8260B Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD Rec.Rec. Limits RPD RPD
Limit
mg/kg mg/kg %%%%%
TPH (GC/MS) Low Fraction 5.00 5.34 107 52.0 - 154
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3B-OR LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4109766-1
RECOVERY _______________
L1766673-02
LCS Sample / File ID:R4109766-1 / 0820_05C SDG:L1766673
LCSD Sample / File ID:_______________Analytical Batch:WG2345938
Instrument ID:VOCMS28 Dilution Factor:1
Analytical Method:8260B Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD Rec.Rec. Limits RPD RPD
Limit
mg/kg mg/kg %%%%%
Benzene 0.0250 0.0278 111 70.0 - 123
Ethylbenzene 0.0250 0.0248 99.2 74.0 - 126
Methyl tert-butyl ether 0.0250 0.0209 83.6 66.0 - 132
Naphthalene 0.0250 0.0226 90.4 59.0 - 130
Toluene 0.0250 0.0304 122*75.0 - 121
Xylenes, Total 0.0750 0.0669 89.2 72.0 - 127
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3B-OR LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4109766-4
RECOVERY _______________
L1766673-02
LCS Sample / File ID:R4109766-4 / 0820_14 SDG:L1766673
LCSD Sample / File ID:_______________Analytical Batch:WG2345938
Instrument ID:VOCMS28 Dilution Factor:1
Analytical Method:8260B Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD Rec.Rec. Limits RPD RPD
Limit
mg/kg mg/kg %%%%%
TPH (GC/MS) Low Fraction 5.00 4.65 93.0 52.0 - 154
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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4A-OR METHOD BLANK SAMPLE NO.:
R4109766-3
Lab Sample ID:R4109766-3 SDG:L1766673
Lab File ID:0820_13u Preparation Date/Time:08/20/24 12:48
Instrument ID:VOCMS28 Analysis Date/Time:08/20/24 12:48
Analytical Batch:WG2345938 Dilution Factor:25
Analytical Method:8260B Matrix:Solid
Sample ID Lab Sample ID Instrument File ID Analysis
date/time
LCS R4109766-1 VOCMS28 0820_05C 08/20/24 09:39
LCS R4109766-4 VOCMS28 0820_14 08/20/24 13:10
EXC-L1766673-02 VOCMS28 0820_22 08/20/24 16:09
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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4A-OR METHOD BLANK SAMPLE NO.:
R4108548-4
Lab Sample ID:R4108548-4 SDG:L1766673
Lab File ID:0818_09 Preparation Date/Time:08/18/24 13:09
Instrument ID:VOCMS52 Analysis Date/Time:08/18/24 13:09
Analytical Batch:WG2345308 Dilution Factor:1
Analytical Method:8260B Matrix:Solid
Sample ID Lab Sample ID Instrument File ID Analysis
date/time
LCS R4108548-1 VOCMS52 0818_04 08/18/24 11:29
LCSD R4108548-2 VOCMS52 0818_05 08/18/24 11:49
LCS R4108548-3 VOCMS52 0818_07 08/18/24 12:29
EXC-4 L1766673-01 VOCMS52 0818_30 08/18/24 21:50
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5A-OR GC/MS INSTRUMENT
PERFORMANCE CHECK
Lab File ID: 0807B_01 SDG:L1766673
Instrument ID:VOCMS28 Analytical Method:8260B
Analysis Date/Time:08/07/24 23:20
Target Mass (m/e)Relative Mass Low Limit High Limit % Relative Abundance
95 174 50 200 113
96 95 5 9 7
173 174 0 2 0
174 95 50 200 89
175 174 5 9 8
176 174 95 105 102
177 176 5 10 7
Sample ID Lab Sample ID File ID Analysis date/time
STD-0.5 0.5 0807B_05 08/08/24 00:50
STD-1 1 0807B_06 08/08/24 01:12
STD-2 2 0807B_07 08/08/24 01:35
STD-5.0 5.0 0807B_08 08/08/24 01:57
STD-25 25 0807B_09 08/08/24 02:19
STD-100 100 0807B_11 08/08/24 03:04
STD-200 200 0807B_12 08/08/24 03:26
SSCV VOCMS28080724B0807B_16746224 0807B_16 08/08/24 04:56
SSCV VOCMS28080724B0807B_18746224 0807B_18 08/08/24 05:40
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5A-OR GC/MS INSTRUMENT
PERFORMANCE CHECK
Lab File ID: 0815_01 SDG:L1766673
Instrument ID:VOCMS28 Analytical Method:8260B
Analysis Date/Time:08/15/24 09:55
Target Mass (m/e)Relative Mass Low Limit High Limit % Relative Abundance
95 174 50 200 114
96 95 5 9 6
173 174 0 2 0
174 95 50 200 88
175 174 5 9 8
176 174 95 105 101
177 176 5 10 7
Sample ID Lab Sample ID File ID Analysis date/time
STD-0.5A 0.5A 0815_04 08/15/24 11:02
STD-1A 1A 0815_05 08/15/24 11:25
STD-5A 5A 0815_06 08/15/24 11:47
STD-10A 10A 0815_07 08/15/24 12:09
STD-15A 15A 0815_08 08/15/24 12:32
STD-20A 20A 0815_09 08/15/24 12:54
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5A-OR GC/MS INSTRUMENT
PERFORMANCE CHECK
Lab File ID: 0820_02T SDG:L1766673
Instrument ID:VOCMS28 Analytical Method:8260B
Analysis Date/Time:08/20/24 08:32
Target Mass (m/e)Relative Mass Low Limit High Limit % Relative Abundance
95 174 50 200 117
96 95 5 9 7
173 174 0 2 1
174 95 50 200 85
175 174 5 9 8
176 174 95 105 102
177 176 5 10 6
Sample ID Lab Sample ID File ID Analysis date/time
ICV VOCMS280820240820_04746224 0820_04 08/20/24 09:17
LCS R4109766-1 0820_05C 08/20/24 09:39
ICV VOCMS280820240820_09746224 0820_09 08/20/24 11:18
BLANK R4109766-3 0820_13u 08/20/24 12:48
LCS R4109766-4 0820_14 08/20/24 13:10
EXC-L1766673-02 0820_22 08/20/24 16:09
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5A-OR GC/MS INSTRUMENT
PERFORMANCE CHECK
Lab File ID: 0815_06 SDG:L1766673
Instrument ID:VOCMS52 Analytical Method:8260B
Analysis Date/Time:08/15/24 22:50
Target Mass (m/e)Relative Mass Low Limit High Limit % Relative Abundance
95 174 50 200 122
96 95 5 9 6
173 174 0 2 0
174 95 50 200 82
175 174 5 9 8
176 174 95 105 96
177 176 5 10 7
Sample ID Lab Sample ID File ID Analysis date/time
STD-0.5 0.5 0815_10 08/16/24 00:11
STD-1 1 0815_11 08/16/24 00:31
STD-2 2 0815_12 08/16/24 00:51
STD-5.0 5.0 0815_13 08/16/24 01:11
STD-25 25 0815_14 08/16/24 01:31
STD-75 75 0815_15 08/16/24 01:51
STD-100 100 0815_16 08/16/24 02:11
STD-200 200 0815_17 08/16/24 02:31
SSCV VOCMS520815240815_21746527 0815_21 08/16/24 03:52
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5A-OR GC/MS INSTRUMENT
PERFORMANCE CHECK
Lab File ID: 0815_25 SDG:L1766673
Instrument ID:VOCMS52 Analytical Method:8260B
Analysis Date/Time:08/16/24 10:31
Target Mass (m/e)Relative Mass Low Limit High Limit % Relative Abundance
95 174 50 200 122
96 95 5 9 7
173 174 0 2 1
174 95 50 200 82
175 174 5 9 7
176 174 95 105 98
177 176 5 10 6
Sample ID Lab Sample ID File ID Analysis date/time
SSCV VOCMS520815240815_25746527 0815_25 08/16/24 10:31
STD-0.5A 0.5A 0815_28 08/16/24 11:40
STD-1A 1A 0815_29 08/16/24 12:00
STD-5A 5A 0815_30 08/16/24 12:20
STD-10A 10A 0815_31 08/16/24 12:40
STD-15A 15A 0815_32 08/16/24 13:00
STD-20A 20A 0815_33 08/16/24 13:20
STD-0.5 0.5 0815_39 08/16/24 15:30
STD-1 1 0815_40 08/16/24 15:51
STD-2 2 0815_41 08/16/24 16:11
STD-5.0 5.0 0815_42 08/16/24 16:31
STD-10 10 0815_43 08/16/24 16:51
STD-20 20 0815_44 08/16/24 17:11
SSCV VOCMS520815240815_47746527 0815_47 08/16/24 18:12
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5A-OR GC/MS INSTRUMENT
PERFORMANCE CHECK
Lab File ID: 0818_01T SDG:L1766673
Instrument ID:VOCMS52 Analytical Method:8260B
Analysis Date/Time:08/18/24 10:29
Target Mass (m/e)Relative Mass Low Limit High Limit % Relative Abundance
95 174 50 200 118
96 95 5 9 7
173 174 0 2 1
174 95 50 200 84
175 174 5 9 8
176 174 95 105 96
177 176 5 10 6
Sample ID Lab Sample ID File ID Analysis date/time
ICV VOCMS520818240818_03746527 0818_03 08/18/24 11:09
LCS R4108548-1 0818_04 08/18/24 11:29
LCSD R4108548-2 0818_05 08/18/24 11:49
ICV VOCMS520818240818_06746527 0818_06 08/18/24 12:09
LCS R4108548-3 0818_07 08/18/24 12:29
BLANK R4108548-4 0818_09 08/18/24 13:09
EXC-4 L1766673-01 0818_30 08/18/24 21:50
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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8A-OR INTERNAL STANDARD
AND RETENTION TIME
SDG:L1766673 Analytical Method:8260B
Instrument ID:VOCMS28 Calibration Start Date:08/08/24 00:50
Std File: 0820_04 Calibration End Date:08/15/24 12:54
Std Analysis Date:08/20/24 09:17
Sample ID File ID 1,4-DCB 8260-CB 8260-FB
Response RT Response RT Response RT
STANDARD 94027 7.95 100836 6.26 215713 4.34
UPPER LIMIT 188054 201672 431426
LOWER LIMIT 47014 50418 107857
LCS R4109766-1
WG2345938 1x 0820_05C 90323 7.95 83244 6.26 210349 4.34
BLANK R4109766-3
WG2345938 25x 0820_13u 69703 7.95 82349 6.26 187611 4.32
LCS R4109766-4
WG2345938 1x 0820_14 48198 7.95 52272 6.26 180611 4.34
L1766673-02 WG2345938
25x 0820_22 95608 7.95 98003 6.26 209822 4.32
1,4-DCB - 8260-1,4-DICHLOROBENZENE-D4 8260-CB - 8260-CHLOROBENZENE-D5
8260-FB - 8260-FLUOROBENZENE
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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8A-OR INTERNAL STANDARD
AND RETENTION TIME
SDG:L1766673 Analytical Method:8260B
Instrument ID:VOCMS52 Calibration Start Date:08/16/24 00:11
Std File: 0818_03 Calibration End Date:08/16/24 17:11
Std Analysis Date:08/18/24 11:09
Sample ID File ID 1,4-DCB 8260-CB 8260-FB
Response RT Response RT Response RT
STANDARD 54957 8.02 67757 6.32 184571 4.38
UPPER LIMIT 109914 135514 369142
LOWER LIMIT 27479 33879 92286
LCS R4108548-1
WG2345308 1x 0818_04 50751 8.02 63793 6.32 175015 4.38
LCSD R4108548-2
WG2345308 1x 0818_05 61127 8.02 71720 6.32 196003 4.38
LCS R4108548-3
WG2345308 1x 0818_07 57931 8.02 74955 6.32 209661 4.38
BLANK R4108548-4
WG2345308 1x 0818_09 51215 8.02 68807 6.32 197105 4.38
L1766673-01 WG2345308
1x 0818_30 51597 8.02 71851 6.32 189239 4.37
1,4-DCB - 8260-1,4-DICHLOROBENZENE-D4 8260-CB - 8260-CHLOROBENZENE-D5
8260-FB - 8260-FLUOROBENZENE
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET EXC-4
Lab Sample ID:L1766673-01 SDG:L1766673
Client Sample ID:EXC-4 Collected Date/Time:08/12/24 12:24
Lab File ID:0818_30 Received Date/Time:08/13/24 12:00
Instrument ID:VOCMS52 Preparation Date/Time:08/12/24 12:24
Analytical Batch:WG2345308 Analysis Date/Time:08/18/24 21:50
Dilution Factor:1 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:6.26 g
Total Solids (%):80.0 Final Wt/Vol:5 mL
Analyte CAS RT Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
TPH (GC/MS) Low Fraction 8006-61-9 5 ND 0.229 0.625
Benzene 71-43-2 4.15 0.00451 0.000469 0.00125
Ethylbenzene 100-41-4 6.34 0.00129 0.000375 0.00125
Methyl tert-butyl ether 1634-04-4 3.09 ND 0.000437 0.00125
Naphthalene 91-20-3 9.83 ND 0.00622 0.00625
Toluene 108-88-3 5.34 ND 0.00154 0.00625
Xylenes, Total 1330-20-7 6.74 0.0102 0.000625 0.00375
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET EXC-
Lab Sample ID:L1766673-02 SDG:L1766673
Client Sample ID:EXC-Collected Date/Time:08/12/24 12:30
Lab File ID:0820_22 Received Date/Time:08/13/24 12:00
Instrument ID:VOCMS28 Preparation Date/Time:08/12/24 12:30
Analytical Batch:WG2345938 Analysis Date/Time:08/20/24 16:09
Dilution Factor:25 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:6.05 g
Total Solids (%):79.3 Final Wt/Vol:5 mL
Analyte CAS RT Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
TPH (GC/MS) Low Fraction 8006-61-9 0 ND 7.23 19.7
Benzene 71-43-2 4.10 0.0592 0.0148 0.0395
Ethylbenzene 100-41-4 6.27 0.0559 0.0118 0.0395
Methyl tert-butyl ether 1634-04-4 0 ND 0.0138 0.0395
Naphthalene 91-20-3 9.75 ND 0.197 0.197
Toluene 108-88-3 5.28 ND J4 0.0486 0.197
Xylenes, Total 1330-20-7 6.67 0.262 0.0197 0.118
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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6A-OR GC/MS INITIAL CALIBRATION DATA
SDG:L1766673 Analytical Method:8260B
Instrument ID:VOCMS28
Analyte RRF: 0.5 RRF: 1 RRF: 2 RRF: 5.0 RRF: 25 RRF: 100 RRF: 200 RRF. Avg %RSD COD
Analysis date/time 08/08/24
00:50
08/08/24
01:12
08/08/24
01:35
08/08/24
01:57
08/08/24
02:19
08/08/24
03:04
08/08/24
03:26
TPH (GC/MS) LOW FRACTION 1117 1171 1284 1309 1170 1149 1200.039 6.48
METHYL TERT-BUTYL ETHER 0.4290 0.4340 0.4690 0.4060 0.4760 0.4520 0.43 0.442245 5.6
BENZENE 0.9780 0.92 0.91 0.9050 0.9160 0.8690 0.8160 0.901987 5.5
TOLUENE 2.3640 2.2390 2.4850 1.5420 2.2730 2.2970 2.1670 2.195318 13.89
ETHYLBENZENE 0.76 0.7380 0.8420 0.8270 0.8360 0.85 0.8060 0.808464 5.37
M&P-XYLENE 0.9390 0.8880 0.9090 0.9780 1.02 1.0390 0.9990 0.967487 5.9
O-XYLENE 0.8160 0.8280 0.9120 0.8960 0.9580 0.9680 0.9380 0.902276 6.67
NAPHTHALENE 1.4560 1.3510 1.5130 1.5160 1.5280 1.7370 1.6890 1.541419 8.6
1,2-DICHLOROETHANE-D4 0.28 0.2790 0.2750 0.2780 0.2710 0.26 0.2560 0.271005 3.55
TOLUENE-D8 2.3890 2.3650 2.5040 1.5970 2.25 2.2280 2.1340 2.20952 13.41
4-BROMOFLUOROBENZENE 0.8120 0.8110 0.8360 0.8210 0.82 0.8150 0.7950 0.815828 1.54
File ID:0807B_05 0807B_06 0807B_07 0807B_08 0807B_09 0807B_11 0807B_12
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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6A-OR GC/MS INITIAL CALIBRATION DATA
SDG:L1766673 Analytical Method:8260B
Instrument ID:VOCMS52
Analyte RRF: 0.5 RRF: 1 RRF: 2 RRF: 5.0 RRF: 25 RRF: 75 RRF: 100 RRF: 200
Analysis date/time 08/16/24
00:11
08/16/24
00:31
08/16/24
00:51
08/16/24
01:11
08/16/24
01:31
08/16/24
01:51
08/16/24
02:11
08/16/24
02:31
TPH (GC/MS) LOW FRACTION 1347 1247 1191 1170 1209 1221
METHYL TERT-BUTYL ETHER 0.7080 0.62 0.6530 0.6410 0.6450 0.6150 0.5760 0.63
BENZENE 1.1050 1.0050 1.0630 1.0350 1.0860 1.0350 0.9810 1.0910
TOLUENE 3.8440 3.1610 3.4050 3.1720 3.3740 3.1050 2.8820 3.08
ETHYLBENZENE 1.2790 1.1340 1.1420 1.1510 1.2460 1.2050 1.1350 1.2940
M&P-XYLENE 1.4220 1.3690 1.4260 1.3840 1.4950 1.4520 1.3850 1.5630
O-XYLENE 1.4230 1.2960 1.3810 1.2780 1.4180 1.3110 1.2280 1.3320
NAPHTHALENE 2.9570 2.5940 2.6560 2.6520 2.9510 2.5890 2.5350 2.7890
1,2-DICHLOROETHANE-D4 0.2770 0.2770 0.2760 0.28 0.2820 0.2780 0.2730 0.28
TOLUENE-D8 2.5520 2.4990 2.5060 2.4520 2.4410 2.3680 2.2660 2.2230
4-BROMOFLUOROBENZENE 0.8430 0.8450 0.85 0.8080 0.8370 0.8320 0.8130 0.7920
File ID:0815_10 0815_11 0815_12 0815_13 0815_14 0815_15 0815_16 0815_17
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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6A-OR GC/MS INITIAL CALIBRATION DATA
SDG:L1766673 Analytical Method:8260B
Instrument ID:VOCMS52
Analyte RRF. Avg %RSD COD
Analysis date/time
TPH (GC/MS) LOW FRACTION 1230.885 5.1
METHYL TERT-BUTYL ETHER 0.635911 5.93
BENZENE 1.050066 4.16
TOLUENE 3.252937 8.94
ETHYLBENZENE 1.198278 5.61
M&P-XYLENE 1.437141 4.56
O-XYLENE 1.333461 5.18
NAPHTHALENE 2.715507 6.06
1,2-DICHLOROETHANE-D4 0.277641 0.99
TOLUENE-D8 2.413528 4.89
4-BROMOFLUOROBENZENE 0.827656 2.51
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7A-OR GC/MS CONTINUING
CALIBRATION VERIFICATION
SDG:L1766673 Calibration (begin) date/time:08/08/24 00:50
Instrument ID:VOCMS28 Calibration (end) date/time:08/15/24 12:54
Lab File ID:0807B_16 Analysis date/time:08/08/24 04:56
Analytical Method:8260B Sample ID:SSCV
Analyte Avg. RRF RRF Min. RRF Diff.Max Diff.True Value Result Result Limits
%%mg/l mg/l % Rec.%
BENZENE 0.901987 0.91555160 1.50 40 0.0250 0.02538 102
ETHYLBENZENE 0.808464 0.83907140 3.79 20.49 0.0250 0.02595 104
M&P-XYLENE 0.967487 1.027444 6.20 40 0.05 0.05310 106
METHYL TERT-BUTYL ETHER 0.442245 0.46001980 4.02 40 0.0250 0.02600 104
NAPHTHALENE 1.541419 1.650749 7.09 40 0.0250 0.02677 107 54 - 135
O-XYLENE 0.902276 0.970224 7.53 40 0.0250 0.02688 108
TOLUENE 2.195318 2.253793 2.66 20.49 0.0250 0.02567 103
XYLENES, TOTAL 0 1.063780 0 40 0.0750 0.07998 107
1,2-DICHLOROETHANE-D4 0.271005 0.29246210 7.92 40 0.0160 0.01727 108 70 - 130
4-BROMOFLUOROBENZENE 0.815828 0.83766250 2.68 40 0.0160 0.01643 103 67 - 138
TOLUENE-D8 2.209520 2.297389 3.98 40 0.0160 0.01664 104 75 - 131
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7A-OR GC/MS CONTINUING
CALIBRATION VERIFICATION
SDG:L1766673 Calibration (begin) date/time:08/08/24 00:50
Instrument ID:VOCMS28 Calibration (end) date/time:08/15/24 12:54
Lab File ID:0811A_14 Analysis date/time:08/11/24 23:16
Analytical Method:8260B Sample ID:SSCV
Analyte Avg. RRF RRF Min. RRF Diff.Max Diff.True Value Result Result Limits
%%mg/l mg/l % Rec.%
TPH (GC/MS) LOW FRACTION 1200.0390 1.283162 99.90 0 5 5.346 107
1,2-DICHLOROETHANE-D4 0.271005 0.29831330 10.10 40 0.0160 0.01761 110 70 - 130
4-BROMOFLUOROBENZENE 0.815828 0.82624910 1.28 40 0.0160 0.01620 101 67 - 138
TOLUENE-D8 2.209520 2.188045 0.9720 40 0.0160 0.01584 99 75 - 131
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7A-OR GC/MS CONTINUING
CALIBRATION VERIFICATION
SDG:L1766673 Calibration (begin) date/time:08/08/24 00:50
Instrument ID:VOCMS28 Calibration (end) date/time:08/15/24 12:54
Lab File ID:0820_04 Analysis date/time:08/20/24 09:17
Analytical Method:8260B Sample ID:ICV
Analyte Avg. RRF RRF Min. RRF Diff.Max Diff.True Value Result Result Limits
%%mg/l mg/l % Rec.%
BENZENE 0.901987 0.98381390 9.07 0.0250 0.02727 109
ETHYLBENZENE 0.808464 0.81155150 0.3820 20 0.0250 0.02510 100
M&P-XYLENE 0.967487 0.99357220 2.70 0.05 0.05135 103
METHYL TERT-BUTYL ETHER 0.442245 0.475767 7.58 0.0250 0.02689 108
NAPHTHALENE 1.541419 1.288379 16.40 0.0250 0.02090 83.60
O-XYLENE 0.902276 0.90655250 0.4740 0.0250 0.02512 100
TOLUENE 2.195318 2.282518 3.97 20 0.0250 0.02599 104
XYLENES, TOTAL 0 1.034415 0 0.0750 0.07647 102
1,2-DICHLOROETHANE-D4 0.271005 0.30823830 13.70 0.0160 0.01820 114 70 - 130
4-BROMOFLUOROBENZENE 0.815828 0.79768140 2.22 0.0160 0.01564 97.80 70 - 130
TOLUENE-D8 2.209520 2.223740 0.6440 0.0160 0.01610 101 70 - 130
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7A-OR GC/MS CONTINUING
CALIBRATION VERIFICATION
SDG:L1766673 Calibration (begin) date/time:08/08/24 00:50
Instrument ID:VOCMS28 Calibration (end) date/time:08/15/24 12:54
Lab File ID:0820_09 Analysis date/time:08/20/24 11:18
Analytical Method:8260B Sample ID:ICV
Analyte Avg. RRF RRF Min. RRF Diff.Max Diff.True Value Result Result Limits
%%mg/l mg/l % Rec.%
TPH (GC/MS) LOW FRACTION 1200.0390 1.434360 99.90 5 5.976 120 80 - 120
1,2-DICHLOROETHANE-D4 0.271005 0.29666770 9.47 0.0160 0.01752 109 70 - 130
4-BROMOFLUOROBENZENE 0.815828 0.84089850 3.07 0.0160 0.01649 103 70 - 130
TOLUENE-D8 2.209520 2.171355 1.73 0.0160 0.01572 98.20 70 - 130
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7A-OR GC/MS CONTINUING
CALIBRATION VERIFICATION
SDG:L1766673 Calibration (begin) date/time:08/16/24 00:11
Instrument ID:VOCMS52 Calibration (end) date/time:08/16/24 17:11
Lab File ID:0815_21 Analysis date/time:08/16/24 03:52
Analytical Method:8260B Sample ID:SSCV
Analyte Avg. RRF RRF Min. RRF Diff.Max Diff.True Value Result Result Limits
%%mg/l mg/l % Rec.%
BENZENE 1.050066 1.088047 3.62 40 0.0250 0.02590 104
ETHYLBENZENE 1.198278 1.286157 7.33 20.49 0.0250 0.02683 107
M&P-XYLENE 1.437141 1.554311 8.15 40 0.05 0.05408 108
METHYL TERT-BUTYL ETHER 0.635911 0.595889 6.29 40 0.0250 0.02343 93.70
NAPHTHALENE 2.715507 2.881828 6.12 40 0.0250 0.02653 106 54 - 135
O-XYLENE 1.333461 1.434136 7.55 40 0.0250 0.02689 108
TOLUENE 3.252937 3.385948 4.09 20.49 0.0250 0.02602 104
XYLENES, TOTAL 0 1.854456 0 40 0.0750 0.08097 108
1,2-DICHLOROETHANE-D4 0.277641 0.28522540 2.73 40 0.0160 0.01644 103 70 - 130
4-BROMOFLUOROBENZENE 0.827656 0.831111 0.4170 40 0.0160 0.01607 100 67 - 138
TOLUENE-D8 2.413528 2.588012 7.23 40 0.0160 0.01716 107 75 - 131
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7A-OR GC/MS CONTINUING
CALIBRATION VERIFICATION
SDG:L1766673 Calibration (begin) date/time:08/16/24 00:11
Instrument ID:VOCMS52 Calibration (end) date/time:08/16/24 17:11
Lab File ID:0815_47 Analysis date/time:08/16/24 18:12
Analytical Method:8260B Sample ID:SSCV
Analyte Avg. RRF RRF Min. RRF Diff.Max Diff.True Value Result Result Limits
%%mg/l mg/l % Rec.%
TPH (GC/MS) LOW FRACTION 1230.8850 1.489153 99.90 0 5 6.049 121
1,2-DICHLOROETHANE-D4 0.277641 0.27981080 0.7820 40 0.0160 0.01613 101 70 - 130
4-BROMOFLUOROBENZENE 0.827656 0.91066930 10 40 0.0160 0.01760 110 67 - 138
TOLUENE-D8 2.413528 2.552618 5.76 40 0.0160 0.01692 106 75 - 131
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7A-OR GC/MS CONTINUING
CALIBRATION VERIFICATION
SDG:L1766673 Calibration (begin) date/time:08/16/24 00:11
Instrument ID:VOCMS52 Calibration (end) date/time:08/16/24 17:11
Lab File ID:0818_03 Analysis date/time:08/18/24 11:09
Analytical Method:8260B Sample ID:ICV
Analyte Avg. RRF RRF Min. RRF Diff.Max Diff.True Value Result Result Limits
%%mg/l mg/l % Rec.%
BENZENE 1.050066 0.98538050 6.16 0.0250 0.02346 93.80
ETHYLBENZENE 1.198278 1.114609 6.98 20 0.0250 0.02325 93
M&P-XYLENE 1.437141 1.361496 5.26 0.05 0.04737 94.70
METHYL TERT-BUTYL ETHER 0.635911 0.58764080 7.59 0.0250 0.02310 92.40
NAPHTHALENE 2.715507 2.716503 0.0367 0.0250 0.02501 100
O-XYLENE 1.333461 1.243389 6.75 0.0250 0.02331 93.20
TOLUENE 3.252937 2.959668 9.02 20 0.0250 0.02275 91
XYLENES, TOTAL 0 1.630063 0 0.0750 0.07068 94.20
1,2-DICHLOROETHANE-D4 0.277641 0.30330880 9.24 0.0160 0.01748 109 70 - 130
4-BROMOFLUOROBENZENE 0.827656 0.78484880 5.17 0.0160 0.01517 94.80 70 - 130
TOLUENE-D8 2.413528 2.504317 3.76 0.0160 0.01660 104 70 - 130
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7A-OR GC/MS CONTINUING
CALIBRATION VERIFICATION
SDG:L1766673 Calibration (begin) date/time:08/16/24 00:11
Instrument ID:VOCMS52 Calibration (end) date/time:08/16/24 17:11
Lab File ID:0818_06 Analysis date/time:08/18/24 12:09
Analytical Method:8260B Sample ID:ICV
Analyte Avg. RRF RRF Min. RRF Diff.Max Diff.True Value Result Result Limits
%%mg/l mg/l % Rec.%
TPH (GC/MS) LOW FRACTION 1230.8850 1.274515 99.90 5 5.177 104 80 - 120
1,2-DICHLOROETHANE-D4 0.277641 0.294349 6.02 0.0160 0.01696 106 70 - 130
4-BROMOFLUOROBENZENE 0.827656 0.88027120 6.36 0.0160 0.01702 106 70 - 130
TOLUENE-D8 2.413528 2.513776 4.15 0.0160 0.01666 104 70 - 130
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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8B-OR ANALYTICAL SEQUENCE
SDG:L1766673 Analytical Method:8260B
Instrument ID:VOCMS28 Calibration Start Date:08/08/24 00:50
Calibration End Date:08/15/24 12:54
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
TUNE VOCMS28080724B0807B_01746224 0807B_01 08/07/24 23:20
CAL 0.5 0807B_05 08/08/24 00:50
CAL 1 0807B_06 08/08/24 01:12
CAL 2 0807B_07 08/08/24 01:35
CAL 5.0 0807B_08 08/08/24 01:57
CAL 25 0807B_09 08/08/24 02:19
CAL 100 0807B_11 08/08/24 03:04
CAL 200 0807B_12 08/08/24 03:26
SSCV VOCMS28080724B0807B_16746224 0807B_16 08/08/24 04:56
SSCV VOCMS28080724B0807B_18746224 0807B_18 08/08/24 05:40
CAL 0.5 0811A_05 08/11/24 19:55
CAL 1 0811A_06 08/11/24 20:17
CAL 2 0811A_07 08/11/24 20:40
CAL 5.0 0811A_08 08/11/24 21:02
CAL 10 0811A_09 08/11/24 21:24
CAL 20 0811A_10 08/11/24 21:47
SSCV VOCMS28081124A0811A_14746224 0811A_14 08/11/24 23:16
TUNE VOCMS280815240815_01746224 0815_01 08/15/24 09:55
CAL 0.5A 0815_04 08/15/24 11:02
CAL 1A 0815_05 08/15/24 11:25
CAL 5A 0815_06 08/15/24 11:47
CAL 10A 0815_07 08/15/24 12:09
CAL 15A 0815_08 08/15/24 12:32
CAL 20A 0815_09 08/15/24 12:54
TUNE VOCMS280820240820_02T746224 0820_02T 08/20/24 08:32
ICV VOCMS280820240820_04746224 0820_04 08/20/24 09:17
LCS R4109766-1 0820_05C 08/20/24 09:39 1 WG2345938
LCS R4109767-1 0820_05 08/20/24 09:39 1 WG2346375
LCS R4109768-1 0820_05B 08/20/24 09:39 1 WG2346377
ICV VOCMS280820240820_06746224 0820_06 08/20/24 10:11
LCS R4109767-2 0820_07A 08/20/24 10:33 1 WG2346375
LCS R4109768-2 0820_07B 08/20/24 10:33 1 WG2346377
ICV VOCMS280820240820_09746224 0820_09 08/20/24 11:18
BLANK R4109768-3 0820_12 08/20/24 12:25 1 WG2346377
BLANK R4109766-3 0820_13u 08/20/24 12:48 25 WG2345938
BLANK R4109767-3 0820_13 08/20/24 12:48 25 WG2346375
LCS R4109766-4 0820_14 08/20/24 13:10 1 WG2345938
L1766669-01 L1766669-01 0820_16 08/20/24 13:55 1.01 WG2346377
L1767483-01 L1767483-01 0820_17 08/20/24 14:17 1 WG2346377
L1764580-08 L1764580-08 0820_20 08/20/24 15:24 25 WG2346375
EXC-L1766673-02 0820_22 08/20/24 16:09 25 WG2345938
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8B-OR ANALYTICAL SEQUENCE
SDG:L1766673 Analytical Method:8260B
Instrument ID:VOCMS52 Calibration Start Date:08/16/24 00:11
Calibration End Date:08/16/24 17:11
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
TUNE VOCMS520815240815_06746527 0815_06 08/15/24 22:50
CAL 0.5 0815_10 08/16/24 00:11
CAL 1 0815_11 08/16/24 00:31
CAL 2 0815_12 08/16/24 00:51
CAL 5.0 0815_13 08/16/24 01:11
CAL 25 0815_14 08/16/24 01:31
CAL 75 0815_15 08/16/24 01:51
CAL 100 0815_16 08/16/24 02:11
CAL 200 0815_17 08/16/24 02:31
SSCV VOCMS520815240815_21746527 0815_21 08/16/24 03:52
SSCV VOCMS520815240815_25746527 0815_25 08/16/24 10:31
TUNE VOCMS520815240815_25746527 0815_25 08/16/24 10:31
CAL 0.5A 0815_28 08/16/24 11:40
CAL 1A 0815_29 08/16/24 12:00
CAL 5A 0815_30 08/16/24 12:20
CAL 10A 0815_31 08/16/24 12:40
CAL 15A 0815_32 08/16/24 13:00
CAL 20A 0815_33 08/16/24 13:20
CAL 0.5 0815_39 08/16/24 15:30
CAL 1 0815_40 08/16/24 15:51
CAL 2 0815_41 08/16/24 16:11
CAL 5.0 0815_42 08/16/24 16:31
CAL 10 0815_43 08/16/24 16:51
CAL 20 0815_44 08/16/24 17:11
SSCV VOCMS520815240815_47746527 0815_47 08/16/24 18:12
TUNE VOCMS520818240818_01T746527 0818_01T 08/18/24 10:29
ICV VOCMS520818240818_03746527 0818_03 08/18/24 11:09
LCS R4108548-1 0818_04 08/18/24 11:29 1 WG2345308
LCSD R4108548-2 0818_05 08/18/24 11:49 1 WG2345308
ICV VOCMS520818240818_06746527 0818_06 08/18/24 12:09
LCS R4108548-3 0818_07 08/18/24 12:29 1 WG2345308
BLANK R4108548-4 0818_09 08/18/24 13:09 1 WG2345308
L1765750-13 L1765750-13 0818_11 08/18/24 15:30 1 WG2345308
L1764110-06 L1764110-06 0818_12 08/18/24 15:50 1 WG2345308
L1764110-08 L1764110-08 0818_13 08/18/24 16:10 1 WG2345308
L1764110-10 L1764110-10 0818_14 08/18/24 16:30 1 WG2345308
L1764110-12 L1764110-12 0818_15 08/18/24 16:50 1 WG2345308
L1765750-04 L1765750-04 0818_16 08/18/24 17:10 1 WG2345308
L1765750-05 L1765750-05 0818_17 08/18/24 17:30 1 WG2345308
L1765750-06 L1765750-06 0818_18 08/18/24 17:50 1 WG2345308
L1765875-01 L1765875-01 0818_19 08/18/24 18:10 1 WG2345308
L1765875-02 L1765875-02 0818_20 08/18/24 18:30 1 WG2345308
L1765875-03 L1765875-03 0818_21 08/18/24 18:50 1 WG2345308
L1765875-04 L1765875-04 0818_22 08/18/24 19:10 1 WG2345308
L1765875-05 L1765875-05 0818_23 08/18/24 19:30 1 WG2345308
L1765875-06 L1765875-06 0818_24 08/18/24 19:50 1 WG2345308
L1765875-07 L1765875-07 0818_25 08/18/24 20:10 1 WG2345308
L1765875-08 L1765875-08 0818_26 08/18/24 20:30 1 WG2345308
L1765875-09 L1765875-09 0818_27 08/18/24 20:50 1 WG2345308
L1766247-01 L1766247-01 0818_28 08/18/24 21:10 1 WG2345308
L1766247-02 L1766247-02 0818_29 08/18/24 21:30 1 WG2345308
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
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8B-OR ANALYTICAL SEQUENCE
SDG:L1766673 Analytical Method:8260B
Instrument ID:VOCMS52 Calibration Start Date:08/16/24 00:11
Calibration End Date:08/16/24 17:11
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
EXC-4 L1766673-01 0818_30 08/18/24 21:50 1 WG2345308
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11-OR DETECTION LIMIT SUMMARY
Lab Sample IDs:L1766673-01,02 Analytical Method:8260B
Matrix:Solid Prep Method:5035A
Analyte CAS MDL RDL
mg/kg mg/kg
TPH (GC/MS) Low Fraction 8006-61-9 0.1830 0.50
Ethylbenzene 100-41-4 0.0003 0.0010
Methyl tert-butyl ether 1634-04-4 0.000350 0.0010
Naphthalene 91-20-3 0.004980 0.0050
Toluene 108-88-3 0.001230 0.0050
Benzene 71-43-2 0.000375 0.0010
Xylenes, Total 1330-20-7 0.0005 0.0030
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET R4108548-4
Lab Sample ID:R4108548-4 SDG:L1766673
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:0818_09 Received Date/Time:_______________
Instrument ID:VOCMS52 Preparation Date/Time:08/18/24 13:09
Analytical Batch:WG2345308 Analysis Date/Time:08/18/24 13:09
Dilution Factor:1 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:5 g
Total Solids (%):_______________Final Wt/Vol:5 mL
Analyte CAS RT Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
TPH (GC/MS) Low Fraction 8006-61-9 5 U 0.183 0.500
Benzene 71-43-2 0 U 0.000375 0.00100
Ethylbenzene 100-41-4 0 U 0.000300 0.00100
Methyl tert-butyl ether 1634-04-4 0 U 0.000350 0.00100
Naphthalene 91-20-3 9.82 U 0.00498 0.00500
Toluene 108-88-3 5.34 U 0.00123 0.00500
Xylenes, Total 1330-20-7 6.43 U 0.000500 0.00300
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET R4109766-3
Lab Sample ID:R4109766-3 SDG:L1766673
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:0820_13u Received Date/Time:_______________
Instrument ID:VOCMS28 Preparation Date/Time:08/20/24 12:48
Analytical Batch:WG2345938 Analysis Date/Time:08/20/24 12:48
Dilution Factor:25 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:5 g
Total Solids (%):_______________Final Wt/Vol:5 mL
Analyte CAS RT Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
TPH (GC/MS) Low Fraction 8006-61-9 0 U 4.58 12.5
Benzene 71-43-2 0 U 0.00938 0.0250
Ethylbenzene 100-41-4 0 U 0.00750 0.0250
Methyl tert-butyl ether 1634-04-4 0 U 0.00875 0.0250
Naphthalene 91-20-3 0 U 0.125 0.125
Toluene 108-88-3 0 U 0.0308 0.125
Xylenes, Total 1330-20-7 0 U 0.0125 0.0750
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET R4108548-1
Lab Sample ID:R4108548-1 SDG:L1766673
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:0818_04 Received Date/Time:_______________
Instrument ID:VOCMS52 Preparation Date/Time:08/18/24 11:29
Analytical Batch:WG2345308 Analysis Date/Time:08/18/24 11:29
Dilution Factor:1 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:5 g
Total Solids (%):_______________Final Wt/Vol:5 mL
Analyte CAS RT Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Benzene 71-43-2 4.15 0.0256 0.000375 0.00100
Ethylbenzene 100-41-4 6.34 0.0254 0.000300 0.00100
Methyl tert-butyl ether 1634-04-4 3.09 0.0255 0.000350 0.00100
Naphthalene 91-20-3 9.82 0.0290 0.000498 0.00500
Toluene 108-88-3 5.34 0.0252 0.00123 0.00500
Xylenes, Total 1330-20-7 6.74 0.0786 0.000500 0.00300
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET R4108548-3
Lab Sample ID:R4108548-3 SDG:L1766673
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:0818_07 Received Date/Time:_______________
Instrument ID:VOCMS52 Preparation Date/Time:08/18/24 12:29
Analytical Batch:WG2345308 Analysis Date/Time:08/18/24 12:29
Dilution Factor:1 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:5 g
Total Solids (%):_______________Final Wt/Vol:5 mL
Analyte CAS RT Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
TPH (GC/MS) Low Fraction 8006-61-9 5 5.34 0.183 0.500
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET R4109766-1
Lab Sample ID:R4109766-1 SDG:L1766673
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:0820_05C Received Date/Time:_______________
Instrument ID:VOCMS28 Preparation Date/Time:08/20/24 09:39
Analytical Batch:WG2345938 Analysis Date/Time:08/20/24 09:39
Dilution Factor:1 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:5 g
Total Solids (%):_______________Final Wt/Vol:5 mL
Analyte CAS RT Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Benzene 71-43-2 4.11 0.0278 0.000375 0.00100
Ethylbenzene 100-41-4 6.28 0.0248 0.000300 0.00100
Methyl tert-butyl ether 1634-04-4 3.07 0.0209 0.000350 0.00100
Naphthalene 91-20-3 9.75 0.0226 0.000498 0.00500
Toluene 108-88-3 5.29 0.0304 J4 0.00123 0.00500
Xylenes, Total 1330-20-7 6.67 0.0669 0.000500 0.00300
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET R4109766-4
Lab Sample ID:R4109766-4 SDG:L1766673
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:0820_14 Received Date/Time:_______________
Instrument ID:VOCMS28 Preparation Date/Time:08/20/24 13:10
Analytical Batch:WG2345938 Analysis Date/Time:08/20/24 13:10
Dilution Factor:1 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:5 g
Total Solids (%):_______________Final Wt/Vol:5 mL
Analyte CAS RT Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
TPH (GC/MS) Low Fraction 8006-61-9 5 4.65 0.183 0.500
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1A-OR SAMPLE RESULT SUMMARY SAMPLE NO.:
ORGANIC ANALYSIS DATA SHEET R4108548-2
Lab Sample ID:R4108548-2 SDG:L1766673
Client Sample ID:LCSD Collected Date/Time:_______________
Lab File ID:0818_05 Received Date/Time:_______________
Instrument ID:VOCMS52 Preparation Date/Time:08/18/24 11:49
Analytical Batch:WG2345308 Analysis Date/Time:08/18/24 11:49
Dilution Factor:1 Prep Method:5035A
Analytical Method:8260B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:5 g
Total Solids (%):_______________Final Wt/Vol:5 mL
Analyte CAS RT Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Benzene 71-43-2 4.15 0.0238 0.000375 0.00100
Ethylbenzene 100-41-4 6.34 0.0244 0.000300 0.00100
Methyl tert-butyl ether 1634-04-4 3.09 0.0237 0.000350 0.00100
Naphthalene 91-20-3 9.82 0.0242 0.000498 0.00500
Toluene 108-88-3 5.34 0.0235 0.00123 0.00500
Xylenes, Total 1330-20-7 6.74 0.0735 0.000500 0.00300
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GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
The information below is designed to better explain the various terms used in your report of analytical results from the Laboratory. This is not
intended as a comprehensive explanation, and if you have additional questions please contact your project representative.
Results Disclaimer - Information that may be provided by the customer, and contained within this report, include Permit Limits, Project Name,
Sample ID, Sample Matrix, Sample Preservation, Field Blanks, Field Spikes, Field Duplicates, On-Site Data, Sampling Collection Dates/Times, and
Sampling Location. Results relate to the accuracy of this information provided, and as the samples are received.
Abbreviations and Definitions
COD Coefficient of Determination.
(dry)Results are reported based on the dry weight of the sample. [this will only be present on a dry report basis for soils].
Mass Mass of parameter.
MDL Method Detection Limit.
MDL (dry)Method Detection Limit.
RDL Reported Detection Limit.
RDL (dry)Reported Detection Limit.
Rec.Recovery.
RPD Relative Percent Difference.
RRF Relative Response Factor.
RT Retention Time.
SDG Sample Delivery Group.
Analyte The name of the particular compound or analysis performed. Some Analyses and Methods will have multiple analytes
reported.
Dilution
If the sample matrix contains an interfering material, the sample preparation volume or weight values differ from the
standard, or if concentrations of analytes in the sample are higher than the highest limit of concentration that the
laboratory can accurately report, the sample may be diluted for analysis. If a value different than 1 is used in this field, the
result reported has already been corrected for this factor.
Limits
These are the target % recovery ranges or % difference value that the laboratory has historically determined as normal
for the method and analyte being reported. Successful QC Sample analysis will target all analytes recovered or
duplicated within these ranges.
Qualifier
This column provides a letter and/or number designation that corresponds to additional information concerning the result
reported. If a Qualifier is present, a definition per Qualifier is provided within the Glossary and Definitions page and
potentially a discussion of possible implications of the Qualifier in the Case Narrative if applicable.
Result
The actual analytical final result (corrected for any sample specific characteristics) reported for your sample. If there was
no measurable result returned for a specific analyte, the result in this column may state “ND” (Not Detected) or “BDL”
(Below Detectable Levels). The information in the results column should always be accompanied by either an MDL
(Method Detection Limit) or RDL (Reporting Detection Limit) that defines the lowest value that the laboratory could detect
or report for this analyte.
Uncertainty
(Radiochemistry)Confidence level of 2 sigma.
Wavelength Wavelength of parameter.
Case Narrative (Cn)
A brief discussion about the included sample results, including a discussion of any non-conformances to protocol
observed either at sample receipt by the laboratory from the field or during the analytical process. If present, there will
be a section in the Case Narrative to discuss the meaning of any data qualifiers used in the report.
Quality Control
Summary (Qc)
This section of the report includes the results of the laboratory quality control analyses required by procedure or
analytical methods to assist in evaluating the validity of the results reported for your samples. These analyses are not
being performed on your samples typically, but on laboratory generated material.
Sample Chain of
Custody (Sc)
This is the document created in the field when your samples were initially collected. This is used to verify the time and
date of collection, the person collecting the samples, and the analyses that the laboratory is requested to perform. This
chain of custody also documents all persons (excluding commercial shippers) that have had control or possession of the
samples from the time of collection until delivery to the laboratory for analysis.
Sample Results (Sr)
This section of your report will provide the results of all testing performed on your samples. These results are provided
by sample ID and are separated by the analyses performed on each sample. The header line of each analysis section for
each sample will provide the name and method number for the analysis reported.
Sample Summary (Ss)This section of the Analytical Report defines the specific analyses performed for each sample ID, including the dates and
times of preparation and/or analysis.
Qualifier Description
J1 Surrogate recovery limits have been exceeded; values are outside upper control limits.
J4 The associated batch QC was outside the established quality control range for accuracy.
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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Pace Analytical National 12065 Lebanon Rd Mount Juliet, TN 37122
Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN000032021-1
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹TN00003
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹DW21704
Georgia NELAP North Carolina ³41
Georgia ¹923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶KY90010 South Carolina 84004002
Kentucky ²16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴2006
Louisiana LA018 Texas T104704245-20-18
Maine TN00003 Texas ⁵LAB0152
Maryland 324 Utah TN000032021-11
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 110033
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 998093910
Montana CERT0086 Wyoming A2LA
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS

¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace Analytical.
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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ANALYTICAL REPORT
October 28, 2024
Wasatch Environmental
Sample Delivery Group:L1770255
Samples Received:08/22/2024
Project Number:
Description:Emergency Response and Remediation Split Samples
Report To:Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Entire Report Reviewed By:
October 28, 2024
[Preliminary Report]
John Hawkins
Project Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be
reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace
Analytical National is performed per guidance provided in laboratory standard operating procedures ENV-SOP-MTJL-0067 and
ENV-SOP-MTJL-0068. Where sampling conducted by the customer, results relate to the accuracy of the information provided,
and as the samples are received.
Pace Analytical National
12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 mydata.pacelabs.com
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1770255 10/28/24 13:09 1 of 53
October 28, 2024
John Hawkins
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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TABLE OF CONTENTSTABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 4
Cn: Case Narrative 5
Su: Summary Results 6
2540 G-2011 Total Solids 6
Sample Result Inorganic Analysis Data Sheet 7
L1770255-01 08/24/24 16:38 LOGBAL1 7
BLANK(R4111467-1) WG2349218 08/24/24 16:38 LOGBAL1 8
DUP(R4111467-3) WG2349218 08/24/24 16:38 LOGBAL1 9
LCS(R4111467-2) WG2349218 08/24/24 16:38 LOGBAL1 10
Blank 11
LOGBAL1 WG2349218 11
Laboratory Duplicate 12
WG2349218 DUP(R4111467-3) 12
Laboratory Control Sample / Duplicate 13
WG2349218 LCS(R4111467-2) 13
Detection Limit Summary 14
2540 G-2011 - Solid 14
Analysis Log 15
LOGBAL1 WG2349218 15
6020 Metals (ICPMS) 16
Sample Result Inorganic Analysis Data Sheet 17
L1770255-01 08/28/24 12:23 ICPMS14 17
BLANK(R4112786-1) WG2351421 08/28/24 11:18 ICPMS14 18
LCS(R4112786-2) WG2351421 08/28/24 11:21 ICPMS14 19
MS(R4112786-5) WG2351421 08/28/24 11:34 ICPMS14 20
MS(R4112786-8) WG2351421 08/28/24 12:07 ICPMS14 21
MSD(R4112786-6) WG2351421 08/28/24 11:37 ICPMS14 22
MSD(R4112786-9) WG2351421 08/28/24 12:10 ICPMS14 23
PS(R4112786-4) WG2351421 08/28/24 11:31 ICPMS14 24
PS(R4112786-7) WG2351421 08/28/24 12:04 ICPMS14 25
SD(R4112786-3) WG2351421 08/28/24 11:28 ICPMS14 26
Calibration Verification 27
ICPMS14 082824ICPMS14 27
Blank 29
ICPMS14 082824ICPMS14 29
ICP Interference Check Sample 31
ICPMS14 08/28/24 10:09 31
Matrix Spike / Duplicate 32
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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WG2351421 MS(R4112786-5) MSD(R4112786-6) 32
WG2351421 MS(R4112786-8) MSD(R4112786-9) 33
Post Digestion Spike 34
WG2351421 PS(R4112786-4) 34
WG2351421 PS(R4112786-7) 35
Laboratory Control Sample / Duplicate 36
WG2351421 LCS(R4112786-2) 36
Serial Dilution 37
WG2351421 SD(R4112786-3) 37
Detection Limit Summary 38
6020 - Solid 38
Linear Dynamic Range 39
ICPMS14 08/16/24 10:13 39
Internal Standard Association 40
ICPMS14 08/28/24 07:39 40
Analysis Log 41
ICPMS14 082824ICPMS14 08/28/24 08:25 41
ICP/MS Tune 42
ICPMS14 082824ICPMS14 08/28/24 07:39 42
Internal Standard Relative Intensity 43
ICPMS14 082824ICPMS14 43
Initial Calibration Recovery 46
ICPMS14 082824ICPMS14 08/28/24 08:25 46
ICP/MS Initial Calibration 50
ICPMS14 082824ICPMS14 08/28/24 08:25 50
Gl: Glossary of Terms 51
Al: Accreditations & Locations 52
Sc: Sample Chain of Custody 53
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
EXC-2 L1770255-01 Solid Jacob Scott 08/21/24 10:21 08/22/24 08:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2349218 1 08/24/24 16:17 08/24/24 16:38 JAV Mt. Juliet, TN
Metals (ICPMS) by Method 6020 WG2351421 5 08/27/24 16:33 08/28/24 12:23 JPD Mt. Juliet, TN
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the
appropriate preservatives, and within method specified holding times, unless qualified or notated within
the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples
have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control
are within established criteria except where addressed in this case narrative, a non-conformance form
or properly qualified within the sample results. By my digital signature below, I affirm to the best of my
knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the
quality of the data have been identified by the laboratory, and no information or data have been
knowingly withheld that would affect the quality of the data.
[Preliminary Report]
John Hawkins
Project Manager
Report Revision History
Level II Report - Version 1: 08/29/24 10:12
Project Narrative
Reprint for QC3 and EDD
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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John Hawkins
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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2540 G-2011 Total Solids
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET EXC-2
Lab Sample ID:L1770255-01 SDG:L1770255
Client Sample ID:EXC-2 Collected Date/Time:08/21/24 10:21
Lab File ID:04 Received Date/Time:08/22/24 08:30
Instrument ID:LOGBAL1 Preparation Date/Time:08/24/24 16:17
Analytical Batch:WG2349218 Analysis Date/Time:08/24/24 16:38
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:10.948 g
Total Solids (%):83.8 Final Wt/Vol:9.378 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 83.8
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4111467-1
Lab Sample ID:R4111467-1 SDG:L1770255
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:01 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/24/24 16:05
Analytical Batch:WG2349218 Analysis Date/Time:08/24/24 16:38
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:1.275 g
Total Solids (%):_______________Final Wt/Vol:1.274 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 0.00100
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4111467-3
Lab Sample ID:R4111467-3 SDG:L1770255
Client Sample ID:DUP Collected Date/Time:08/16/24 13:36
Lab File ID:02 Received Date/Time:08/22/24 09:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/24/24 16:17
Analytical Batch:WG2349218 Analysis Date/Time:08/24/24 16:38
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:11.916 g
Total Solids (%):77.0 Final Wt/Vol:9.326 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 75.7
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4111467-2
Lab Sample ID:R4111467-2 SDG:L1770255
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:03 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/24/24 16:05
Analytical Batch:WG2349218 Analysis Date/Time:08/24/24 16:38
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:11.266 g
Total Solids (%):_______________Final Wt/Vol:6.265 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 50.0
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1770255 Calibration (begin) date/time:_______________
Instrument ID:LOGBAL1 Calibration (end) date/time:_______________
Analytical Method:2540 G-2011 Analytical Run:WG2349218
Sample ID:BLANK Result BLANK
Qual
File ID:01
Analyte %
TOTAL SOLIDS 0.00100
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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6-IN DUPLICATES SAMPLE NO.:
L1770255-01 R4111467-3
DUP Sample / File ID:R4111467-3 / 02 SDG:L1770255
OS Sample / File ID:L1770338-07 / 06 Analytical Batch:WG2349218
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte OS
Result
DUP
Result RPD RPD
Limits
%%%%
Total Solids 77.0 75.7 1.71 10
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7-IN LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4111467-2
RECOVERY _______________
L1770255-01
LCS Sample / File ID:R4111467-2 / 03 SDG:L1770255
LCSD Sample / File ID:_______________Analytical Batch:WG2349218
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD
Rec.Rec. Limits RPD RPD Limits
%%%%%%%
Total Solids 50.0 50.0 100 90.0 - 110
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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9-IN DETECTION LIMIT SUMMARY
Lab Sample IDs:L1770255-01 Analytical Method:2540 G-2011
Matrix:Solid Prep Method:SM 2540 G
Analyte CAS Wavelength Mass MDL RDL
%%
Total Solids TSOLIDS
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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12-IN ANALYSIS LOG
SDG:L1770255 Analytical Method:2540 G-2011
Instrument ID:LOGBAL1 Calibration Start Date:_______________
Analytical Run:WG2349218 Calibration End Date:_______________
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
BLANK R4111467-1 01 08/24/24 16:38 1 WG2349218
DUP R4111467-3 02 08/24/24 16:38 1 WG2349218
LCS R4111467-2 03 08/24/24 16:38 1 WG2349218
OS L1770338-07 06 08/24/24 16:38
EXC-2 L1770255-01 04 08/24/24 16:38 1 WG2349218
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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6020 Metals (ICPMS)
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET EXC-2
Lab Sample ID:L1770255-01 SDG:L1770255
Client Sample ID:EXC-2 Collected Date/Time:08/21/24 10:21
Lab File ID:20240828122337 Received Date/Time:08/22/24 08:30
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:33
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 12:23
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.52 g
Total Solids (%):83.8 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 14.3 0.119 1.19
Lead 7439-92-1 324 0.118 2.39
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-1
Lab Sample ID:R4112786-1 SDG:L1770255
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:20240828111813 Received Date/Time:_______________
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:27
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 11:18
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.49 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 U 0.100 1.00
Lead 7439-92-1 U 0.0990 2.00
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-2
Lab Sample ID:R4112786-2 SDG:L1770255
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:20240828112130 Received Date/Time:_______________
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:27
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 11:21
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.53 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 93.5 0.100 1.00
Lead 7439-92-1 90.4 0.0990 2.00
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-5
Lab Sample ID:R4112786-5 SDG:L1770255
Client Sample ID:MS Collected Date/Time:08/16/24 09:30
Lab File ID:20240828113433 Received Date/Time:08/21/24 09:00
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:27
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 11:34
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.51 g
Total Solids (%):71.3 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 143 0.140 1.40
Lead 7439-92-1 142 0.139 2.81
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-8
Lab Sample ID:R4112786-8 SDG:L1770255
Client Sample ID:MS Collected Date/Time:08/24/24 16:55
Lab File ID:20240828120716 Received Date/Time:08/26/24 10:00
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:27
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 12:07
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.51 g
Total Solids (%):88.8 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 104 0.113 1.13
Lead 7439-92-1 104 0.112 2.25
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-6
Lab Sample ID:R4112786-6 SDG:L1770255
Client Sample ID:MSD Collected Date/Time:08/16/24 09:30
Lab File ID:20240828113749 Received Date/Time:08/21/24 09:00
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:27
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 11:37
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.53 g
Total Solids (%):71.3 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 134 0.140 1.40
Lead 7439-92-1 132 0.139 2.81
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-9
Lab Sample ID:R4112786-9 SDG:L1770255
Client Sample ID:MSD Collected Date/Time:08/24/24 16:55
Lab File ID:20240828121032 Received Date/Time:08/26/24 10:00
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:27
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 12:10
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.53 g
Total Solids (%):88.8 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 98.7 0.113 1.13
Lead 7439-92-1 97.4 0.112 2.25
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-4
Lab Sample ID:R4112786-4 SDG:L1770255
Client Sample ID:PS Collected Date/Time:08/16/24 09:30
Lab File ID:20240828113118 Received Date/Time:08/21/24 09:00
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:33
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 11:31
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.53 g
Total Solids (%):71.3 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 143 0.140 1.40
Lead 7439-92-1 139 0.139 2.81
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-7
Lab Sample ID:R4112786-7 SDG:L1770255
Client Sample ID:PS Collected Date/Time:08/24/24 16:55
Lab File ID:20240828120401 Received Date/Time:08/26/24 10:00
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:33
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 12:04
Dilution Factor:5 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.53 g
Total Solids (%):88.8 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 108 0.113 1.13
Lead 7439-92-1 105 0.112 2.25
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112786-3
Lab Sample ID:R4112786-3 SDG:L1770255
Client Sample ID:SD Collected Date/Time:08/16/24 09:30
Lab File ID:20240828112801 Received Date/Time:08/21/24 09:00
Instrument ID:ICPMS14 Preparation Date/Time:08/27/24 16:33
Analytical Batch:WG2351421 Analysis Date/Time:08/28/24 11:28
Dilution Factor:25 Prep Method:3051
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.53 g
Total Solids (%):71.3 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 12.0 0.702 7.02
Lead 7439-92-1 ND 0.695 14.0
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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2-IN CALIBRATION VERIFICATION
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Concentration Units:mg/l
ICV ICVLL CCV
Sample ID:ICPMS140828240925-4 ICPMS140828241002-4 ICPMS140828241041-4
Analyte True Found %R %RSD True Found %R %RSD True Found %R %RSD
ARSENIC 0.10 0.09857308 98.6
0 0.860000 0.0010 0.001009698 101 10.600000 0.10 0.1031381 103 0.590000
LEAD 0.10 0.101606 102 2.580000 0.0010 0.001017926 102 2.050000 0.10 0.1010212 101 1.880000
ICV Limits:90 - 110 ICVLL Limits:50 - 150 CCV Limits:90 - 110 CCVLL Limits:50 - 150
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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2-IN CALIBRATION VERIFICATION
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Concentration Units:mg/l
CCV CCV CCVLL
Sample ID:ICPMS140828241150-2 ICPMS140828241233-2 ICPMS140828241323-4
Analyte True Found %R %RSD True Found %R %RSD True Found %R %RSD
ARSENIC 0.10 0.100955 101 1.800000 0.10 0.1033225 103 2.600000 0.0010 0.001059847 106 4.880000
LEAD 0.10 0.1004448 100 1.660000 0.10 0.1005668 101 0.350000 0.0010 0.00102653 103 1.830000
ICV Limits:90 - 110 ICVLL Limits:50 - 150 CCV Limits:90 - 110 CCVLL Limits:50 - 150
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Sample ID:ICB Result ICB Qual CCB Result CCB Qual BLANK Result BLANK
Qual CCB Result CCB Qual
File ID:20240828093928-4 20240828110201-4 20240828111813 20240828115728-2
Analyte mg/l mg/l mg/kg mg/l
ARSENIC 0.000002767 U 0.000039479 U U 0.000034484 U
LEAD 0.000013775 U 0.000076269 U U 0.000060289 U
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Sample ID:CCB Result CCB Qual
File ID:20240828123909-2
Analyte mg/l
ARSENIC 0.000020506 U
LEAD 0.000063293 U
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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4-IN INTERFERENCE CHECK SAMPLE
SDG:L1770255 Analytical Method:6020
Instrument ID:ICPMS14 Date:08/28/24 10:09
Instrument Run:082824ICPMS14
Analyte True Found True Found
ICSA ICSA ICSA ICSAB ICSAB ICSAB
mg/l mg/l % Rec.mg/l mg/l % Rec.
ALUMINUM 100 107.5586 108 100 109.448 109
ANTIMONY 0 0.000114165 0.02 0.02176508 109
ARSENIC 0 0.000045423 0.02 0.01944567 97.20
BARIUM 0 0.000563437 0.02 0.01981667 99.10
BERYLLIUM 0 0.000011576 0.02 0.02051204 103
BISMUTH (NO HE)1412268 89.20 1348311 85.20
BORON 0 0.001742675 0.02 0.02208777 110
CADMIUM 0 0.000131972 0.02 0.02081878 104
CALCIUM 100 95.64196 95.60 100 96.51297 96.50
CHROMIUM 0 0.001188765 0.02 0.02102722 105
COBALT 0 0.000127482 0.02 0.02032701 102
COPPER 0 0.001381567 0.02 0.02107942 105
GERMANIUM 10958.88 93 10627.96 90.20
GERMANIUM (NO HE)95796.95 96.50 91229.46 91.90
IRON 100 100.5141 101 100 99.87774 99.90
LEAD 0 0.000115999 0.02 0.02005079 100
LITHIUM 0 0.000432335 0 0.000454574
MAGNESIUM 100 101.2749 101 100 102.1798 102
MANGANESE 0 0.000298625 0.02 0.02046771 102
MOLYBDENUM 2 2.053392 103 2 2.06581 103
NICKEL 0 0.000315767 0.02 0.02012343 101
POTASSIUM 100 97.84201 97.80 100 99.48191 99.50
RHODIUM 255725.7 87.70 245963.3 84.40
SCANDIUM 146858.5 92.50 142956.7 90
SCANDIUM (NO HE)2750809 92.90 2694585 91
SELENIUM 0 0.000114997 0.02 0.02123901 106
SILVER 0 0.000006567 0.02 0.02046902 102
SODIUM 100 100.3658 100 100 103.249 103
STRONTIUM 0 0.000761598 0.02 0.02174528 109
TELLURIUM 22565.75 87.40 21461.66 83.10
TELLURIUM (HIGH HE)115156.4 88.60 111905.2 86.10
TELLURIUM (NO HE)259203.3 90.20 247504.4 86.20
THALLIUM 0 0.000004602 0.02 0.01960053 98
THORIUM 0 0.000014316 0.02 0.02001839 100
TIN 0 0.000134206 0.02 0.01933205 96.70
TITANIUM 2 2.018223 101 2 2.024667 101
URANIUM 0 0.000011148 0.02 0.01983681 99.20
VANADIUM 0 0.000008281 0.02 0.02010339 101
ZINC 0 0.000673316 0.02 0.02076039 104
ICSA Limits:80 - 120 ICSAB Limits:80 - 120
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1770255 10/28/24 13:09 31 of 53
5A-IN MATRIX SPIKE /SAMPLE NO.:
MATRIX SPIKE DUPLICATE RECOVERY R4112786-5
L1770255-01 R4112786-6
MS Sample / File ID:R4112786-5 / 20240828113433 SDG:L1770255
MSD Sample / File ID:R4112786-6 / 20240828113749 Analytical Batch:WG2351421
OS Sample / File ID:L1769970-04 / 20240828112445 Matrix:Solid
Instrument ID:ICPMS14
Analytical Method:6020
Analyte
Spike
Amount
(dry)
OS
Result
(dry)
MS
Result
(dry)
MSD
Result
(dry)
MS Rec.MSD
Rec.Dilution Rec. Limits RPD RPD Limits
mg/kg mg/kg mg/kg mg/kg %%%%%
Arsenic 140 11.8 143 134 93.5 87.3 5 75.0 - 125 6.27 20
Lead 140 9.14 142 132 94.7 87.4 5 75.0 - 125 7.54 20
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5A-IN MATRIX SPIKE /SAMPLE NO.:
MATRIX SPIKE DUPLICATE RECOVERY R4112786-8
L1770255-01 R4112786-9
MS Sample / File ID:R4112786-8 / 20240828120716 SDG:L1770255
MSD Sample / File ID:R4112786-9 / 20240828121032 Analytical Batch:WG2351421
OS Sample / File ID:L1771468-10 / 20240828120045 Matrix:Solid
Instrument ID:ICPMS14
Analytical Method:6020
Analyte
Spike
Amount
(dry)
OS
Result
(dry)
MS
Result
(dry)
MSD
Result
(dry)
MS Rec.MSD
Rec.Dilution Rec. Limits RPD RPD Limits
mg/kg mg/kg mg/kg mg/kg %%%%%
Arsenic 113 ND 104 98.7 92.1 87.1 5 75.0 - 125 5.61 20
Lead 113 ND 104 97.4 91.7 85.8 5 75.0 - 125 6.56 20
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5B-IN POST-DIGESTION / DISTILLATION SPIKE SAMPLE NO.:
SAMPLE RECOVERY R4112786-4
L1770255-01
PS Sample / File ID:R4112786-4 / 20240828113118 SDG:L1770255
OS Sample / File ID:L1769970-04 / 20240828112445 Analytical Batch:WG2351421
Instrument ID:ICPMS14 Dilution Factor:5
Analytical Method:6020 Matrix:Solid
Analyte
Spike
Amount
(dry)
OS
Result
(dry)
PD
Result
(dry)
DS
Result
(dry)
PD Rec.DS Rec.Dilution Rec.
Limits RPD RPD
Limits
mg/kg mg/kg mg/kg %%%mg/kg mg/kg
Arsenic 140 11.8 143 93.7 5 80.0 -
120
Lead 140 9.14 139 92.3 5 80.0 -
120
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1770255 10/28/24 13:09 34 of 53
5B-IN POST-DIGESTION / DISTILLATION SPIKE SAMPLE NO.:
SAMPLE RECOVERY R4112786-7
L1770255-01
PS Sample / File ID:R4112786-7 / 20240828120401 SDG:L1770255
OS Sample / File ID:L1771468-10 / 20240828120045 Analytical Batch:WG2351421
Instrument ID:ICPMS14 Dilution Factor:5
Analytical Method:6020 Matrix:Solid
Analyte
Spike
Amount
(dry)
OS
Result
(dry)
PD
Result
(dry)
DS
Result
(dry)
PD Rec.DS Rec.Dilution Rec.
Limits RPD RPD
Limits
mg/kg mg/kg mg/kg %%%mg/kg mg/kg
Arsenic 113 ND 108 95.8 5 80.0 -
120
Lead 113 ND 105 92.4 5 80.0 -
120
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7-IN LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4112786-2
RECOVERY _______________
L1770255-01
LCS Sample / File ID:R4112786-2 / 20240828112130 SDG:L1770255
LCSD Sample / File ID:_______________Analytical Batch:WG2351421
Instrument ID:ICPMS14 Dilution Factor:5
Analytical Method:6020 Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD
Rec.Rec. Limits RPD RPD Limits
mg/kg mg/kg %%%%%
Arsenic 100 93.5 93.5 80.0 - 120
Lead 100 90.4 90.4 80.0 - 120
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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8-IN ICP AND ICP/MS SAMPLE NO.:
SERIAL DILUTIONS R4112786-3
L1770255-01
SD Sample / File ID:R4112786-3 / 20240828112801 SDG:L1770255
OS Sample / File ID:L1769970-04 / 20240828112445 Analytical Batch:WG2351421
Lab File ID:20240828112801 Dilution Factor:25
Instrument ID:ICPMS14 Matrix:Solid
Analytical Method:6020
Analyte
OS
Result
(dry)
SD
Result
(dry)
RPD RPD
Limits
mg/kg mg/kg %%
Arsenic 11.8 12.0 1.52 10
Lead 9.14 ND 2.79 10
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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9-IN DETECTION LIMIT SUMMARY
Lab Sample IDs:L1770255-01 Analytical Method:6020
Matrix:Solid Prep Method:3051
Analyte CAS Wavelength Mass MDL RDL
mg/kg mg/kg
Arsenic 7440-38-2 75 0.02 0.20
Lead 7439-92-1 208 0.0198 0.40
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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10C-IN LINEAR DYNAMIC RANGE
SDG:L1770255 Analytical Method:6020
Instrument ID:ICPMS14 Date:08/16/24 10:13
Analyte LDR
ppm
ALUMINUM 100
ANTIMONY 10
ARSENIC 10
BARIUM 10
BERYLLIUM 10
BORON 5
CADMIUM 10
CALCIUM 1000
CHROMIUM 10
COBALT 10
IRON 100
LEAD 10
MAGNESIUM 1000
MANGANESE 10
MOLYBDENUM 10
NICKEL 10
POTASSIUM 1000
SELENIUM 10
SODIUM 1000
STRONTIUM 5
THALLIUM 10
THORIUM 10
TIN 10
TITANIUM 10
URANIUM 10
VANADIUM 10
ZINC 10
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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11-IN INTERNAL STANDARD ASSOCIATION
SDG:L1770255 Analytical Method:6020
Instrument ID:ICPMS14 Analysis Date:08/28/24 07:39
Instrument Run:082824ICPMS14
Analyte Assoc. Internal Standard 1
ARSENIC - 75 GERMANIUM - 72
LEAD - 208 BISMUTH (NO HE) - 209
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1770255 10/28/24 13:09 40 of 53
12-IN ANALYSIS LOG
SDG:L1770255 Analytical Method:6020
Instrument ID:ICPMS14 Calibration Start Date:08/28/24 08:25
Analytical Run:082824ICPMS14 Calibration End Date:08/28/24 08:49
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
CALBLK ICPMS140828240821 20240828082140 08/28/24 08:21
CAL STD1 20240828082512 08/28/24 08:25
CAL STD3 20240828082843 08/28/24 08:28
CAL STD4 20240828083214 08/28/24 08:32
CAL STD5 20240828083545 08/28/24 08:35
CAL STD6 20240828083917 08/28/24 08:39
CAL STD7 20240828084248 08/28/24 08:42
CAL STD8 20240828084617 08/28/24 08:46
CAL STD9 20240828084942 08/28/24 08:49
ICV ICPMS140828240925-4 20240828092522-4 08/28/24 09:25
ICB ICPMS140828240939-4 20240828093928-4 08/28/24 09:39
ICVLL ICPMS140828241002-4 20240828100238-4 08/28/24 10:02
ICSA ICPMS140828241009-4 20240828100910-4 08/28/24 10:09
ICSAB ICPMS140828241012-4 20240828101221-4 08/28/24 10:12
CCV ICPMS140828241041-4 20240828104125-4 08/28/24 10:41
CCB ICPMS140828241102-4 20240828110201-4 08/28/24 11:02
BLANK R4112786-1 20240828111813 08/28/24 11:18 5 WG2351421
LCS R4112786-2 20240828112130 08/28/24 11:21 5 WG2351421
OS L1769970-04 20240828112445 08/28/24 11:24
SD R4112786-3 20240828112801 08/28/24 11:28 25 WG2351421
PS R4112786-4 20240828113118 08/28/24 11:31 5 WG2351421
MS R4112786-5 20240828113433 08/28/24 11:34 5 WG2351421
MSD R4112786-6 20240828113749 08/28/24 11:37 5 WG2351421
CCV ICPMS140828241150-2 20240828115053-2 08/28/24 11:50
CCB ICPMS140828241157-2 20240828115728-2 08/28/24 11:57
OS L1771468-10 20240828120045 08/28/24 12:00
PS R4112786-7 20240828120401 08/28/24 12:04 5 WG2351421
MS R4112786-8 20240828120716 08/28/24 12:07 5 WG2351421
MSD R4112786-9 20240828121032 08/28/24 12:10 5 WG2351421
L1766949-02 L1766949-02 20240828121348 08/28/24 12:13 5 WG2351421
EXC-2 L1770255-01 20240828122337 08/28/24 12:23 5 WG2351421
CCV ICPMS140828241233-2 20240828123319-2 08/28/24 12:33
CCB ICPMS140828241239-2 20240828123909-2 08/28/24 12:39
CCVLL ICPMS140828241323-4 20240828132343-4 08/28/24 13:23
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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13-IN ICP/MS TUNE
Lab File ID:20240828073934-4 SDG:L1770255
Instrument ID:ICPMS14 Analysis Date/Time 08/28/24 07:39
Analytical Method:6020
Element - Mass Avg. Measured Mass Avg. Peak Width Height RSD
u u %%
IN - 115 115 0.43112850 10 1.304608
PB - 206 206 0.44685770 10 1.020535
PB - 207 206.95 0.43210140 10 0.81644060
PB - 208 207.95 0.43445680 10 1.199856
MG - 24 23.95 0.47487990 10 0.86816960
MG - 25 24.95 0.475836 10 1.282403
MG - 26 25.95 0.477220 10 1.279114
CO - 59 58.95 0.46888130 10 0.76827620
BE - 9 9.05 0.42148840 10 0.866922
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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14-IN ICP/MS INTERNAL STANDARDS
RELATIVE INTENSITY
SDG:L1770255 Analytical Method:6020
Instrument ID:ICPMS14 Start Date:08/28/24 09:25
Instrument Run:082824ICPMS14 End Date:08/28/24 12:10
Client Sample ID Lab Sample ID Analysis Date Time Dilution BISMUTH (NO
HE)GERMANIUM GERMANIUM
(NO HE)
% Rec.Q % Rec.Q % Rec.Q
ICV ICPMS140828240925-
4 08/28/24 09:25 1 97.50 99.70 98.70
ICB ICPMS140828240939-
4 08/28/24 09:39 1 99.40 100 99.70
ICVLL ICPMS140828241002-4 08/28/24 10:02 1 99.10 99.80 100
ICSA ICPMS140828241009-4 08/28/24 10:09 1 89.20 93 96.50
ICSAB ICPMS140828241012-4 08/28/24 10:12 1 85.20 90.20 91.90
CCV ICPMS140828241041-4 08/28/24 10:41 1 87.70 91.30 92.50
CCB ICPMS140828241102-4 08/28/24 11:02 1 92.80 94.30 94.80
CCV ICPMS140828241150-2 08/28/24 11:50 1 90 92.60 91.60
CCB ICPMS140828241157-2 08/28/24 11:57 1 92.50 91.30 91
CCV ICPMS140828241233-2 08/28/24 12:33 1 93 95.90 94.80
CCB ICPMS140828241239-2 08/28/24 12:39 1 92.40 95.10 94.40
CCVLL ICPMS140828241323-4 08/28/24 13:23 1 90.60 94.60 93.70
OS L1769970-04 08/28/24 11:24 5 88.90 95.40 92.80
EXC-2 L1770255-01 08/28/24 12:23 5 91.30 96.70 94.50
OS L1771468-10 08/28/24 12:00 5 90.30 90.30 89.40
BLANK R4112786-1 08/28/24 11:18 5 86.80 89.10 90.10
LCS R4112786-2 08/28/24 11:21 5 87.50 91.20 91.30
SD R4112786-3 08/28/24 11:28 25 90 92.10 93
PS R4112786-4 08/28/24 11:31 5 90.50 94.20 91.80
MS R4112786-5 08/28/24 11:34 5 89.80 92.70 92.30
MSD R4112786-6 08/28/24 11:37 5 90.90 92.40 93
PS R4112786-7 08/28/24 12:04 5 92.30 91.90 93.60
MS R4112786-8 08/28/24 12:07 5 90.30 93.10 93.10
MSD R4112786-9 08/28/24 12:10 5 90.80 93.50 92.60
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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14-IN ICP/MS INTERNAL STANDARDS
RELATIVE INTENSITY
SDG:L1770255 Analytical Method:6020
Instrument ID:ICPMS14 Start Date:08/28/24 09:25
Instrument Run:082824ICPMS14 End Date:08/28/24 12:10
Client Sample ID Lab Sample ID Analysis Date Time Dilution RHODIUM SCANDIUM SCANDIUM (NO
HE)
% Rec.Q % Rec.Q % Rec.Q
ICV ICPMS140828240925-
4 08/28/24 09:25 1 97.30 97.30 98.50
ICB ICPMS140828240939-
4 08/28/24 09:39 1 100 98.70 97.50
ICVLL ICPMS140828241002-4 08/28/24 10:02 1 99.10 98.10 97.30
ICSA ICPMS140828241009-4 08/28/24 10:09 1 87.70 92.50 92.90
ICSAB ICPMS140828241012-4 08/28/24 10:12 1 84.40 90 91
CCV ICPMS140828241041-4 08/28/24 10:41 1 90.80 94.30 92.40
CCB ICPMS140828241102-4 08/28/24 11:02 1 93.50 94.60 94.60
CCV ICPMS140828241150-2 08/28/24 11:50 1 91.40 90.10 90.80
CCB ICPMS140828241157-2 08/28/24 11:57 1 91 88.20 90.70
CCV ICPMS140828241233-2 08/28/24 12:33 1 94.60 96.20 91.90
CCB ICPMS140828241239-2 08/28/24 12:39 1 93.70 93 90.70
CCVLL ICPMS140828241323-4 08/28/24 13:23 1 93.40 94.10 89.20
OS L1769970-04 08/28/24 11:24 5 90.70 92.70 89.60
EXC-2 L1770255-01 08/28/24 12:23 5 92.20 93 92
OS L1771468-10 08/28/24 12:00 5 89.60 88 87.70
BLANK R4112786-1 08/28/24 11:18 5 89.70 91.30 88.30
LCS R4112786-2 08/28/24 11:21 5 90.20 91.80 89.40
SD R4112786-3 08/28/24 11:28 25 91.30 92.50 91
PS R4112786-4 08/28/24 11:31 5 89.70 91.40 89.90
MS R4112786-5 08/28/24 11:34 5 89.90 90.40 90.50
MSD R4112786-6 08/28/24 11:37 5 90.50 90.20 90.30
PS R4112786-7 08/28/24 12:04 5 91.70 90.60 92.50
MS R4112786-8 08/28/24 12:07 5 91.80 91 90.40
MSD R4112786-9 08/28/24 12:10 5 91 91.80 90.10
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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14-IN ICP/MS INTERNAL STANDARDS
RELATIVE INTENSITY
SDG:L1770255 Analytical Method:6020
Instrument ID:ICPMS14 Start Date:08/28/24 09:25
Instrument Run:082824ICPMS14 End Date:08/28/24 12:10
Client Sample ID Lab Sample ID Analysis Date Time Dilution TELLURIUM TELLURIUM
(HIGH HE)
TELLURIUM (NO
HE)
% Rec.Q % Rec.Q % Rec.Q
ICV ICPMS140828240925-
4 08/28/24 09:25 1 97.90 97.70 98.90
ICB ICPMS140828240939-
4 08/28/24 09:39 1 98.90 99.10 98.90
ICVLL ICPMS140828241002-4 08/28/24 10:02 1 100 100 100
ICSA ICPMS140828241009-4 08/28/24 10:09 1 87.40 88.60 90.20
ICSAB ICPMS140828241012-4 08/28/24 10:12 1 83.10 86.10 86.20
CCV ICPMS140828241041-4 08/28/24 10:41 1 90.80 94.40 91.30
CCB ICPMS140828241102-4 08/28/24 11:02 1 92.20 94.80 93.90
CCV ICPMS140828241150-2 08/28/24 11:50 1 91.90 93.30 92.20
CCB ICPMS140828241157-2 08/28/24 11:57 1 90.60 92.40 91.50
CCV ICPMS140828241233-2 08/28/24 12:33 1 97.20 97.20 94.90
CCB ICPMS140828241239-2 08/28/24 12:39 1 93.20 94.70 93.30
CCVLL ICPMS140828241323-4 08/28/24 13:23 1 95 96 93.60
OS L1769970-04 08/28/24 11:24 5 89.50 90.90 89.40
EXC-2 L1770255-01 08/28/24 12:23 5 93.20 94.10 92.40
OS L1771468-10 08/28/24 12:00 5 89.60 91.50 90
BLANK R4112786-1 08/28/24 11:18 5 88.30 89.90 86.90
LCS R4112786-2 08/28/24 11:21 5 89.40 91.20 89.30
SD R4112786-3 08/28/24 11:28 25 91.20 92.70 91.20
PS R4112786-4 08/28/24 11:31 5 88.70 90.80 89.60
MS R4112786-5 08/28/24 11:34 5 88.80 90.90 90.10
MSD R4112786-6 08/28/24 11:37 5 89.30 91 90.50
PS R4112786-7 08/28/24 12:04 5 92.60 93.50 92.10
MS R4112786-8 08/28/24 12:07 5 91.90 92.90 91.90
MSD R4112786-9 08/28/24 12:10 5 92.20 93.70 92.20
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
ARSENIC 0.0010 .001008386 101 0.0020 .002025631 101
LEAD 0.0010 .001067216 107 0.0020 .002006619 100
File ID: 20240828082843 20240828083214
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1770255 10/28/24 13:09 46 of 53
15-IN INITIAL CALIBRATION RECOVERY
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
ARSENIC 0.01 .010118 101 0.05 .05019874 100
LEAD 0.01 .0098836 98.80 0.05 .04859984 97.20
File ID: 20240828083545 20240828083917
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
ARSENIC 0.10 .09909218 99.10 0.20 .198911 99.50
LEAD 0.10 .09932294 99.30 0.20 .2024197 101
File ID: 20240828084248 20240828084617
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Analyte Std Conc Result Rec.
mg/l mg/l %
ARSENIC 0.40 .4007435 100
LEAD 0.40 .3991371 99.80
File ID: 20240828084942
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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16B-IN ICP/MS INITIAL
CALIBRATION
SDG:L1770255 Calibration (begin) date/time:08/28/24 08:25
Instrument ID:ICPMS14 Calibration (end) date/time:08/28/24 08:49
Analytical Method:6020 Analytical Run:082824ICPMS14
Analyte Mass Cal. Type Weightage Corr.Slope Incpt
ARSENIC 75 0 5 0.999991 15.30698 0.00034
LEAD 208 0 5 0.999968 1.358432 0.000175
Calibration Type
0 = Linear Regression
Weightage
5 = None
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
The information below is designed to better explain the various terms used in your report of analytical results from the Laboratory. This is not
intended as a comprehensive explanation, and if you have additional questions please contact your project representative.
Results Disclaimer - Information that may be provided by the customer, and contained within this report, include Permit Limits, Project Name,
Sample ID, Sample Matrix, Sample Preservation, Field Blanks, Field Spikes, Field Duplicates, On-Site Data, Sampling Collection Dates/Times, and
Sampling Location. Results relate to the accuracy of this information provided, and as the samples are received.
Abbreviations and Definitions
Corr.Correlation Coefficient.
(dry)Results are reported based on the dry weight of the sample. [this will only be present on a dry report basis for soils].
Incpt Intercept.
Mass Mass of parameter.
MDL Method Detection Limit.
MDL (dry)Method Detection Limit.
RDL Reported Detection Limit.
RDL (dry)Reported Detection Limit.
Rec.Recovery.
RPD Relative Percent Difference.
RSD Relative Standard Deviation.
SDG Sample Delivery Group.
Analyte The name of the particular compound or analysis performed. Some Analyses and Methods will have multiple analytes
reported.
Dilution
If the sample matrix contains an interfering material, the sample preparation volume or weight values differ from the
standard, or if concentrations of analytes in the sample are higher than the highest limit of concentration that the
laboratory can accurately report, the sample may be diluted for analysis. If a value different than 1 is used in this field, the
result reported has already been corrected for this factor.
Limits
These are the target % recovery ranges or % difference value that the laboratory has historically determined as normal
for the method and analyte being reported. Successful QC Sample analysis will target all analytes recovered or
duplicated within these ranges.
Qualifier
This column provides a letter and/or number designation that corresponds to additional information concerning the result
reported. If a Qualifier is present, a definition per Qualifier is provided within the Glossary and Definitions page and
potentially a discussion of possible implications of the Qualifier in the Case Narrative if applicable.
Result
The actual analytical final result (corrected for any sample specific characteristics) reported for your sample. If there was
no measurable result returned for a specific analyte, the result in this column may state “ND” (Not Detected) or “BDL”
(Below Detectable Levels). The information in the results column should always be accompanied by either an MDL
(Method Detection Limit) or RDL (Reporting Detection Limit) that defines the lowest value that the laboratory could detect
or report for this analyte.
Slope Slope of calibration curve.
Uncertainty
(Radiochemistry)Confidence level of 2 sigma.
Wavelength Wavelength of parameter.
Case Narrative (Cn)
A brief discussion about the included sample results, including a discussion of any non-conformances to protocol
observed either at sample receipt by the laboratory from the field or during the analytical process. If present, there will
be a section in the Case Narrative to discuss the meaning of any data qualifiers used in the report.
Quality Control
Summary (Qc)
This section of the report includes the results of the laboratory quality control analyses required by procedure or
analytical methods to assist in evaluating the validity of the results reported for your samples. These analyses are not
being performed on your samples typically, but on laboratory generated material.
Sample Chain of
Custody (Sc)
This is the document created in the field when your samples were initially collected. This is used to verify the time and
date of collection, the person collecting the samples, and the analyses that the laboratory is requested to perform. This
chain of custody also documents all persons (excluding commercial shippers) that have had control or possession of the
samples from the time of collection until delivery to the laboratory for analysis.
Sample Results (Sr)
This section of your report will provide the results of all testing performed on your samples. These results are provided
by sample ID and are separated by the analyses performed on each sample. The header line of each analysis section for
each sample will provide the name and method number for the analysis reported.
Sample Summary (Ss)This section of the Analytical Report defines the specific analyses performed for each sample ID, including the dates and
times of preparation and/or analysis.
Qualifier Description
The remainder of this page intentionally left blank, there are no qualifiers applied to this SDG.
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Pace Analytical National 12065 Lebanon Rd Mount Juliet, TN 37122
Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN000032021-1
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹TN00003
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹DW21704
Georgia NELAP North Carolina ³41
Georgia ¹923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶KY90010 South Carolina 84004002
Kentucky ²16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴2006
Louisiana LA018 Texas T104704245-20-18
Maine TN00003 Texas ⁵LAB0152
Maryland 324 Utah TN000032021-11
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 110033
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 998093910
Montana CERT0086 Wyoming A2LA
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS

¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace Analytical.
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ANALYTICAL REPORT
September 04, 2024
Wasatch Environmental
Sample Delivery Group:L1771052
Samples Received:08/23/2024
Project Number:
Description:Sommers Emergency Response Split
Site:SOMMERS AUTO
Report To:Blake Downey, P.G.
2410 West California Avenue
Salt Lake City, UT 84104
Entire Report Reviewed By:
September 04, 2024
[Preliminary Report]
John Hawkins
Project Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be
reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace
Analytical National is performed per guidance provided in laboratory standard operating procedures ENV-SOP-MTJL-0067 and
ENV-SOP-MTJL-0068. Where sampling conducted by the customer, results relate to the accuracy of the information provided,
and as the samples are received.
Pace Analytical National
12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 mydata.pacelabs.com
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September 04, 2024
John Hawkins
Project Manager
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TABLE OF CONTENTSTABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 4
Cn: Case Narrative 5
Su: Summary Results 6
2540 G-2011 Total Solids 6
Sample Result Inorganic Analysis Data Sheet 7
L1771052-01 08/27/24 16:33 LOGBAL1 7
BLANK(R4112694-1) WG2351250 08/27/24 16:33 LOGBAL1 8
DUP(R4112694-3) WG2351250 08/27/24 16:33 LOGBAL1 9
LCS(R4112694-2) WG2351250 08/27/24 16:33 LOGBAL1 10
Blank 11
LOGBAL1 WG2351250 11
Laboratory Duplicate 12
WG2351250 DUP(R4112694-3) 12
Laboratory Control Sample / Duplicate 13
WG2351250 LCS(R4112694-2) 13
Detection Limit Summary 14
2540 G-2011 - Solid 14
Analysis Log 15
LOGBAL1 WG2351250 15
6020 Metals (ICPMS) 16
Sample Result Inorganic Analysis Data Sheet 17
L1771052-01 09/03/24 18:56 ICPMS9 17
BLANK(R4115153-1) WG2352159 09/03/24 18:49 ICPMS9 18
LCS(R4115153-2) WG2352159 09/03/24 18:52 ICPMS9 19
MS(R4115153-5) WG2352159 09/03/24 19:06 ICPMS9 20
MSD(R4115153-6) WG2352159 09/03/24 19:09 ICPMS9 21
PS(R4115153-4) WG2352159 09/03/24 19:02 ICPMS9 22
SD(R4115153-3) WG2352159 09/03/24 18:59 ICPMS9 23
Calibration Verification 24
ICPMS9 090324ICPMS9 24
Blank 26
ICPMS9 090324ICPMS9 26
ICP Interference Check Sample 27
ICPMS9 09/03/24 12:38 27
Matrix Spike / Duplicate 28
WG2352159 MS(R4115153-5) MSD(R4115153-6) 28
Post Digestion Spike 29
WG2352159 PS(R4115153-4) 29
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8 Sc
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Laboratory Control Sample / Duplicate 30
WG2352159 LCS(R4115153-2) 30
Serial Dilution 31
WG2352159 SD(R4115153-3) 31
Detection Limit Summary 32
6020 - Solid 32
Linear Dynamic Range 33
ICPMS9 02/13/24 09:54 33
Internal Standard Association 34
ICPMS9 09/03/24 10:01 34
Analysis Log 35
ICPMS9 090324ICPMS9 09/03/24 10:27 35
ICP/MS Tune 36
ICPMS9 090324ICPMS9 09/03/24 10:01 36
Internal Standard Relative Intensity 37
ICPMS9 090324ICPMS9 37
Initial Calibration Recovery 39
ICPMS9 090324ICPMS9 09/03/24 10:27 39
ICPMS9 090324ICPMS9 09/03/24 10:27 43
ICP/MS Initial Calibration 47
ICPMS9 090324ICPMS9 09/03/24 10:27 47
ICPMS9 090324ICPMS9 09/03/24 10:27 48
Gl: Glossary of Terms 49
Al: Accreditations & Locations 50
Sc: Sample Chain of Custody 51
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
EXC-3 L1771052-01 Solid Jacob Scott 08/22/24 11:02 08/23/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2351250 1 08/27/24 16:18 08/27/24 16:33 KDW Mt. Juliet, TN
Metals (ICPMS) by Method 6020 WG2352159 5 09/02/24 22:59 09/03/24 18:56 SJM Mt. Juliet, TN
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CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the
appropriate preservatives, and within method specified holding times, unless qualified or notated within
the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples
have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control
are within established criteria except where addressed in this case narrative, a non-conformance form
or properly qualified within the sample results. By my digital signature below, I affirm to the best of my
knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the
quality of the data have been identified by the laboratory, and no information or data have been
knowingly withheld that would affect the quality of the data.
[Preliminary Report]
John Hawkins
Project Manager
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John Hawkins
Project Manager
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2540 G-2011 Total Solids
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET EXC-3
Lab Sample ID:L1771052-01 SDG:L1771052
Client Sample ID:EXC-3 Collected Date/Time:08/22/24 11:02
Lab File ID:07 Received Date/Time:08/23/24 08:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/27/24 16:18
Analytical Batch:WG2351250 Analysis Date/Time:08/27/24 16:33
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:12.053 g
Total Solids (%):86.5 Final Wt/Vol:10.605 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 86.5
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112694-1
Lab Sample ID:R4112694-1 SDG:L1771052
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:01 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/27/24 16:15
Analytical Batch:WG2351250 Analysis Date/Time:08/27/24 16:33
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:1.296 g
Total Solids (%):_______________Final Wt/Vol:1.297 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 0.00100
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112694-3
Lab Sample ID:R4112694-3 SDG:L1771052
Client Sample ID:DUP Collected Date/Time:08/21/24 15:50
Lab File ID:02 Received Date/Time:08/24/24 09:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/27/24 16:15
Analytical Batch:WG2351250 Analysis Date/Time:08/27/24 16:33
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:8.224 g
Total Solids (%):89.9 Final Wt/Vol:7.489 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 89.4
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112694-2
Lab Sample ID:R4112694-2 SDG:L1771052
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:03 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/27/24 16:15
Analytical Batch:WG2351250 Analysis Date/Time:08/27/24 16:33
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:11.315 g
Total Solids (%):_______________Final Wt/Vol:6.316 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 50.0
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3-IN BLANKS
SDG:L1771052 Calibration (begin) date/time:_______________
Instrument ID:LOGBAL1 Calibration (end) date/time:_______________
Analytical Method:2540 G-2011 Analytical Run:WG2351250
Sample ID:BLANK Result BLANK
Qual
File ID:01
Analyte %
TOTAL SOLIDS 0.00100
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6-IN DUPLICATES SAMPLE NO.:
L1771052-01 R4112694-3
DUP Sample / File ID:R4112694-3 / 02 SDG:L1771052
OS Sample / File ID:L1771153-01 / 09 Analytical Batch:WG2351250
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte OS
Result
DUP
Result RPD RPD
Limits
%%%%
Total Solids 89.9 89.4 0.659 10
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
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7-IN LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4112694-2
RECOVERY _______________
L1771052-01
LCS Sample / File ID:R4112694-2 / 03 SDG:L1771052
LCSD Sample / File ID:_______________Analytical Batch:WG2351250
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD
Rec.Rec. Limits RPD RPD Limits
%%%%%%%
Total Solids 50.0 50.0 100 90.0 - 110
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
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9-IN DETECTION LIMIT SUMMARY
Lab Sample IDs:L1771052-01 Analytical Method:2540 G-2011
Matrix:Solid Prep Method:SM 2540 G
Analyte CAS Wavelength Mass MDL RDL
%%
Total Solids TSOLIDS
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12-IN ANALYSIS LOG
SDG:L1771052 Analytical Method:2540 G-2011
Instrument ID:LOGBAL1 Calibration Start Date:_______________
Analytical Run:WG2351250 Calibration End Date:_______________
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
BLANK R4112694-1 01 08/27/24 16:33 1 WG2351250
DUP R4112694-3 02 08/27/24 16:33 1 WG2351250
LCS R4112694-2 03 08/27/24 16:33 1 WG2351250
OS L1771153-01 09 08/27/24 16:33
EXC-3 L1771052-01 07 08/27/24 16:33 1 WG2351250
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6020 Metals (ICPMS)
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET EXC-3
Lab Sample ID:L1771052-01 SDG:L1771052
Client Sample ID:EXC-3 Collected Date/Time:08/22/24 11:02
Lab File ID:20240903185607 Received Date/Time:08/23/24 08:00
Instrument ID:ICPMS9 Preparation Date/Time:09/02/24 22:59
Analytical Batch:WG2352159 Analysis Date/Time:09/03/24 18:56
Dilution Factor:5 Prep Method:3050B
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.49 g
Total Solids (%):86.5 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 15.7 0.116 1.16
Lead 7439-92-1 104 J3 J5 0.114 2.31
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115153-1
Lab Sample ID:R4115153-1 SDG:L1771052
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:20240903184923 Received Date/Time:_______________
Instrument ID:ICPMS9 Preparation Date/Time:09/02/24 23:14
Analytical Batch:WG2352159 Analysis Date/Time:09/03/24 18:49
Dilution Factor:5 Prep Method:3050B
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.48 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 U 0.100 1.00
Lead 7439-92-1 0.138 J 0.0990 2.00
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115153-2
Lab Sample ID:R4115153-2 SDG:L1771052
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:20240903185245 Received Date/Time:_______________
Instrument ID:ICPMS9 Preparation Date/Time:09/02/24 23:14
Analytical Batch:WG2352159 Analysis Date/Time:09/03/24 18:52
Dilution Factor:5 Prep Method:3050B
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.50 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 101 0.100 1.00
Lead 7439-92-1 101 0.0990 2.00
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115153-5
Lab Sample ID:R4115153-5 SDG:L1771052
Client Sample ID:MS Collected Date/Time:08/22/24 11:02
Lab File ID:20240903190608 Received Date/Time:08/23/24 08:00
Instrument ID:ICPMS9 Preparation Date/Time:09/02/24 22:59
Analytical Batch:WG2352159 Analysis Date/Time:09/03/24 19:06
Dilution Factor:5 Prep Method:3050B
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.48 g
Total Solids (%):86.5 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 138 0.116 1.16
Lead 7439-92-1 325 J5 0.114 2.31
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115153-6
Lab Sample ID:R4115153-6 SDG:L1771052
Client Sample ID:MSD Collected Date/Time:08/22/24 11:02
Lab File ID:20240903190928 Received Date/Time:08/23/24 08:00
Instrument ID:ICPMS9 Preparation Date/Time:09/02/24 22:59
Analytical Batch:WG2352159 Analysis Date/Time:09/03/24 19:09
Dilution Factor:5 Prep Method:3050B
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.48 g
Total Solids (%):86.5 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 139 0.116 1.16
Lead 7439-92-1 250 J3 J5 0.114 2.31
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115153-4
Lab Sample ID:R4115153-4 SDG:L1771052
Client Sample ID:PS Collected Date/Time:08/22/24 11:02
Lab File ID:20240903190249 Received Date/Time:08/23/24 08:00
Instrument ID:ICPMS9 Preparation Date/Time:09/02/24 22:59
Analytical Batch:WG2352159 Analysis Date/Time:09/03/24 19:02
Dilution Factor:5 Prep Method:3050B
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.49 g
Total Solids (%):86.5 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 142 0.116 1.16
Lead 7439-92-1 230 0.114 2.31
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115153-3
Lab Sample ID:R4115153-3 SDG:L1771052
Client Sample ID:SD Collected Date/Time:08/22/24 11:02
Lab File ID:20240903185927 Received Date/Time:08/23/24 08:00
Instrument ID:ICPMS9 Preparation Date/Time:09/02/24 22:59
Analytical Batch:WG2352159 Analysis Date/Time:09/03/24 18:59
Dilution Factor:25 Prep Method:3050B
Analytical Method:6020 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.49 g
Total Solids (%):86.5 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Arsenic 7440-38-2 16.3 0.578 5.78
Lead 7439-92-1 111 0.572 11.6
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2-IN CALIBRATION VERIFICATION
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Concentration Units:mg/l
ICV ICVLL CCV
Sample ID:ICPMS90903241147-2 ICPMS90903241233-2 ICPMS90903241819-2
Analyte True Found %R %RSD True Found %R %RSD True Found %R %RSD
ARSENIC 0.10 0.1004029 100 0.440000 0.0010 0.000941709 94.2
0 5.300000 0.10 0.1022332 102 2.300000
LEAD 0.10 0.0999316 99.9
0 0.560000 0.0010 0.001037919 104 10.700000 0.10 0.102173 102 0.800000
ICV Limits:90 - 110 ICVLL Limits:50 - 150 CCV Limits:90 - 110
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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2-IN CALIBRATION VERIFICATION
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Concentration Units:mg/l
CCV
Sample ID:ICPMS90903241922
Analyte True Found %R %RSD
ARSENIC 0.10 0.1029529 103 1.800000
LEAD 0.10 0.1034118 103 0.180000
ICV Limits:90 - 110 ICVLL Limits:50 - 150 CCV Limits:90 - 110
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Sample ID:ICB Result ICB Qual CCB Result CCB Qual BLANK Result BLANK
Qual CCB Result CCB Qual
File ID:20240903115836-2 20240903182253-2 20240903184923 20240903192610
Analyte mg/l mg/l mg/kg mg/l
ARSENIC 0.000003769 U 0.000185088 U U 0.000196255 U
LEAD 0.000011372 U 0.000031828 U 0.138 J 0.000420274 U
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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4-IN INTERFERENCE CHECK SAMPLE
SDG:L1771052 Analytical Method:6020
Instrument ID:ICPMS9 Date:09/03/24 12:38
Instrument Run:090324ICPMS9
Analyte True Found True Found
ICSA ICSA ICSA ICSAB ICSAB ICSAB
mg/l mg/l % Rec.mg/l mg/l % Rec.
ALUMINUM 100 97.2185 97.20 100 96.27542 96.30
ANTIMONY 0 0.00009312 0.02 0.02046163 102
ARSENIC 0 0.000044647 0.02 0.0189191 94.60
BARIUM 0 0.000503871 0.02 0.01964671 98.20
BERYLLIUM 0 -0.000021739 0.02 0.01903929 95.20
BISMUTH 661347.3 94.20 667965.6 95.10
BORON 0 0.002138474 0.02 0.02050474 103
CADMIUM 0 0.000070241 0.02 0.02055186 103
CALCIUM 100 96.0237 96 100 94.32823 94.30
CHROMIUM 0 0.001017533 0.02 0.02033793 102
COBALT 0 0.000100856 0.02 0.02022782 101
COPPER 0 0.000974615 0.02 0.02086334 104
GERMANIUM 298674.2 96.60 304619.1 98.50
IRON 100 105.4054 105 100 102.7378 103
LEAD 0 0.000049377 0.02 0.01992834 99.60
LITHIUM 0 0.000387007 0 0.000521541
MAGNESIUM 100 97.49015 97.50 100 96.36149 96.40
MANGANESE 0 0.00030915 0.02 0.02037971 102
MOLYBDENUM 2 2.03995 102 2 2.027771 101
NICKEL 0 0.00037312 0.02 0.02007371 100
POTASSIUM 100 98.58453 98.60 100 98.15161 98.20
RHODIUM 319465.4 94.10 321131.8 94.60
SCANDIUM 8483992 97.60 8700208 100
SELENIUM 0 -0.000128591 0.02 0.01900839 95
SILVER 0 -0.000005294 0.02 0.01980927 99
SODIUM 100 100.1849 100 100 101.5844 102
STRONTIUM 0 0.000718299 0.02 0.02069339 103
TELLURIUM 51633.97 92.30 51474.18 92
THALLIUM 0 0.000021202 0.02 0.01961137 98.10
THORIUM 0 0.000049192 0.02 0.02000608 100
TIN 0 0.000053212 0.02 0.01855596 92.80
TITANIUM 2 1.976071 98.80 2 1.953006 97.70
URANIUM 0 0.000007106 0.02 0.01991643 99.60
VANADIUM 0 0.000012866 0.02 0.01973962 98.70
ZINC 0 0.001107767 0.02 0.01993898 99.70
ICSA Limits:80 - 120 ICSAB Limits:80 - 120
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5A-IN MATRIX SPIKE /SAMPLE NO.:
MATRIX SPIKE DUPLICATE RECOVERY R4115153-5
L1771052-01 R4115153-6
MS Sample / File ID:R4115153-5 / 20240903190608 SDG:L1771052
MSD Sample / File ID:R4115153-6 / 20240903190928 Analytical Batch:WG2352159
OS Sample / File ID:L1771052-01 / 20240903185607 Matrix:Solid
Instrument ID:ICPMS9
Analytical Method:6020
Analyte
Spike
Amount
(dry)
OS
Result
(dry)
MS
Result
(dry)
MSD
Result
(dry)
MS Rec.MSD
Rec.Dilution Rec. Limits RPD RPD Limits
mg/kg mg/kg mg/kg mg/kg %%%%%
Arsenic 116 15.7 138 139 106 107 5 75.0 - 125 0.786 20
Lead 116 104 325 250 190*126*5 75.0 - 125 25.9*20
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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5B-IN POST-DIGESTION / DISTILLATION SPIKE SAMPLE NO.:
SAMPLE RECOVERY R4115153-4
L1771052-01
PS Sample / File ID:R4115153-4 / 20240903190249 SDG:L1771052
OS Sample / File ID:L1771052-01 / 20240903185607 Analytical Batch:WG2352159
Instrument ID:ICPMS9 Dilution Factor:5
Analytical Method:6020 Matrix:Solid
Analyte
Spike
Amount
(dry)
OS
Result
(dry)
PD
Result
(dry)
DS
Result
(dry)
PD Rec.DS Rec.Dilution Rec.
Limits RPD RPD
Limits
mg/kg mg/kg mg/kg %%%mg/kg mg/kg
Arsenic 116 15.7 142 109 5 80.0 -
120
Lead 116 104 230 109 5 80.0 -
120
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7-IN LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4115153-2
RECOVERY _______________
L1771052-01
LCS Sample / File ID:R4115153-2 / 20240903185245 SDG:L1771052
LCSD Sample / File ID:_______________Analytical Batch:WG2352159
Instrument ID:ICPMS9 Dilution Factor:5
Analytical Method:6020 Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD
Rec.Rec. Limits RPD RPD Limits
mg/kg mg/kg %%%%%
Arsenic 100 101 101 80.0 - 120
Lead 100 101 101 80.0 - 120
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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8-IN ICP AND ICP/MS SAMPLE NO.:
SERIAL DILUTIONS R4115153-3
L1771052-01
SD Sample / File ID:R4115153-3 / 20240903185927 SDG:L1771052
OS Sample / File ID:L1771052-01 / 20240903185607 Analytical Batch:WG2352159
Lab File ID:20240903185927 Dilution Factor:25
Instrument ID:ICPMS9 Matrix:Solid
Analytical Method:6020
Analyte
OS
Result
(dry)
SD
Result
(dry)
RPD RPD
Limits
mg/kg mg/kg %%
Arsenic 15.7 16.3 3.71 10
Lead 104 111 5.85 10
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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9-IN DETECTION LIMIT SUMMARY
Lab Sample IDs:L1771052-01 Analytical Method:6020
Matrix:Solid Prep Method:3050B
Analyte CAS Wavelength Mass MDL RDL
mg/kg mg/kg
Arsenic 7440-38-2 75 0.02 0.20
Lead 7439-92-1 208 0.0198 0.40
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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10C-IN LINEAR DYNAMIC RANGE
SDG:L1771052 Analytical Method:6020
Instrument ID:ICPMS9 Date:02/13/24 09:54
Analyte LDR
ppm
ALUMINUM 100
ANTIMONY 1
ARSENIC 10
BARIUM 2
BERYLLIUM 5
BORON 2
CADMIUM 10
CALCIUM 1000
CHROMIUM 10
COBALT 10
COPPER 0.40
IRON 100
LEAD 10
LITHIUM 2
MAGNESIUM 1000
MANGANESE 10
MOLYBDENUM 1
NICKEL 10
POTASSIUM 1000
SELENIUM 0.20
SILVER 0.20
SODIUM 1000
STRONTIUM 2
THALLIUM 10
THORIUM 0.20
TIN 2
TITANIUM 10
URANIUM 1
VANADIUM 2
ZINC 10
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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11-IN INTERNAL STANDARD ASSOCIATION
SDG:L1771052 Analytical Method:6020
Instrument ID:ICPMS9 Analysis Date:09/03/24 10:01
Instrument Run:090324ICPMS9
Analyte Assoc. Internal Standard 1
ARSENIC - 75 GERMANIUM - 74
LEAD - 208 BISMUTH - 209
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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12-IN ANALYSIS LOG
SDG:L1771052 Analytical Method:6020
Instrument ID:ICPMS9 Calibration Start Date:09/03/24 10:27
Analytical Run:090324ICPMS9 Calibration End Date:09/03/24 10:52
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
CALBLK ICPMS90903241023 20240903102339 09/03/24 10:23
CAL STD3 20240903103101 09/03/24 10:31
CAL STD4 20240903103439 09/03/24 10:34
CAL STD5 20240903103816 09/03/24 10:38
CAL STD6 20240903104153 09/03/24 10:41
CAL STD7 20240903104531 09/03/24 10:45
CAL STD8 20240903104909 09/03/24 10:49
CAL STD9 20240903105245 09/03/24 10:52
ICV ICPMS90903241147-2 20240903114714-2 09/03/24 11:47
ICB ICPMS90903241158-2 20240903115836-2 09/03/24 11:58
ICVLL ICPMS90903241233-2 20240903123344-2 09/03/24 12:33
ICSA ICPMS90903241238-2 20240903123852-2 09/03/24 12:38
ICSAB ICPMS90903241242-2 20240903124212-2 09/03/24 12:42
CCV ICPMS90903241819-2 20240903181932-2 09/03/24 18:19
CCB ICPMS90903241822-2 20240903182253-2 09/03/24 18:22
BLANK R4115153-1 20240903184923 09/03/24 18:49 5 WG2352159
LCS R4115153-2 20240903185245 09/03/24 18:52 5 WG2352159
EXC-3 L1771052-01 20240903185607 09/03/24 18:56 5 WG2352159
SD R4115153-3 20240903185927 09/03/24 18:59 25 WG2352159
PS R4115153-4 20240903190249 09/03/24 19:02 5 WG2352159
MS R4115153-5 20240903190608 09/03/24 19:06 5 WG2352159
MSD R4115153-6 20240903190928 09/03/24 19:09 5 WG2352159
L1771268-01 L1771268-01 20240903191248 09/03/24 19:12 5 WG2352159
L1771762-01 L1771762-01 20240903191607 09/03/24 19:16 5 WG2352159
CCV ICPMS90903241922 20240903192249 09/03/24 19:22
CCB ICPMS90903241926 20240903192610 09/03/24 19:26
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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13-IN ICP/MS TUNE
Lab File ID:20240903100128-2 SDG:L1771052
Instrument ID:ICPMS9 Analysis Date/Time 09/03/24 10:01
Analytical Method:6020
Element - Mass Avg. Measured Mass Avg. Peak Width Height RSD
u u %%
IN - 115 115 0.41467630 10 0.30333350
PB - 206 206 0.45327090 10 0.72891240
PB - 207 207 0.43000270 10 0.95717690
PB - 208 208 0.47343960 10 0.29726970
MG - 24 23.95 0.48290120 10 0.54112110
MG - 25 24.95 0.46295170 10 0.48228310
MG - 26 25.95 0.47734740 10 0.65791170
CO - 59 58.95 0.45538740 10 0.43082330
BE - 9 9 0.46528470 10 0.80948210
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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14-IN ICP/MS INTERNAL STANDARDS
RELATIVE INTENSITY
SDG:L1771052 Analytical Method:6020
Instrument ID:ICPMS9 Start Date:09/03/24 11:47
Instrument Run:090324ICPMS9 End Date:09/03/24 19:09
Client Sample ID Lab Sample ID Analysis Date Time Dilution BISMUTH GERMANIUM RHODIUM
% Rec.Q % Rec.Q % Rec.Q
ICV ICPMS90903241147-2 09/03/24 11:47 1 96.60 98.30 97.40
ICB ICPMS90903241158-2 09/03/24 11:58 1 100 96.20 97.30
ICVLL ICPMS90903241233-2 09/03/24 12:33 1 99 97.60 98.40
ICSA ICPMS90903241238-2 09/03/24 12:38 1 94.20 96.60 94.10
ICSAB ICPMS90903241242-2 09/03/24 12:42 1 95.10 98.50 94.60
CCV ICPMS90903241819-2 09/03/24 18:19 1 89.40 97 96.30
CCB ICPMS90903241822-2 09/03/24 18:22 1 94 97.30 98.70
CCV ICPMS90903241922 09/03/24 19:22 1 90.70 98.20 97.10
CCB ICPMS90903241926 09/03/24 19:26 1 91.90 96.70 96.40
EXC-3 L1771052-01 09/03/24 18:56 5 91.40 91.80 91.80
BLANK R4115153-1 09/03/24 18:49 5 92.70 91.30 92.50
LCS R4115153-2 09/03/24 18:52 5 91.40 91.30 91.90
SD R4115153-3 09/03/24 18:59 25 92.10 94 93.70
PS R4115153-4 09/03/24 19:02 5 89.90 92 91.20
MS R4115153-5 09/03/24 19:06 5 89.50 92.20 91.70
MSD R4115153-6 09/03/24 19:09 5 89.80 93 92.50
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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14-IN ICP/MS INTERNAL STANDARDS
RELATIVE INTENSITY
SDG:L1771052 Analytical Method:6020
Instrument ID:ICPMS9 Start Date:09/03/24 11:47
Instrument Run:090324ICPMS9 End Date:09/03/24 19:09
Client Sample ID Lab Sample ID Analysis Date Time Dilution SCANDIUM TELLURIUM
% Rec.Q % Rec.Q
ICV ICPMS90903241147-2 09/03/24 11:47 1 98.10 97.70
ICB ICPMS90903241158-2 09/03/24 11:58 1 98.80 94.40
ICVLL ICPMS90903241233-2 09/03/24 12:33 1 99.90 96.10
ICSA ICPMS90903241238-2 09/03/24 12:38 1 97.60 92.30
ICSAB ICPMS90903241242-2 09/03/24 12:42 1 100 92
CCV ICPMS90903241819-2 09/03/24 18:19 1 102 94.50
CCB ICPMS90903241822-2 09/03/24 18:22 1 100 93
CCV ICPMS90903241922 09/03/24 19:22 1 99.20 94.20
CCB ICPMS90903241926 09/03/24 19:26 1 99.20 91.30
EXC-3 L1771052-01 09/03/24 18:56 5 96.70 87.10
BLANK R4115153-1 09/03/24 18:49 5 95.70 86.60
LCS R4115153-2 09/03/24 18:52 5 95.70 86.90
SD R4115153-3 09/03/24 18:59 25 98 89.90
PS R4115153-4 09/03/24 19:02 5 95.80 87.60
MS R4115153-5 09/03/24 19:06 5 96.40 86.90
MSD R4115153-6 09/03/24 19:09 5 96.40 88.20
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
ARSENIC 0.0010 .001070127 107 0.0020 .001893552 94.70
File ID: 20240903103101 20240903103439
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
ARSENIC 0.01 .01024802 102 0.05 .05094347 102
File ID: 20240903103816 20240903104153
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
ARSENIC 0.10 .1004601 100 0.20 .1995957 99.80
File ID: 20240903104531 20240903104909
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Std Conc Result Rec.
mg/l mg/l %
ARSENIC 0.40 .3999634 100
File ID: 20240903105245
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
LEAD 0.0010 .000962646 96.30 0.0020 .002029374 101
File ID: 20240903103101 20240903103439
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
LEAD 0.01 .00980698 98.10 0.05 .05063015 101
File ID: 20240903103816 20240903104153
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
LEAD 0.10 .1015711 102 0.20 .201623 101
File ID: 20240903104531 20240903104909
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Std Conc Result Rec.
mg/l mg/l %
LEAD 0.40 .3987217 99.70
File ID: 20240903105245
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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16B-IN ICP/MS INITIAL
CALIBRATION
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Mass Cal. Type Weightage Corr.Slope Incpt
ARSENIC 75 0 5 0.999996 0.120937 0.000026
Calibration Type
0 = Linear Regression
Weightage
5 = None
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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16B-IN ICP/MS INITIAL
CALIBRATION
SDG:L1771052 Calibration (begin) date/time:09/03/24 10:27
Instrument ID:ICPMS9 Calibration (end) date/time:09/03/24 10:52
Analytical Method:6020 Analytical Run:090324ICPMS9
Analyte Mass Cal. Type Weightage Corr.Slope Incpt
LEAD 208 0 5 0.999978 2.195442 0.000228
Calibration Type
0 = Linear Regression
Weightage
5 = None
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
The information below is designed to better explain the various terms used in your report of analytical results from the Laboratory. This is not
intended as a comprehensive explanation, and if you have additional questions please contact your project representative.
Results Disclaimer - Information that may be provided by the customer, and contained within this report, include Permit Limits, Project Name,
Sample ID, Sample Matrix, Sample Preservation, Field Blanks, Field Spikes, Field Duplicates, On-Site Data, Sampling Collection Dates/Times, and
Sampling Location. Results relate to the accuracy of this information provided, and as the samples are received.
Abbreviations and Definitions
Corr.Correlation Coefficient.
(dry)Results are reported based on the dry weight of the sample. [this will only be present on a dry report basis for soils].
Incpt Intercept.
Mass Mass of parameter.
MDL Method Detection Limit.
MDL (dry)Method Detection Limit.
RDL Reported Detection Limit.
RDL (dry)Reported Detection Limit.
Rec.Recovery.
RPD Relative Percent Difference.
RSD Relative Standard Deviation.
SDG Sample Delivery Group.
Analyte The name of the particular compound or analysis performed. Some Analyses and Methods will have multiple analytes
reported.
Dilution
If the sample matrix contains an interfering material, the sample preparation volume or weight values differ from the
standard, or if concentrations of analytes in the sample are higher than the highest limit of concentration that the
laboratory can accurately report, the sample may be diluted for analysis. If a value different than 1 is used in this field, the
result reported has already been corrected for this factor.
Limits
These are the target % recovery ranges or % difference value that the laboratory has historically determined as normal
for the method and analyte being reported. Successful QC Sample analysis will target all analytes recovered or
duplicated within these ranges.
Qualifier
This column provides a letter and/or number designation that corresponds to additional information concerning the result
reported. If a Qualifier is present, a definition per Qualifier is provided within the Glossary and Definitions page and
potentially a discussion of possible implications of the Qualifier in the Case Narrative if applicable.
Result
The actual analytical final result (corrected for any sample specific characteristics) reported for your sample. If there was
no measurable result returned for a specific analyte, the result in this column may state “ND” (Not Detected) or “BDL”
(Below Detectable Levels). The information in the results column should always be accompanied by either an MDL
(Method Detection Limit) or RDL (Reporting Detection Limit) that defines the lowest value that the laboratory could detect
or report for this analyte.
Slope Slope of calibration curve.
Uncertainty
(Radiochemistry)Confidence level of 2 sigma.
Wavelength Wavelength of parameter.
Case Narrative (Cn)
A brief discussion about the included sample results, including a discussion of any non-conformances to protocol
observed either at sample receipt by the laboratory from the field or during the analytical process. If present, there will
be a section in the Case Narrative to discuss the meaning of any data qualifiers used in the report.
Quality Control
Summary (Qc)
This section of the report includes the results of the laboratory quality control analyses required by procedure or
analytical methods to assist in evaluating the validity of the results reported for your samples. These analyses are not
being performed on your samples typically, but on laboratory generated material.
Sample Chain of
Custody (Sc)
This is the document created in the field when your samples were initially collected. This is used to verify the time and
date of collection, the person collecting the samples, and the analyses that the laboratory is requested to perform. This
chain of custody also documents all persons (excluding commercial shippers) that have had control or possession of the
samples from the time of collection until delivery to the laboratory for analysis.
Sample Results (Sr)
This section of your report will provide the results of all testing performed on your samples. These results are provided
by sample ID and are separated by the analyses performed on each sample. The header line of each analysis section for
each sample will provide the name and method number for the analysis reported.
Sample Summary (Ss)This section of the Analytical Report defines the specific analyses performed for each sample ID, including the dates and
times of preparation and/or analysis.
Qualifier Description
J The identification of the analyte is acceptable; the reported value is an estimate.
J3 The associated batch QC was outside the established quality control range for precision.
J5 The sample matrix interfered with the ability to make any accurate determination; spike value is high.
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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Pace Analytical National 12065 Lebanon Rd Mount Juliet, TN 37122
Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN000032021-1
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹TN00003
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹DW21704
Georgia NELAP North Carolina ³41
Georgia ¹923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶KY90010 South Carolina 84004002
Kentucky ²16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴2006
Louisiana LA018 Texas T104704245-20-18
Maine TN00003 Texas ⁵LAB0152
Maryland 324 Utah TN000032021-11
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 110033
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 998093910
Montana CERT0086 Wyoming A2LA
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS

¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace Analytical.
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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ANALYTICAL REPORT
September 05, 2024
Wasatch Environmental
Sample Delivery Group:L1771237
Samples Received:08/24/2024
Project Number:
Description:Sommers Auto Emergency Response
Site:COMMERS AUTO
Report To:Blake Downey, P.G.
2410 West California Avenue
Salt Lake City, UT 84104
Entire Report Reviewed By:
September 05, 2024
[Preliminary Report]
John Hawkins
Project Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be
reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace
Analytical National is performed per guidance provided in laboratory standard operating procedures ENV-SOP-MTJL-0067 and
ENV-SOP-MTJL-0068. Where sampling conducted by the customer, results relate to the accuracy of the information provided,
and as the samples are received.
Pace Analytical National
12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 mydata.pacelabs.com
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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TABLE OF CONTENTSTABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 4
Cn: Case Narrative 5
Su: Summary Results 6
2540 G-2011 Total Solids 6
Sample Result Inorganic Analysis Data Sheet 7
L1771237-01 08/27/24 10:08 LOGBAL1 7
BLANK(R4112601-1) WG2350446 08/27/24 10:08 LOGBAL1 8
DUP(R4112601-3) WG2350446 08/27/24 10:08 LOGBAL1 9
LCS(R4112601-2) WG2350446 08/27/24 10:08 LOGBAL1 10
Blank 11
LOGBAL1 WG2350446 11
Laboratory Duplicate 12
WG2350446 DUP(R4112601-3) 12
Laboratory Control Sample / Duplicate 13
WG2350446 LCS(R4112601-2) 13
Detection Limit Summary 14
2540 G-2011 - Solid 14
Analysis Log 15
LOGBAL1 WG2350446 15
6010B Metals (ICP) 16
Sample Result Inorganic Analysis Data Sheet 17
L1771237-01 09/05/24 09:53 ICP16 17
BLANK(R4115894-1) WG2351411 09/05/24 09:06 ICP16 18
LCS(R4115894-2) WG2351411 09/05/24 09:07 ICP16 19
MS(R4115894-5) WG2351411 09/05/24 09:14 ICP16 20
MSD(R4115894-6) WG2351411 09/05/24 09:15 ICP16 21
PS(R4115894-4) WG2351411 09/05/24 09:12 ICP16 22
SD(R4115894-3) WG2351411 09/05/24 09:10 ICP16 23
Calibration Verification 24
ICP16 090524ICP16 24
Blank 27
ICP16 090524ICP16 27
ICP Interference Check Sample 29
ICP16 09/05/24 07:09 29
ICP16 09/05/24 13:11 30
Matrix Spike / Duplicate 31
WG2351411 MS(R4115894-5) MSD(R4115894-6) 31
Post Digestion Spike 32
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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WG2351411 PS(R4115894-4) 32
Laboratory Control Sample / Duplicate 33
WG2351411 LCS(R4115894-2) 33
Serial Dilution 34
WG2351411 SD(R4115894-3) 34
Detection Limit Summary 35
6010B - Solid 35
Linear Dynamic Range 36
ICP16 01/25/24 15:25 36
Analysis Log 37
ICP16 090524ICP16 09/05/24 06:48 37
Initial Calibration Recovery 38
ICP16 090524ICP16 09/05/24 06:48 38
Initial Calibration 41
ICP16 090524ICP16 09/05/24 06:48 41
Gl: Glossary of Terms 42
Al: Accreditations & Locations 43
Sc: Sample Chain of Custody 44
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
EXC-1 L1771237-01 Solid Jacob Scott 08/23/24 10:42 08/24/24 09:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Total Solids by Method 2540 G-2011 WG2350446 1 08/27/24 09:57 08/27/24 10:08 KDW Mt. Juliet, TN
Metals (ICP) by Method 6010B WG2351411 1 09/04/24 08:21 09/05/24 09:53 DJS Mt. Juliet, TN
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the
appropriate preservatives, and within method specified holding times, unless qualified or notated within
the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples
have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control
are within established criteria except where addressed in this case narrative, a non-conformance form
or properly qualified within the sample results. By my digital signature below, I affirm to the best of my
knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the
quality of the data have been identified by the laboratory, and no information or data have been
knowingly withheld that would affect the quality of the data.
[Preliminary Report]
John Hawkins
Project Manager
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
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2540 G-2011 Total Solids
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET EXC-1
Lab Sample ID:L1771237-01 SDG:L1771237
Client Sample ID:EXC-1 Collected Date/Time:08/23/24 10:42
Lab File ID:08 Received Date/Time:08/24/24 09:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/27/24 09:57
Analytical Batch:WG2350446 Analysis Date/Time:08/27/24 10:08
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:15.459 g
Total Solids (%):96.1 Final Wt/Vol:14.906 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 96.1
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112601-1
Lab Sample ID:R4112601-1 SDG:L1771237
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:01 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/27/24 09:56
Analytical Batch:WG2350446 Analysis Date/Time:08/27/24 10:08
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:1.258 g
Total Solids (%):_______________Final Wt/Vol:1.258 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 0.000
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112601-3
Lab Sample ID:R4112601-3 SDG:L1771237
Client Sample ID:DUP Collected Date/Time:08/22/24 11:20
Lab File ID:02 Received Date/Time:08/23/24 09:00
Instrument ID:LOGBAL1 Preparation Date/Time:08/27/24 09:57
Analytical Batch:WG2350446 Analysis Date/Time:08/27/24 10:08
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:5.269 g
Total Solids (%):81.7 Final Wt/Vol:4.57 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 82.6
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4112601-2
Lab Sample ID:R4112601-2 SDG:L1771237
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:03 Received Date/Time:_______________
Instrument ID:LOGBAL1 Preparation Date/Time:08/27/24 09:56
Analytical Batch:WG2350446 Analysis Date/Time:08/27/24 10:08
Dilution Factor:1 Prep Method:SM 2540 G
Analytical Method:2540 G-2011 Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:11.267 g
Total Solids (%):_______________Final Wt/Vol:6.267 g
Analyte CAS Result Qualifier
%
Total Solids TSOLIDS 50.0
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1771237 Calibration (begin) date/time:_______________
Instrument ID:LOGBAL1 Calibration (end) date/time:_______________
Analytical Method:2540 G-2011 Analytical Run:WG2350446
Sample ID:BLANK Result BLANK
Qual
File ID:01
Analyte %
TOTAL SOLIDS 0.000
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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6-IN DUPLICATES SAMPLE NO.:
L1771237-01 R4112601-3
DUP Sample / File ID:R4112601-3 / 02 SDG:L1771237
OS Sample / File ID:L1770986-09 / 05 Analytical Batch:WG2350446
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte OS
Result
DUP
Result RPD RPD
Limits
%%%%
Total Solids 81.7 82.6 1.03 10
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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7-IN LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4112601-2
RECOVERY _______________
L1771237-01
LCS Sample / File ID:R4112601-2 / 03 SDG:L1771237
LCSD Sample / File ID:_______________Analytical Batch:WG2350446
Instrument ID:LOGBAL1 Dilution Factor:1
Analytical Method:2540 G-2011 Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD
Rec.Rec. Limits RPD RPD Limits
%%%%%%%
Total Solids 50.0 50.0 100 90.0 - 110
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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9-IN DETECTION LIMIT SUMMARY
Lab Sample IDs:L1771237-01 Analytical Method:2540 G-2011
Matrix:Solid Prep Method:SM 2540 G
Analyte CAS Wavelength Mass MDL RDL
%%
Total Solids TSOLIDS
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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12-IN ANALYSIS LOG
SDG:L1771237 Analytical Method:2540 G-2011
Instrument ID:LOGBAL1 Calibration Start Date:_______________
Analytical Run:WG2350446 Calibration End Date:_______________
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
BLANK R4112601-1 01 08/27/24 10:08 1 WG2350446
DUP R4112601-3 02 08/27/24 10:08 1 WG2350446
LCS R4112601-2 03 08/27/24 10:08 1 WG2350446
OS L1770986-09 05 08/27/24 10:08
EXC-1 L1771237-01 08 08/27/24 10:08 1 WG2350446
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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6010B Metals (ICP)
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET EXC-1
Lab Sample ID:L1771237-01 SDG:L1771237
Client Sample ID:EXC-1 Collected Date/Time:08/23/24 10:42
Lab File ID:20240905095359 Received Date/Time:08/24/24 09:00
Instrument ID:ICP16 Preparation Date/Time:09/04/24 08:21
Analytical Batch:WG2351411 Analysis Date/Time:09/05/24 09:53
Dilution Factor:1 Prep Method:3050B
Analytical Method:6010B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.51 g
Total Solids (%):96.1 Final Wt/Vol:50 mL
Analyte CAS Result (dry)Qualifier MDL (dry)RDL (dry)
mg/kg mg/kg mg/kg
Lead 7439-92-1 125 0.216 0.520
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115894-1
Lab Sample ID:R4115894-1 SDG:L1771237
Client Sample ID:BLANK Collected Date/Time:_______________
Lab File ID:20240905090602 Received Date/Time:_______________
Instrument ID:ICP16 Preparation Date/Time:09/04/24 08:21
Analytical Batch:WG2351411 Analysis Date/Time:09/05/24 09:06
Dilution Factor:1 Prep Method:3050B
Analytical Method:6010B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.52 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Lead 7439-92-1 U 0.208 0.500
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115894-2
Lab Sample ID:R4115894-2 SDG:L1771237
Client Sample ID:LCS Collected Date/Time:_______________
Lab File ID:20240905090741 Received Date/Time:_______________
Instrument ID:ICP16 Preparation Date/Time:09/04/24 08:21
Analytical Batch:WG2351411 Analysis Date/Time:09/05/24 09:07
Dilution Factor:1 Prep Method:3050B
Analytical Method:6010B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.51 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Lead 7439-92-1 98.9 0.208 0.500
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115894-5
Lab Sample ID:R4115894-5 SDG:L1771237
Client Sample ID:MS Collected Date/Time:08/21/24 14:10
Lab File ID:20240905091417 Received Date/Time:08/22/24 08:00
Instrument ID:ICP16 Preparation Date/Time:09/04/24 08:21
Analytical Batch:WG2351411 Analysis Date/Time:09/05/24 09:14
Dilution Factor:1 Prep Method:3050B
Analytical Method:6010B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.47 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Lead 7439-92-1 120 0.208 0.500
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115894-6
Lab Sample ID:R4115894-6 SDG:L1771237
Client Sample ID:MSD Collected Date/Time:08/21/24 14:10
Lab File ID:20240905091556 Received Date/Time:08/22/24 08:00
Instrument ID:ICP16 Preparation Date/Time:09/04/24 08:21
Analytical Batch:WG2351411 Analysis Date/Time:09/05/24 09:15
Dilution Factor:1 Prep Method:3050B
Analytical Method:6010B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.49 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Lead 7439-92-1 111 0.208 0.500
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115894-4
Lab Sample ID:R4115894-4 SDG:L1771237
Client Sample ID:PS Collected Date/Time:08/21/24 14:10
Lab File ID:20240905091238 Received Date/Time:08/22/24 08:00
Instrument ID:ICP16 Preparation Date/Time:09/04/24 08:21
Analytical Batch:WG2351411 Analysis Date/Time:09/05/24 09:12
Dilution Factor:1 Prep Method:3050B
Analytical Method:6010B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.47 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Lead 7439-92-1 111 0.208 0.500
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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1-IN SAMPLE RESULT SUMMARY SAMPLE NO.:
INORGANIC ANALYSIS DATA SHEET R4115894-3
Lab Sample ID:R4115894-3 SDG:L1771237
Client Sample ID:SD Collected Date/Time:08/21/24 14:10
Lab File ID:20240905091059 Received Date/Time:08/22/24 08:00
Instrument ID:ICP16 Preparation Date/Time:09/04/24 08:21
Analytical Batch:WG2351411 Analysis Date/Time:09/05/24 09:10
Dilution Factor:5 Prep Method:3050B
Analytical Method:6010B Sample Vol Used:_______________
Matrix:Solid Initial Wt/Vol:0.47 g
Total Solids (%):_______________Final Wt/Vol:50 mL
Analyte CAS Result Qualifier MDL RDL
mg/kg mg/kg mg/kg
Lead 7439-92-1 11.7 1.04 2.50
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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2-IN CALIBRATION VERIFICATION
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Concentration Units:mg/l
ICV ICVLL CCV
Sample ID:ICP160905240700 ICP160905240707 ICP160905240902
Analyte True Found %R %RSD True Found %R %RSD True Found %R %RSD
LEAD 1 0.9837419 98.4
0 0.346000 0.0050 0.00542645
9 109 63.500000 0.50 0.4948854 99 0.542000
ICV Limits:90 - 110 ICVLL Limits:50 - 150 CCV Limits:90 - 110 CCVLL Limits:50 - 150
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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2-IN CALIBRATION VERIFICATION
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Concentration Units:mg/l
CCV CCV CCV
Sample ID:ICP160905240922 ICP160905240942 ICP160905240959
Analyte True Found %R %RSD True Found %R %RSD True Found %R %RSD
LEAD 0.50 0.4914545 98.3
0 0.966000 0.50 0.4912165 98.2
0 1.420000 0.50 0.4898168 98 1.050000
ICV Limits:90 - 110 ICVLL Limits:50 - 150 CCV Limits:90 - 110 CCVLL Limits:50 - 150
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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2-IN CALIBRATION VERIFICATION
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Concentration Units:mg/l
CCVLL
Sample ID:ICP160905241309
Analyte True Found %R %RSD
LEAD 0.0050 0.007443687 149 6.390000
ICV Limits:90 - 110 ICVLL Limits:50 - 150 CCV Limits:90 - 110 CCVLL Limits:50 - 150
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Sample ID:ICB Result ICB Qual CCB Result CCB Qual BLANK Result BLANK
Qual CCB Result CCB Qual
File ID:20240905070152 20240905090420 20240905090602 20240905092412
Analyte mg/l mg/l mg/kg mg/l
LEAD -0.0007590767 U 0.0003304284 U U -0.0004083644 U
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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3-IN BLANKS
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Sample ID:CCB Result CCB Qual CCB Result CCB Qual
File ID:20240905094403 20240905100042
Analyte mg/l mg/l
LEAD 0.00005300844 U 0.0002644257 U
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 28 of 44
4-IN INTERFERENCE CHECK SAMPLE
SDG:L1771237 Analytical Method:6010B
Instrument ID:ICP16 Date:09/05/24 07:09
Instrument Run:090524ICP16
Analyte True Found True Found
ICSA ICSA ICSA ICSAB ICSAB ICSAB
mg/l mg/l % Rec.mg/l mg/l % Rec.
ALUMINUM 500 505.8973 101 500 504.1155 101
ANTIMONY 0 0.01490872 0.50 0.5109207 102
ARSENIC 0 0.007786994 0.50 0.5031079 101
BARIUM 0 0.002004127 0.50 0.5059784 101
BERYLLIUM 0 0.0006072984 0.50 0.4963944 99.30
BORON 0 0.001841965 1 0.9835576 98.40
CADMIUM 0 0.0001067063 1 1.007807 101
CALCIUM 500 500.7343 100 500 505.8027 101
CERIUM 0 0.03330617 0 0.05625895
CHROMIUM 0 -0.004523226 0.50 0.5046873 101
COBALT 0 -0.001063141 0.50 0.4802877 96.10
COPPER 0 0.003766054 0.50 0.5248016 105
IRON 200 200.5647 100 200 201.389 101
LANTHANUM 0 0.0001168901 0 -0.0095062
LEAD 0 0.002619069 1 0.9766952 97.70
LITHIUM 0 -0.004573032 0 -0.001577618
MAGNESIUM 500 503.0465 101 500 496.5673 99.30
MANGANESE 0 -0.01362355 0.50 0.5046789 101
MOLYBDENUM 0 0.001293961 0.50 0.4915217 98.30
NICKEL 0 -0.000001032714 1 0.932381 93.20
PHOSPHORUS 0 -0.0004310764 0 -0.02478732
POTASSIUM 0 0.1247434 0 0.07666738
SELENIUM 0 0.005756097 0.50 0.541282 108
SILICON 0 -0.01357732 1 1.078641 108
SILVER 0 -0.00297215 1 0.8641268 86.40
SODIUM 0 0.02296306 0 0.0461232
STRONTIUM 0 0.003673917 0 0.003908505
SULFUR 0 0.02181511 0 0.06045035
THALLIUM 0 0.01187618 0.50 0.4948022 99
TIN 0 0.001374573 0.50 0.4793545 95.90
TITANIUM 0 -0.004421009 0.50 0.4756931 95.10
VANADIUM 0 0.000902899 0.50 0.4777883 95.60
ZINC 0 0.006029244 1 0.961248 96.10
ICSA Limits:80 - 120 ICSAB Limits:80 - 120
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 29 of 44
4-IN INTERFERENCE CHECK SAMPLE
SDG:L1771237 Analytical Method:6010B
Instrument ID:ICP16 Date:09/05/24 13:11
Instrument Run:090524ICP16
Analyte True Found True Found
ICSA ICSA ICSA ICSAB ICSAB ICSAB
mg/l mg/l % Rec.mg/l mg/l % Rec.
ALUMINUM 500 504.2316 101 500 502.5875 101
ANTIMONY 0 0.02527426 0.50 0.5304247 106
ARSENIC 0 0.00716979 0.50 0.5042524 101
BARIUM 0 0.001800067 0.50 0.5083771 102
BERYLLIUM 0 0.0006714921 0.50 0.4993085 99.90
BORON 0 0.002730585 1 1.009116 101
CADMIUM 0 0.0005097996 1 1.013998 101
CALCIUM 500 503.523 101 500 505.4343 101
CERIUM 0 0.05710079 0 0.04225946
CHROMIUM 0 -0.004043739 0.50 0.5044173 101
COBALT 0 -0.0008162483 0.50 0.4863905 97.30
COPPER 0 0.003887514 0.50 0.526344 105
IRON 200 202.0616 101 200 203.1656 102
LANTHANUM 0 -0.001744416 0 -0.0070988
LEAD 0 0.007672323 1 0.9976029 99.80
LITHIUM 0 0.002403017 0 0.0004001574
MAGNESIUM 500 491.8417 98.40 500 490.7532 98.20
MANGANESE 0 -0.01446227 0.50 0.4934163 98.70
MOLYBDENUM 0 0.002626 0.50 0.499081 99.80
NICKEL 0 -0.0005139027 1 0.9469912 94.70
PHOSPHORUS 0 -0.006227043 0 -0.02303722
POTASSIUM 0 0.3038401 0 0.257425
SELENIUM 0 -0.008090527 0.50 0.5254499 105
SILICON 0 -0.01031113 1 1.091448 109
SILVER 0 -0.001350656 1 0.8590196 85.90
SODIUM 0 0.1282103 0 0.1393647
STRONTIUM 0 0.004029091 0 0.004306728
SULFUR 0 0.02822482 0 0.06068221
THALLIUM 0 0.01256634 0.50 0.4949562 99
TIN 0 0.001190844 0.50 0.4849454 97
TITANIUM 0 -0.003880352 0.50 0.4804282 96.10
VANADIUM 0 0.003086789 0.50 0.4804037 96.10
ZINC 0 0.005938939 1 0.9606874 96.10
ICSA Limits:80 - 120 ICSAB Limits:80 - 120
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 30 of 44
5A-IN MATRIX SPIKE /SAMPLE NO.:
MATRIX SPIKE DUPLICATE RECOVERY R4115894-5
L1771237-01 R4115894-6
MS Sample / File ID:R4115894-5 / 20240905091417 SDG:L1771237
MSD Sample / File ID:R4115894-6 / 20240905091556 Analytical Batch:WG2351411
OS Sample / File ID:L1770095-11 / 20240905090920 Matrix:Solid
Instrument ID:ICP16
Analytical Method:6010B
Analyte Spike
Amount
OS
Result
MS
Result
MSD
Result MS Rec.MSD
Rec.Dilution Rec. Limits RPD RPD Limits
mg/kg mg/kg mg/kg mg/kg %%%%%
Lead 100 12.7 120 111 107 98.3 1 75.0 - 125 7.67 20
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 31 of 44
5B-IN POST-DIGESTION / DISTILLATION SPIKE SAMPLE NO.:
SAMPLE RECOVERY R4115894-4
L1771237-01
PS Sample / File ID:R4115894-4 / 20240905091238 SDG:L1771237
OS Sample / File ID:L1770095-11 / 20240905090920 Analytical Batch:WG2351411
Instrument ID:ICP16 Dilution Factor:1
Analytical Method:6010B Matrix:Solid
Analyte Spike
Amount
OS
Result
PD
Result
DS
Result PD Rec.DS Rec.Dilution Rec.
Limits RPD RPD
Limits
mg/kg mg/kg mg/kg %%%mg/kg mg/kg
Lead 100 12.7 111 98.4 1 80.0 -
120
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 32 of 44
7-IN LABORATORY CONTROL SAMPLE SAMPLE NO.:
LABORATORY CONTROL SAMPLE DUPLICATE R4115894-2
RECOVERY _______________
L1771237-01
LCS Sample / File ID:R4115894-2 / 20240905090741 SDG:L1771237
LCSD Sample / File ID:_______________Analytical Batch:WG2351411
Instrument ID:ICP16 Dilution Factor:1
Analytical Method:6010B Matrix:Solid
Analyte Spike
Amount
LCS
Result
LCSD
Result LCS Rec.LCSD
Rec.Rec. Limits RPD RPD Limits
mg/kg mg/kg %%%%%
Lead 100 98.9 98.9 80.0 - 120
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 33 of 44
8-IN ICP AND ICP/MS SAMPLE NO.:
SERIAL DILUTIONS R4115894-3
L1771237-01
SD Sample / File ID:R4115894-3 / 20240905091059 SDG:L1771237
OS Sample / File ID:L1770095-11 / 20240905090920 Analytical Batch:WG2351411
Lab File ID:20240905091059 Dilution Factor:5
Instrument ID:ICP16 Matrix:Solid
Analytical Method:6010B
Analyte OS
Result
SD
Result RPD RPD
Limits
mg/kg mg/kg %%
Lead 12.7 11.7 7.95 10
*: Value outside the established quality control limits.
D: Surrogate recovery cannot be used for control limit evaluation due to dilution.
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 34 of 44
9-IN DETECTION LIMIT SUMMARY
Lab Sample IDs:L1771237-01 Analytical Method:6010B
Matrix:Solid Prep Method:3050B
Analyte CAS Wavelength Mass MDL RDL
mg/kg mg/kg
Lead 7439-92-1 220.3530 0.2080 0.50
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 35 of 44
10C-IN LINEAR DYNAMIC RANGE
SDG:L1771237 Analytical Method:6010B
Instrument ID:ICP16 Date:01/25/24 15:25
Analyte LDR
ppm
ALUMINUM 500
ANTIMONY 10
ARSENIC 50
BARIUM 50
BERYLLIUM 10
BORON 50
CADMIUM 10
CALCIUM 1000
CHROMIUM 50
COBALT 50
COPPER 50
IRON 500
LEAD 100
LITHIUM 10
MAGNESIUM 1000
MANGANESE 20
MOLYBDENUM 20
NICKEL 50
PHOSPHORUS 200
POTASSIUM 500
SELENIUM 10
SILICON 100
SILVER 10
SODIUM 1000
STRONTIUM 20
SULFUR 200
THALLIUM 10
TIN 50
TITANIUM 50
VANADIUM 20
ZINC 20
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 36 of 44
12-IN ANALYSIS LOG
SDG:L1771237 Analytical Method:6010B
Instrument ID:ICP16 Calibration Start Date:09/05/24 06:48
Analytical Run:090524ICP16 Calibration End Date:09/05/24 06:58
Client Sample ID Lab Sample ID File ID Analysis Date Time Dilution Batch
CALBLK ICP160905240646 20240905064656 09/05/24 06:46
CAL STD1 20240905064836 09/05/24 06:48
CAL STD2 20240905065013 09/05/24 06:50
CAL STD3 20240905065151 09/05/24 06:51
CAL STD4 20240905065331 09/05/24 06:53
CAL STD5 20240905065509 09/05/24 06:55
CAL STD6 20240905065646 09/05/24 06:56
ICV ICP160905240700 20240905070014 09/05/24 07:00
ICB ICP160905240701 20240905070152 09/05/24 07:01
ICVLL ICP160905240707 20240905070745 09/05/24 07:07
ICSA ICP160905240709 20240905070925 09/05/24 07:09
ICSAB ICP160905240711 20240905071104 09/05/24 07:11
CCV ICP160905240902 20240905090240 09/05/24 09:02
CCB ICP160905240904 20240905090420 09/05/24 09:04
BLANK R4115894-1 20240905090602 09/05/24 09:06 1 WG2351411
LCS R4115894-2 20240905090741 09/05/24 09:07 1 WG2351411
OS L1770095-11 20240905090920 09/05/24 09:09
L1770095-11 L1770095-11 20240905090920 09/05/24 09:09 1 WG2351411
SD R4115894-3 20240905091059 09/05/24 09:10 5 WG2351411
PS R4115894-4 20240905091238 09/05/24 09:12 1 WG2351411
MS R4115894-5 20240905091417 09/05/24 09:14 1 WG2351411
MSD R4115894-6 20240905091556 09/05/24 09:15 1 WG2351411
L1770095-01 L1770095-01 20240905091735 09/05/24 09:17 1 WG2351411
L1770095-02 L1770095-02 20240905091914 09/05/24 09:19 1 WG2351411
L1770095-03 L1770095-03 20240905092053 09/05/24 09:20 1 WG2351411
CCV ICP160905240922 20240905092232 09/05/24 09:22
CCB ICP160905240924 20240905092412 09/05/24 09:24
CCV ICP160905240942 20240905094224 09/05/24 09:42
CCB ICP160905240944 20240905094403 09/05/24 09:44
L1770613-14 L1770613-14 20240905094901 09/05/24 09:49 1 WG2351411
L1770613-15 L1770613-15 20240905095041 09/05/24 09:50 1 WG2351411
EXC-1 L1771237-01 20240905095359 09/05/24 09:53 1 WG2351411
CCV ICP160905240959 20240905095902 09/05/24 09:59
CCB ICP160905241000 20240905100042 09/05/24 10:00
CCVLL ICP160905241309 20240905130931 09/05/24 13:09
ICSA ICP160905241311 20240905131112 09/05/24 13:11
ICSAB ICP160905241312 20240905131254 09/05/24 13:12
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 37 of 44
15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
LEAD 0.0050 .004708615 94.20 0.10 .09708201 97.10
File ID: 20240905064836 20240905065013
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 38 of 44
15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
LEAD 0.20 .1942288 97.10 0.50 .4851612 97
File ID: 20240905065151 20240905065331
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 39 of 44
15-IN INITIAL CALIBRATION RECOVERY
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Analyte Std Conc Result Rec.Std Conc Result Rec.
mg/l mg/l %mg/l mg/l %
LEAD 1 .9818987 98.20 2 2.013484 101
File ID: 20240905065509 20240905065646
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 40 of 44
16A-IN INITIAL
CALIBRATION
SDG:L1771237 Calibration (begin) date/time:09/05/24 06:48
Instrument ID:ICP16 Calibration (end) date/time:09/05/24 06:58
Analytical Method:6010B Analytical Run:090524ICP16
Analyte Wavelength Cal. Type Weightage Corr.Slope Incpt
LEAD 220.353 8 5 0.999882 566.581 0.382631
Calibration Type
8 = Linear Regression Forced through Blank
Weightage
5 = None
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 41 of 44
GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
The information below is designed to better explain the various terms used in your report of analytical results from the Laboratory. This is not
intended as a comprehensive explanation, and if you have additional questions please contact your project representative.
Results Disclaimer - Information that may be provided by the customer, and contained within this report, include Permit Limits, Project Name,
Sample ID, Sample Matrix, Sample Preservation, Field Blanks, Field Spikes, Field Duplicates, On-Site Data, Sampling Collection Dates/Times, and
Sampling Location. Results relate to the accuracy of this information provided, and as the samples are received.
Abbreviations and Definitions
Corr.Correlation Coefficient.
(dry)Results are reported based on the dry weight of the sample. [this will only be present on a dry report basis for soils].
Incpt Intercept.
Mass Mass of parameter.
MDL Method Detection Limit.
MDL (dry)Method Detection Limit.
RDL Reported Detection Limit.
RDL (dry)Reported Detection Limit.
Rec.Recovery.
RPD Relative Percent Difference.
SDG Sample Delivery Group.
Analyte The name of the particular compound or analysis performed. Some Analyses and Methods will have multiple analytes
reported.
Dilution
If the sample matrix contains an interfering material, the sample preparation volume or weight values differ from the
standard, or if concentrations of analytes in the sample are higher than the highest limit of concentration that the
laboratory can accurately report, the sample may be diluted for analysis. If a value different than 1 is used in this field, the
result reported has already been corrected for this factor.
Limits
These are the target % recovery ranges or % difference value that the laboratory has historically determined as normal
for the method and analyte being reported. Successful QC Sample analysis will target all analytes recovered or
duplicated within these ranges.
Qualifier
This column provides a letter and/or number designation that corresponds to additional information concerning the result
reported. If a Qualifier is present, a definition per Qualifier is provided within the Glossary and Definitions page and
potentially a discussion of possible implications of the Qualifier in the Case Narrative if applicable.
Result
The actual analytical final result (corrected for any sample specific characteristics) reported for your sample. If there was
no measurable result returned for a specific analyte, the result in this column may state “ND” (Not Detected) or “BDL”
(Below Detectable Levels). The information in the results column should always be accompanied by either an MDL
(Method Detection Limit) or RDL (Reporting Detection Limit) that defines the lowest value that the laboratory could detect
or report for this analyte.
Slope Slope of calibration curve.
Uncertainty
(Radiochemistry)Confidence level of 2 sigma.
Wavelength Wavelength of parameter.
Case Narrative (Cn)
A brief discussion about the included sample results, including a discussion of any non-conformances to protocol
observed either at sample receipt by the laboratory from the field or during the analytical process. If present, there will
be a section in the Case Narrative to discuss the meaning of any data qualifiers used in the report.
Quality Control
Summary (Qc)
This section of the report includes the results of the laboratory quality control analyses required by procedure or
analytical methods to assist in evaluating the validity of the results reported for your samples. These analyses are not
being performed on your samples typically, but on laboratory generated material.
Sample Chain of
Custody (Sc)
This is the document created in the field when your samples were initially collected. This is used to verify the time and
date of collection, the person collecting the samples, and the analyses that the laboratory is requested to perform. This
chain of custody also documents all persons (excluding commercial shippers) that have had control or possession of the
samples from the time of collection until delivery to the laboratory for analysis.
Sample Results (Sr)
This section of your report will provide the results of all testing performed on your samples. These results are provided
by sample ID and are separated by the analyses performed on each sample. The header line of each analysis section for
each sample will provide the name and method number for the analysis reported.
Sample Summary (Ss)This section of the Analytical Report defines the specific analyses performed for each sample ID, including the dates and
times of preparation and/or analysis.
Qualifier Description
The remainder of this page intentionally left blank, there are no qualifiers applied to this SDG.
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 42 of 44

Pace Analytical National 12065 Lebanon Rd Mount Juliet, TN 37122
Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN000032021-1
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹TN00003
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹DW21704
Georgia NELAP North Carolina ³41
Georgia ¹923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶KY90010 South Carolina 84004002
Kentucky ²16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴2006
Louisiana LA018 Texas T104704245-20-18
Maine TN00003 Texas ⁵LAB0152
Maryland 324 Utah TN000032021-11
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 110033
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 998093910
Montana CERT0086 Wyoming A2LA
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS

¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace Analytical.
1 Cp
2 Tc
3 Ss
4 Cn
5 Su
6 Gl
7 Al
8 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Wasatch Environmental L1771237 09/05/24 14:36 43 of 44
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24F2233
Project: Former Sommers Auto Wrecking
6/27/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 4
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/27/24 11:25 @ 14.5 °C
6/27/2024
Former Sommers Auto Wrecking
Sample ID: MW-4
Lab ID: 24F2233-01Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 6/27/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Metals
mg/L 6/27/246/27/240.0090 EPA 6020A/3010A0.168Copper, Total
mg/L 6/27/246/27/240.100 EPA 6020A/3010A0.318Zinc, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F2233
www.ChemtechFord.com
Page 2 of 4Page 2 of 4
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
6/27/24 11:25 @ 14.5 °C
6/27/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Project Name: Former Sommers Auto Wrecking CtF WO#: 24F2233
www.ChemtechFord.com
Page 3 of 4Page 3 of 4
Page 4 of 4
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24G0433
Project: 2469-002G Sommers Auto
7/9/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 4
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
7/8/24 10:35 @ 14.4 °C
7/9/2024
2469-002G Sommers Auto
Sample ID: MW-4
Lab ID: 24G0433-01Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 7/8/24 10:10
Preparation
Date/Time
Sampled By: R Kubina
Minimum
Reporting
Limit MethodResult
Calculations
mg/L 7/9/247/8/246.7 SM 2340 B/[CALC]1360Hardness, Total as CaCO3
Metals
mg/L 7/9/247/8/240.2 EPA 200.7/200.2308Calcium, Total
mg/L 7/9/247/8/241.5 EPA 200.7/200.2144Magnesium, Total
Project Name: 2469-002G Sommers Auto CtF WO#: 24G0433
www.ChemtechFord.com
Page 2 of 4Page 2 of 4
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
7/8/24 10:35 @ 14.4 °C
7/9/2024
2469-002G Sommers Auto
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Project Name: 2469-002G Sommers Auto CtF WO#: 24G0433
www.ChemtechFord.com
Page 3 of 4Page 3 of 4
Page 4 of 4
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H1959
Project: Former Sommers Auto Wrecking
8/22/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 22
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H1959-01 EXC-2-N
24H1959-02 EXC-2-E
24H1959-03 EXC-2-SE
24H1959-04 EXC-2-S
24H1959-05 EXC-2-W
24H1959-06 EXC-2-Floor
24H1959-07 EXC-2-W2
24H1959-08 Frac Tank
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order, with the following exceptions: Arsenic and Lead were observed above the MRL in
BYH1068-BLK1. The concentration in the method blank is less than 10% of the sample result, which is negligible
according to method criteria.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria. Batch BYH1050 had low LCS recoveries for MTBE.
It is important to note that certain flags on an individual analyte do not constitute failure of the method as a whole. EPA
methodologies recognize that it may not be possible for every compound to meet all recovery or percent difference criteria .
The batch passed required method criteria for these analytes.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
Page 2 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-N
Lab ID: 24H1959-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:40
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800092.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.089 EPA 6020A/3050B24.4Arsenic, Total
mg/kg dry B8/22/248/21/240.107 EPA 6020A/3050B668Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 3 of 22Page 3 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-E
Lab ID: 24H1959-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:45
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800088.8Total Solids
Metals
mg/kg dry B8/22/248/21/240.051 EPA 6020A/3050B21.9Arsenic, Total
mg/kg dry B8/22/248/21/240.609 EPA 6020A/3050B643Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 4 of 22Page 4 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-SE
Lab ID: 24H1959-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:50
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800086.9Total Solids
Metals
mg/kg dry B8/22/248/21/240.082 EPA 6020A/3050B22.6Arsenic, Total
mg/kg dry B8/22/248/21/240.099 EPA 6020A/3050B165Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 5 of 22Page 5 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-S
Lab ID: 24H1959-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 12:55
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800097.2Total Solids
Metals
mg/kg dry B8/22/248/21/240.073 EPA 6020A/3050B12.6Arsenic, Total
mg/kg dry B8/22/248/21/240.087 EPA 6020A/3050B312Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 6 of 22Page 6 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-W
Lab ID: 24H1959-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800094.4Total Solids
Metals
mg/kg dry B8/22/248/21/240.064 EPA 6020A/3050B16.8Arsenic, Total
mg/kg dry B8/22/248/21/240.077 EPA 6020A/3050B352Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 7 of 22Page 7 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-Floor
Lab ID: 24H1959-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:05
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800083.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.057 EPA 6020A/3050B16.6Arsenic, Total
mg/kg dry B8/22/248/21/240.068 EPA 6020A/3050B221Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 8 of 22Page 8 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: EXC-2-W2
Lab ID: 24H1959-07Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/20/24 13:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/21/248/21/240.1 CTF800094.5Total Solids
Metals
mg/kg dry B8/22/248/21/240.094 EPA 6020A/3050B13.9Arsenic, Total
mg/kg dry B8/22/248/21/240.113 EPA 6020A/3050B293Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 9 of 22Page 9 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Sample ID: Frac Tank
Lab ID: 24H1959-08Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/21/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/L 8/21/248/21/241.0 EPA 8015 CNDDiesel Range Organics
Inorganic
mg/L 8/22/248/21/246EPA 1664BNDOil & Grease (HEM)
pH Units SPH8/22/24 13:568/22/24 12:040.1 SM 4500 H-B1.9pH
mg/L 8/21/248/21/24100SM 2540 C1300Total Dissolved Solids (TDS)
mg/L 8/21/248/21/244SM 2540 D4Total Suspended Solids (TSS)
mg/L 8/22/248/21/246EPA 1664BNDTRPH (SGT-HEM)
Metals
mg/L 8/22/248/21/240.0005 EPA 6020A/3010A0.149Arsenic, Total
mg/L 8/22/248/21/240.0030 EPA 6020A/3010A0.607Barium, Total
mg/L 8/22/248/21/240.0010 EPA 6020A/3010A0.0035Chromium, Total
mg/L 8/22/248/21/240.0009 EPA 6020A/3010A0.0019Copper, Total
mg/L 8/22/248/21/240.0006 EPA 6020A/3010A0.0031Lead, Total
mg/L 8/22/248/21/240.0100 EPA 6020A/3010ANDZinc, Total
MBTEXn
mg/L 8/21/248/21/240.005 EPA 8260D/5030BNDBenzene
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDEthylbenzene
mg/L J-LOW-L8/21/248/21/240.008 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDNaphthalene
mg/L 8/21/248/21/240.012 EPA 8260D/5030BNDToluene
mg/L 8/21/248/21/240.038 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/L 8/21/248/21/240.125 EPA 8260B/C 5030A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 10 of 22Page 10 of 22
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/21/24 14:36 @ 4.1 °C
8/22/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
B = Analyte is found in the associated blank as well as in the sample (CLP B-flag).
J-LOW-L = Estimated low due to low recovery of LCS
SPH = Sample submitted past method specified holding time.
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H1959
www.ChemtechFord.com
Page 11 of 22Page 11 of 22
Zn
,
Pb
,
As
,
B
a
,
Cr
,
Cu
ad
d
e
d
pe
r
Bl
a
k
e
Do
w
n
e
y
em
a
i
l
.
-
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-
8/
2
2
/
2
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Page 12 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYH1082-DUP1 QC Source Sample: 24H1959-01Batch: BYH1082
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Solids 0.834 20 93.3 92.5 0.1 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 13 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 1664B
QC Sample ID: BYH1063-BLK1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)ND 5 1.00
TRPH (SGT-HEM)ND 5 1.00
LCS - EPA 1664B
QC Sample ID: BYH1063-BS1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)87.8 78 - 114 35 40.0 5 1.00
TRPH (SGT-HEM)88.5 64 - 132 18 20.0 5 1.00
LCS Dup - EPA 1664B
QC Sample ID: BYH1063-BSD1 Batch: BYH1063
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Oil & Grease (HEM)83.8 4.66 78 - 114 18 34 40.0 5 1.00
TRPH (SGT-HEM)84.0 5.22 64 - 132 34 17 20.0 5 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 14 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6020A
QC Sample ID: BYH1068-BLK1 Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 0.106 0.050 1.00
QB-01 - The method blank contains analyte at a concentration above the MRL; however, concentration is less than 10% of the
sample result, which is negligible according to method criteria.
Lead, Total 0.110 0.060 1.00
QB-01 - The method blank contains analyte at a concentration above the MRL; however, concentration is less than 10% of the
sample result, which is negligible according to method criteria.
QC Sample ID: BYH1069-BLK1 Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total ND 0.0005 1.00
Barium, Total ND 0.0030 1.00
Chromium, Total ND 0.0010 1.00
Copper, Total ND 0.0009 1.00
Lead, Total ND 0.0006 1.00
Zinc, Total ND 0.0100 1.00
LCS - EPA 6020A
QC Sample ID: BYH1069-BS2 Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 99.0 85 - 115 0.396 0.400 0.0050 1.00
Barium, Total 99.9 85 - 115 0.400 0.400 0.0300 1.00
Chromium, Total 97.1 85 - 115 0.388 0.400 0.0100 1.00
Copper, Total 98.7 85 - 115 0.395 0.400 0.0090 1.00
Lead, Total 97.2 85 - 115 0.389 0.400 0.0060 1.00
Zinc, Total 108 85 - 115 0.434 0.400 0.100 1.00
Matrix Spike - EPA 6020A
QC Sample ID: BYH1068-MS2 QC Source Sample: 24H1959-01Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 17.7 75 - 125 25.5 24.4 6.10 0.076 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 298 75 - 125 686 668 6.10 0.092 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1069-MS1 QC Source Sample: 24H1959-08Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 89.8 70 - 130 0.221 0.149 0.0800 0.0005 1.00
Barium, Total 102 70 - 130 0.689 0.607 0.0800 0.0030 1.00
Chromium, Total 92.8 70 - 130 0.078 0.004 0.0800 0.0010 1.00
Copper, Total 81.4 70 - 130 0.067 0.002 0.0800 0.0009 1.00
Lead, Total 90.5 70 - 130 0.076 0.003 0.0800 0.0006 1.00
Zinc, Total 75.3 70 - 130 0.069 0.009 0.0800 0.0100 1.00
Matrix Spike Dup - EPA 6020A
QC Sample ID: BYH1068-MSD2 QC Source Sample: 24H1959-01Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 67.3 10.8 75 - 125 20 28.4 24.4 5.92 0.074 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 366 0.503 75 - 125 20 689 668 5.92 0.089 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
CtF WO#: 24H1959
www.ChemtechFord.com Page 15 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 6020A (cont.)
QC Sample ID: BYH1069-MSD1 QC Source Sample: 24H1959-08Batch: BYH1069
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 93.3 1.26 70 - 130 20 0.224 0.149 0.0800 0.0005 1.00
Barium, Total 115 1.41 70 - 130 20 0.699 0.607 0.0800 0.0030 1.00
Chromium, Total 96.6 3.83 70 - 130 20 0.081 0.004 0.0800 0.0010 1.00
Copper, Total 84.3 3.37 70 - 130 20 0.069 0.002 0.0800 0.0009 1.00
Lead, Total 93.4 3.00 70 - 130 20 0.078 0.003 0.0800 0.0006 1.00
Zinc, Total 78.1 3.19 70 - 130 20 0.071 0.009 0.0800 0.0100 1.00
Reference - EPA 6020A
QC Sample ID: BYH1068-SRM1 Batch: BYH1068
Date Prepared: 08/21/2024 Date Analyzed: 08/22/2024
Arsenic, Total 106 77.78 - 144.3 70.5 66.6 0.099 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
Lead, Total 85.7 63.16 - 121.4 212 247 0.119 1.00
B - Analyte is found in the associated blank as well as in the sample (CLP B-flag).
CtF WO#: 24H1959
www.ChemtechFord.com Page 16 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH1124-BLK1 Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics ND 1.0 1.00
LCS - EPA 8015 C
QC Sample ID: BYH1124-BS1 Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 109 50 - 150 44 40.0 1.0 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH1124-MS1 QC Source Sample: 24H1959-08Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 100 50 - 150 40 ND 40.0 1.0 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH1124-MSD1 QC Source Sample: 24H1959-08Batch: BYH1124
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Diesel Range Organics 108 7.11 50 - 150 20 43 ND 40.0 1.0 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 17 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH1050-BLK1 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
QC Sample ID: BYH1050-BLK2 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene ND 0.100 1.00
Ethylbenzene ND 0.250 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.150 1.00
Naphthalene ND 0.250 1.00
Toluene ND 0.250 1.00
Xylenes, total ND 0.750 1.00
LCS - EPA 8260D
QC Sample ID: BYH1050-BS1 Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 96.6 70 - 130 0.010 0.0100 0.0004 1.00
Ethylbenzene 105 70 - 130 0.011 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)50.3 70 - 130 0.005 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 124 70 - 130 0.012 0.0100 0.001 1.00
Toluene 96.6 70 - 130 0.010 0.0100 0.001 1.00
Xylenes, total 110 70 - 130 0.033 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH1050-MS2 QC Source Sample: 24H1959-08Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 88.9 70 - 130 0.111 ND 0.125 0.005 1.00
Ethylbenzene 89.2 70 - 130 0.112 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)62.7 70 - 130 0.078 ND 0.125 0.008 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Naphthalene 95.3 70 - 130 0.119 ND 0.125 0.012 1.00
Toluene 88.6 70 - 130 0.111 ND 0.125 0.012 1.00
Xylenes, total 94.9 70 - 130 0.356 ND 0.375 0.038 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH1050-MSD2 QC Source Sample: 24H1959-08Batch: BYH1050
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Benzene 87.4 1.70 70 - 130 20 0.109 ND 0.125 0.005 1.00
Ethylbenzene 90.1 1.00 70 - 130 25 0.113 ND 0.125 0.012 1.00
Methyl tert-Butyl Ether (MTBE)54.8 13.4 70 - 130 25 0.068 ND 0.125 0.008 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Naphthalene 92.0 3.52 70 - 130 25 0.115 ND 0.125 0.012 1.00
Toluene 87.2 1.59 70 - 130 20 0.109 ND 0.125 0.012 1.00
Xylenes, total 93.3 1.70 70 - 130 20 0.350 ND 0.375 0.038 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 18 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - SM 2540 C
QC Sample ID: BYH1067-BLK1 Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)ND 10 1.00
Duplicate - SM 2540 C
QC Sample ID: BYH1067-DUP1 QC Source Sample: 24H1959-08Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)0 10 1300 1300 100 1.00
LCS - SM 2540 C
QC Sample ID: BYH1067-BS1 Batch: BYH1067
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Dissolved Solids (TDS)97 90 - 110 388 400 20 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 19 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
QC Sample ID: BYH1081-BLK1 Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)ND 1 1.00
QC Sample ID: BYH1081-DUP1 QC Source Sample: 24H1959-08Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)11.8 20 3 4 4 1.00
QC Sample ID: BYH1081-DUP2 QC Source Sample: XXXXXXX-XXBatch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)20.7 20 5 6 4 1.00
QM-020 - The RPD and/or percent recovery for this QC spike sample cannot be accurately calculated due to the low
concentration of analyte inherent in the sample. The batch was accepted based on acceptable LCS recovery.
QC Sample ID: BYH1081-SRM1 Batch: BYH1081
Date Prepared: 08/21/2024 Date Analyzed: 08/21/2024
Total Suspended Solids (TSS)91.0 80 - 120 91 100 10 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 20 of 22
QC Report for Work Order (WO) - 24H1959
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - SM 4500 H-B
QC Sample ID: BYH1104-DUP1 QC Source Sample: 24H1959-08Batch: BYH1104
Date Prepared: 08/22/2024 Date Analyzed: 08/22/2024
pH 1.60 3 1.9 1.9 0.1 1.00
CtF WO#: 24H1959
www.ChemtechFord.com Page 21 of 22
Surrogates Report for Work Order (WO) - 24H1959
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH1124-BLK1 Bromofluorobenzene 78.4 50 BYH1124 1.001503.14 4.00
BYH1124-BLK1 Capric Acid 0 BYH1124 1.0010.00 10.0
LCS - EPA 8015 C
BYH1124-BS1 Bromofluorobenzene 80.1 50 BYH1124 1.001503.21 4.00
BYH1124-BS1 Capric Acid 0 BYH1124 1.0010.00 10.0
Matrix Spike - EPA 8015 C
BYH1124-MS1 Bromofluorobenzene 126 50 BYH1124 1.001505.06 4.00
BYH1124-MS1 Capric Acid 0 BYH1124 1.0010.00 10.0
Matrix Spike Dup - EPA 8015 C
BYH1124-MSD1 Bromofluorobenzene 125 50 BYH1124 1.001505.01 4.00
BYH1124-MSD1 Capric Acid 0 BYH1124 1.0010.00 10.0
Blank - EPA 8260D
BYH1050-BLK2 Toluene-d8 102 83.3 BYH1050 1.001222.55 2.50
BYH1050-BLK1 Toluene-d8 102 83.3 BYH1050 1.001220.0102 0.0100
LCS - EPA 8260D
BYH1050-BS1 Toluene-d8 101 83.3 BYH1050 1.001220.0101 0.0100
Matrix Spike - EPA 8260D
BYH1050-MS2 Toluene-d8 104 83.3 BYH1050 1.001220.130 0.125
BYH1050-MS1 Toluene-d8 102 83.3 BYH1050 1.001222.54 2.50
Matrix Spike Dup - EPA 8260D
BYH1050-MSD2 Toluene-d8 103 83.3 BYH1050 1.001220.129 0.125
BYH1050-MSD1 Toluene-d8 103 83.3 BYH1050 1.001222.56 2.50
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24H1959-08 Capric Acid 0.00 0 110.0
24H1959-08 Bromofluorobenzene 4.94 123 50 1504.00
MBTEXN-GRO
24H1959-08 Toluene-d8 0.129 103 83.3 1220.125
CtF WO#: 24H1959
www.ChemtechFord.com Page 22 of 22
The analyses presented on this report were performed in accordance with the
National Environmental Laboratory Accreditation Program (NELAP) unless
noted in the comments, flags, or case narrative. If the report is to be used for
regulatory compliance, it should be presented in its entirety, and not be
altered.
Client Service Contact: 801.262.7299
Wasatch Environmental
Attn: Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
Work Order: 24H2214
Project: Former Sommers Auto Wrecking
8/27/2024
Approved By:
Melissa Connolly, Project Manager
9632 South 500 West Sandy, Utah 84070
Serving the Intermountain West since 1953
801.262.7299 Main 866.792.0093 Fax www.ChemtechFord.com
Page 1 of 31
_____________________________________________________________________________________________
Wasatch Environmental
Project: Former Sommers Auto Wrecking
Project Manager: Blake Downey
Laboratory ID Sample Name
24H2214-01 EXC-3-N
24H2214-02 EXC-3-E
24H2214-03 EXC-3-S
24H2214-04 EXC-3-W
24H2214-05 EXC-3-Floor
24H2214-06 EXC-3-Floor 10
24H2214-07 Equipment Blank
24H2214-08 EXC-4-NE2
24H2214-09 EXC-1-Comp
24H2214-10 Trip Blank
24H2214-11 Frack Tank 2
______________________________________________________________________________________________
Work Order Report Narrative
Sample Preparation
All samples were prepared within method specified holding times. No preparation issues were noted.
Method Blanks
All blank values were within method acceptance criteria. No blank values exceeded the minimum reporting limit for any
analysis in this work order.
Laboratory Control Samples
All laboratory control samples were within method acceptance criteria, except as noted by qualifying flags. Batches
BYH1199 and BYH1214 for method 8260D and LCS recoveries outside of the control limits for several compounds. It is
important to note that certain flags on an individual analyte do not constitute failure of the method as a whole. EPA
methodologies recognize that it may not be possible for every compound to meet all recovery or percent difference criteria .
The batch passed required method criteria for these analytes.
Method Spikes
All method spike recoveries were within method acceptance criteria, except as noted by qualifying flags.
Method Spike Duplicates
All method spike duplicates were within method acceptance criteria, except as noted by qualifying flags.
Corrective Actions
There are no corrective actions associated with this work order.
www.ChemtechFord.com
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
Page 2 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-N
Lab ID: 24H2214-01Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800078.6Total Solids
Metals
mg/kg dry 8/26/248/23/240.047 EPA 6020A/3050B15.9Arsenic, Total
mg/kg dry 8/26/248/23/240.056 EPA 6020A/3050B121Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 3 of 30Page 3 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-E
Lab ID: 24H2214-02Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:05
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800082.0Total Solids
Metals
mg/kg dry 8/26/248/23/240.043 EPA 6020A/3050B16.2Arsenic, Total
mg/kg dry 8/26/248/23/240.102 EPA 6020A/3050B183Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 4 of 30Page 4 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-S
Lab ID: 24H2214-03Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:10
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800092.3Total Solids
Metals
mg/kg dry 8/26/248/23/240.085 EPA 6020A/3050B21.4Arsenic, Total
mg/kg dry 8/26/248/23/240.511 EPA 6020A/3050B766Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 5 of 30Page 5 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-W
Lab ID: 24H2214-04Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:15
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800095.5Total Solids
Metals
mg/kg dry 8/26/248/23/240.082 EPA 6020A/3050B15.5Arsenic, Total
mg/kg dry 8/26/248/23/240.098 EPA 6020A/3050B120Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 6 of 30Page 6 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-Floor
Lab ID: 24H2214-05Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:20
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800086.6Total Solids
Metals
mg/kg dry 8/26/248/23/240.084 EPA 6020A/3050B11.0Arsenic, Total
mg/kg dry 8/26/248/23/240.101 EPA 6020A/3050B47.5Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 7 of 30Page 7 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-3-Floor 10
Lab ID: 24H2214-06Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:25
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800084.7Total Solids
Metals
mg/kg dry 8/26/248/23/240.107 EPA 6020A/3050B11.6Arsenic, Total
mg/kg dry 8/26/248/23/240.128 EPA 6020A/3050B107Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 8 of 30Page 8 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Equipment Blank
Lab ID: 24H2214-07Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 11:45
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Metals
mg/L 8/27/248/26/240.0005 EPA 6020A/3010ANDArsenic, Total
mg/L 8/27/248/26/240.0006 EPA 6020A/3010ANDLead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 9 of 30Page 9 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-4-NE2
Lab ID: 24H2214-08Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 13:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Diesel Range with silica gel cleanup
mg/kg dry 8/23/248/23/2461EPA 8015 C296Diesel Range Organics
Inorganic
%8/23/248/23/240.1 CTF800082.5Total Solids
MBTEXn
mg/kg dry 8/23/248/23/240.12 EPA 8260D/5030BNDBenzene
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDEthylbenzene
mg/kg dry J-LOW-L8/23/248/23/240.18 EPA 8260D/5030BNDMethyl tert-Butyl Ether (MTBE)
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDNaphthalene
mg/kg dry 8/23/248/23/240.30 EPA 8260D/5030BNDToluene
mg/kg dry 8/23/248/23/240.91 EPA 8260D/5030BNDXylenes, total
Gasoline Range
mg/kg dry 8/23/248/23/243.03 EPA 8260B/C 5035A/[CALC]NDGasoline Range Organics
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 10 of 30Page 10 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: EXC-1-Comp
Lab ID: 24H2214-09Matrix: Solid
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 15:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
%8/23/248/23/240.1 CTF800096.9Total Solids
Metals
mg/kg dry 8/26/248/23/240.085 EPA 6020A/3050B10.3Arsenic, Total
mg/kg dry 8/26/248/23/240.103 EPA 6020A/3050B290Lead, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 11 of 30Page 11 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank
Lab ID: 24H2214-10Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 12:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,1,2-Tetrachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,1-Trichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2,2-Tetrachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2-Trichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1,2-Trichlorotrifluoroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,1-Dichloropropene
ug/L 8/23/248/23/2410.0 EPA 8260D/5030BND2-Hexanone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,3-Trichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,3-Trichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,4-Trichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2,4-Trimethylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dibromo-3-chloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dibromoethane (EDB)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,2-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3,5-Trimethylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,3-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND1,4-Dichlorobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND2,2-Dichloropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND2-Chlorotoluene
ug/L J-LOW-L8/23/248/23/242.0 EPA 8260D/5030BND2-Nitropropane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BND4-Chlorotoluene
ug/L 8/23/248/23/2420.0 EPA 8260D/5030BNDAcetone
ug/L 8/23/248/23/245.0 EPA 8260D/5030BNDAcrylonitrile
ug/L 8/23/248/23/240.4 EPA 8260D/5030BNDBenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromobenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromochloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030B2.4Bromodichloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDBromoform
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDBromomethane
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDCarbon Disulfide
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDCarbon Tetrachloride
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChlorobenzene
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 12 of 30Page 12 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Trip Blank (cont.)
Lab ID: 24H2214-10Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/22/24 12:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Volatile Organic Compounds (cont.)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030B8.0Chloroform
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDChloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDcis-1,2-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDcis-1,3-Dichloropropene
ug/L J-LOW-C8/23/248/23/2410.0 EPA 8260D/5030BNDCyclohexanone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDibromochloromethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDibromomethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDDichlorodifluoromethane
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDEthyl Acetate
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDEthylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDEthyl Ether
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDHexachlorobutadiene
ug/L 8/23/248/23/2420.0 EPA 8260D/5030BNDIsobutanol
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDIsopropylbenzene
ug/L 8/23/248/23/242.0 EPA 8260D/5030BNDMethyl Ethyl Ketone
ug/L 8/23/248/23/245.0 EPA 8260D/5030BNDMethyl Isobutyl Ketone
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDMethylene Chloride
ug/L 8/23/248/23/240.6 EPA 8260D/5030BNDMethyl-tert-butyl ether (MTBE)
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDNaphthalene
ug/L 8/23/248/23/2450.0 EPA 8260D/5030BNDn-Butyl Alcohol
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDn-Butylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDn-Propyl Benzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDPentachloroethane
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDp-Isopropyltoluene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDsec-Butyl Benzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDStyrene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtert-Butylbenzene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTetrachloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDToluene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtrans-1,2-Dichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDtrans-1,3-Dichloropropene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTrichloroethene
ug/L 8/23/248/23/241.0 EPA 8260D/5030BNDTrichlorofluoromethane
ug/L 8/23/248/23/240.8 EPA 8260D/5030BNDVinyl Chloride
ug/L 8/23/248/23/243.0 EPA 8260D/5030BNDXylenes, total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 13 of 30Page 13 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Sample ID: Frack Tank 2
Lab ID: 24H2214-11Matrix: Water
Flag(s)Units
Analysis
Date/Time
Date Sampled: 8/23/24 10:00
Preparation
Date/Time
Sampled By: Jacob Scott
Minimum
Reporting
Limit MethodResult
Inorganic
mg/L 8/23/248/23/2420SM 2540 C1030Total Dissolved Solids (TDS)
Metals
mg/L 8/27/248/26/240.0005 EPA 6020A/3010A0.0870Arsenic, Total
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 14 of 30Page 14 of 31
xx
Chemtech-Ford Laboratories
Serving the Intermountain West Since 1953
Certificate of Analysis
9632 South 500 West
Sandy, UT 84070
O:[phone] F: [phone]
www.ChemtechFord.com
Wasatch Environmental
Blake Downey
2410 West California Avenue
Salt Lake City, UT 84104
PO#:
Receipt:
Date Reported:
Project Name:
2469-002G
8/23/24 12:38 @ 4.0 °C
8/27/2024
Former Sommers Auto Wrecking
Report Footnotes
Abbreviations
ND = Not detected at the corresponding Minimum Reporting Limit (MRL).
1 mg/L = one milligram per liter or 1 mg/kg = one milligram per kilogram = 1 part per million.
1 ug/L = one microgram per liter or 1 ug/kg = one microgram per kilogram = 1 part per billion.
1 ng/L = one nanogram per liter or 1 ng/kg = one nanogram per kilogram = 1 part per trillion.
On calculated parameters, there may be a slight difference between summing the rounded values shown on the report
vs the unrounded values used in the calculation.
Flag Descriptions
J-LOW-C = Estimated low due to low recovery of CCV
J-LOW-L = Estimated low due to low recovery of LCS
Project Name: Former Sommers Auto Wrecking CtF WO#: 24H2214
www.ChemtechFord.com
Page 15 of 30Page 15 of 31
Page 16 of 31
Page 17 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Duplicate - CTF8000
QC Sample ID: BYH1184-DUP1 QC Source Sample: XXXXXXX-XXBatch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.158 20 81.5 81.6 0.1 1.00
QC Sample ID: BYH1184-DUP2 QC Source Sample: 24H2214-01Batch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.625 20 79.1 78.6 0.1 1.00
QC Sample ID: BYH1184-DUP3 QC Source Sample: 24H2214-08Batch: BYH1184
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Solids 0.483 20 82.1 82.5 0.1 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 18 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 6020A
QC Sample ID: BYH1194-BLK1 Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total ND 0.050 1.00
Lead, Total ND 0.060 1.00
QC Sample ID: BYH1238-BLK1 Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total ND 0.0005 1.00
Lead, Total ND 0.0006 1.00
LCS - EPA 6020A
QC Sample ID: BYH1238-BS1 Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 96.1 85 - 115 0.038 0.0400 0.0005 1.00
Lead, Total 94.0 85 - 115 0.038 0.0400 0.0006 1.00
Matrix Spike - EPA 6020A
QC Sample ID: BYH1194-MS1 QC Source Sample: 24H2214-01Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 141 75 - 125 23.6 15.9 5.49 0.069 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
Lead, Total 844 75 - 125 168 121 5.49 0.082 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1238-MS1 QC Source Sample: 24H2214-11Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 90.4 70 - 130 0.123 0.087 0.0400 0.0005 1.00
Lead, Total 88.0 70 - 130 0.052 0.016 0.0400 0.0006 1.00
Matrix Spike Dup - EPA 6020A
QC Sample ID: BYH1194-MSD1 QC Source Sample: 24H2214-01Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 121 5.90 75 - 125 20 22.3 15.9 5.30 0.066 1.00
Lead, Total 899 0.791 75 - 125 20 169 121 5.30 0.079 1.00
QM-4X - The spike recovery was outside of QC acceptance limits for the MS and/or MSD due to analyte concentration at 4
times or greater the spike concentration. The QC batch was accepted based on LCS and/or LCSD recoveries within the
acceptance limits.
QC Sample ID: BYH1238-MSD1 QC Source Sample: 24H2214-11Batch: BYH1238
Date Prepared: 08/26/2024 Date Analyzed: 08/27/2024
Arsenic, Total 91.9 0.497 70 - 130 20 0.124 0.087 0.0400 0.0005 1.00
Lead, Total 86.6 1.13 70 - 130 20 0.051 0.016 0.0400 0.0006 1.00
Reference - EPA 6020A
QC Sample ID: BYH1194-SRM1 Batch: BYH1194
Date Prepared: 08/23/2024 Date Analyzed: 08/26/2024
Arsenic, Total 108 77.78 - 144.3 72.0 66.6 0.177 1.00
Lead, Total 86.2 63.16 - 121.4 213 247 0.213 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 19 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8015 C
QC Sample ID: BYH1227-BLK1 Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics ND 50 1.00
LCS - EPA 8015 C
QC Sample ID: BYH1227-BS1 Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 106 50 - 150 2120 2000 50 1.00
Matrix Spike - EPA 8015 C
QC Sample ID: BYH1227-MS1 QC Source Sample: 24H2214-08Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 105 50 - 150 2840 296 2430 61 1.00
Matrix Spike Dup - EPA 8015 C
QC Sample ID: BYH1227-MSD1 QC Source Sample: 24H2214-08Batch: BYH1227
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Diesel Range Organics 94.3 9.56 50 - 150 20 2580 296 2430 61 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 20 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D
QC Sample ID: BYH1199-BLK1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane ND 1.0 1.00
1,1,1-Trichloroethane ND 1.0 1.00
1,1,2,2-Tetrachloroethane ND 1.0 1.00
1,1,2-Trichloroethane ND 1.0 1.00
1,1,2-Trichlorotrifluoroethane ND 1.0 1.00
1,1-Dichloroethane ND 1.0 1.00
1,1-Dichloroethene ND 1.0 1.00
1,1-Dichloropropene ND 1.0 1.00
1,2,3-Trichlorobenzene ND 1.0 1.00
1,2,3-Trichloropropane ND 1.0 1.00
1,2,4-Trichlorobenzene ND 1.0 1.00
1,2,4-Trimethylbenzene ND 1.0 1.00
1,2-Dibromo-3-chloropropane ND 1.0 1.00
1,2-Dibromoethane (EDB)ND 1.0 1.00
1,2-Dichlorobenzene ND 1.0 1.00
1,2-Dichloroethane ND 1.0 1.00
1,2-Dichloropropane ND 1.0 1.00
1,3,5-Trimethylbenzene ND 1.0 1.00
1,3-Dichlorobenzene ND 1.0 1.00
1,3-Dichloropropane ND 1.0 1.00
1,4-Dichlorobenzene ND 1.0 1.00
2,2-Dichloropropane ND 1.0 1.00
2-Chlorotoluene ND 1.0 1.00
2-Hexanone ND 10.0 1.00
2-Nitropropane ND 2.0 1.00
4-Chlorotoluene ND 1.0 1.00
Acetone ND 20.0 1.00
Acrylonitrile ND 5.0 1.00
Benzene ND 0.4 1.00
Bromobenzene ND 1.0 1.00
Bromochloromethane ND 1.0 1.00
Bromodichloromethane ND 1.0 1.00
Bromoform ND 1.0 1.00
Bromomethane ND 2.0 1.00
Carbon Disulfide ND 2.0 1.00
Carbon Tetrachloride ND 1.0 1.00
Chlorobenzene ND 1.0 1.00
Chloroethane ND 1.0 1.00
Chloroform ND 1.0 1.00
Chloromethane ND 1.0 1.00
cis-1,2-Dichloroethene ND 1.0 1.00
cis-1,3-Dichloropropene ND 1.0 1.00
Cyclohexanone ND 10.0 1.00
Dibromochloromethane ND 1.0 1.00
Dibromomethane ND 1.0 1.00
Dichlorodifluoromethane ND 1.0 1.00
Ethyl Acetate ND 2.0 1.00
Ethyl Ether ND 1.0 1.00
Ethylbenzene ND 1.0 1.00
Hexachlorobutadiene ND 1.0 1.00
Isobutanol ND 20.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 21 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - EPA 8260D (cont.)
QC Sample ID: BYH1199-BLK1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Isopropylbenzene ND 1.0 1.00
Methyl Ethyl Ketone ND 2.0 1.00
Methyl Isobutyl Ketone ND 5.0 1.00
Methylene Chloride ND 1.0 1.00
Methyl-tert-butyl ether (MTBE)ND 0.6 1.00
Naphthalene ND 1.0 1.00
n-Butyl Alcohol ND 50.0 1.00
n-Butylbenzene ND 1.0 1.00
n-Propyl Benzene ND 1.0 1.00
Pentachloroethane ND 1.0 1.00
p-Isopropyltoluene ND 1.0 1.00
sec-Butyl Benzene ND 1.0 1.00
Styrene ND 1.0 1.00
tert-Butylbenzene ND 1.0 1.00
Tetrachloroethene ND 1.0 1.00
Toluene ND 1.0 1.00
trans-1,2-Dichloroethene ND 1.0 1.00
trans-1,3-Dichloropropene ND 1.0 1.00
Trichloroethene ND 1.0 1.00
Trichlorofluoromethane ND 1.0 1.00
Vinyl Chloride ND 0.8 1.00
Xylenes, total ND 3.0 1.00
QC Sample ID: BYH1214-BLK1 Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene ND 0.0004 1.00
Ethylbenzene ND 0.001 1.00
Methyl tert-Butyl Ether (MTBE)ND 0.0006 1.00
Naphthalene ND 0.001 1.00
Toluene ND 0.001 1.00
Xylenes, total ND 0.003 1.00
LCS - EPA 8260D
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 111 70 - 130 11.1 10.0 1.0 1.00
1,1,1-Trichloroethane 117 70 - 130 11.7 10.0 1.0 1.00
1,1,2,2-Tetrachloroethane 106 70 - 130 10.6 10.0 1.0 1.00
1,1,2-Trichloroethane 102 70 - 130 10.2 10.0 1.0 1.00
1,1,2-Trichlorotrifluoroethane 120 70 - 130 12.0 10.0 1.0 1.00
1,1-Dichloroethane 120 70 - 130 12.0 10.0 1.0 1.00
1,1-Dichloroethene 107 70 - 130 10.7 10.0 1.0 1.00
1,1-Dichloropropene 111 70 - 130 11.1 10.0 1.0 1.00
1,2,3-Trichlorobenzene 120 70 - 130 12.0 10.0 1.0 1.00
1,2,3-Trichloropropane 115 70 - 130 11.5 10.0 1.0 1.00
1,2,4-Trichlorobenzene 110 70 - 130 11.0 10.0 1.0 1.00
1,2,4-Trimethylbenzene 110 70 - 130 11.0 10.0 1.0 1.00
1,2-Dibromo-3-chloropropane 110 70 - 130 11.0 10.0 1.0 1.00
1,2-Dibromoethane (EDB)106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dichlorobenzene 111 70 - 130 11.1 10.0 1.0 1.00
1,2-Dichloroethane 106 70 - 130 10.6 10.0 1.0 1.00
1,2-Dichloropropane 106 70 - 130 10.6 10.0 1.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 22 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,3,5-Trimethylbenzene 109 70 - 130 10.9 10.0 1.0 1.00
1,3-Dichlorobenzene 117 70 - 130 11.7 10.0 1.0 1.00
1,3-Dichloropropane 114 70 - 130 11.4 10.0 1.0 1.00
1,4-Dichlorobenzene 106 70 - 130 10.6 10.0 1.0 1.00
2,2-Dichloropropane 112 70 - 130 11.2 10.0 1.0 1.00
2-Chlorotoluene 114 70 - 130 11.4 10.0 1.0 1.00
2-Hexanone 132 70 - 130 13.2 10.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
2-Nitropropane 49.2 70 - 130 14.8 30.0 2.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
4-Chlorotoluene 114 70 - 130 11.4 10.0 1.0 1.00
Acetone 95.5 70 - 130 95.5 100 20.0 1.00
Acrylonitrile 108 70 - 130 53.9 50.0 5.0 1.00
Benzene 112 70 - 130 11.2 10.0 0.4 1.00
Bromobenzene 109 70 - 130 10.9 10.0 1.0 1.00
Bromochloromethane 116 70 - 130 11.6 10.0 1.0 1.00
Bromodichloromethane 98.9 70 - 130 9.89 10.0 1.0 1.00
Bromoform 109 70 - 130 10.9 10.0 1.0 1.00
Bromomethane 176 70 - 130 17.6 10.0 2.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 139 70 - 130 13.9 10.0 2.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Tetrachloride 114 70 - 130 11.4 10.0 1.0 1.00
Chlorobenzene 109 70 - 130 10.9 10.0 1.0 1.00
Chloroethane 124 70 - 130 12.4 10.0 1.0 1.00
Chloroform 108 70 - 130 10.8 10.0 1.0 1.00
Chloromethane 146 70 - 130 14.6 10.0 1.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
cis-1,2-Dichloroethene 113 70 - 130 11.3 10.0 1.0 1.00
cis-1,3-Dichloropropene 108 70 - 130 10.8 10.0 1.0 1.00
Cyclohexanone 34.5 70 - 130 34.5 100 10.0 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Dibromochloromethane 115 70 - 130 11.5 10.0 1.0 1.00
Dibromomethane 112 70 - 130 11.2 10.0 1.0 1.00
Dichlorodifluoromethane 143 70 - 130 14.3 10.0 1.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Ethyl Acetate 102 70 - 130 20.4 20.0 2.0 1.00
Ethyl Ether 108 70 - 130 10.8 10.0 1.0 1.00
Ethylbenzene 111 70 - 130 11.1 10.0 1.0 1.00
Hexachlorobutadiene 117 70 - 130 11.7 10.0 1.0 1.00
Isobutanol 174 70 - 130 348 200 20.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 104 70 - 130 10.4 10.0 1.0 1.00
Methyl Ethyl Ketone 151 70 - 130 15.1 10.0 2.0 1.00
J-High-L - Analyte estimated high based on LCS recovery
Methyl Isobutyl Ketone 91.6 70 - 130 9.16 10.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 23 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
LCS - EPA 8260D (cont.)
QC Sample ID: BYH1199-BS1 Batch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Methylene Chloride 104 70 - 130 10.4 10.0 1.0 1.00
Methyl-tert-butyl ether (MTBE)182 70 - 130 18.2 10.0 0.6 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 112 70 - 130 11.2 10.0 1.0 1.00
n-Butyl Alcohol 77.4 70 - 130 77.4 100 50.0 1.00
n-Butylbenzene 111 70 - 130 11.1 10.0 1.0 1.00
n-Propyl Benzene 110 70 - 130 11.0 10.0 1.0 1.00
Pentachloroethane 94.1 70 - 130 9.41 10.0 1.0 1.00
p-Isopropyltoluene 115 70 - 130 11.5 10.0 1.0 1.00
sec-Butyl Benzene 112 70 - 130 11.2 10.0 1.0 1.00
Styrene 108 70 - 130 10.8 10.0 1.0 1.00
tert-Butylbenzene 107 70 - 130 10.7 10.0 1.0 1.00
Tetrachloroethene 118 70 - 130 11.8 10.0 1.0 1.00
Toluene 100 70 - 130 10.0 10.0 1.0 1.00
trans-1,2-Dichloroethene 116 70 - 130 11.6 10.0 1.0 1.00
trans-1,3-Dichloropropene 107 70 - 130 10.7 10.0 1.0 1.00
Trichloroethene 120 70 - 130 12.0 10.0 1.0 1.00
Trichlorofluoromethane 118 70 - 130 11.8 10.0 1.0 1.00
Vinyl Chloride 162 70 - 130 16.2 10.0 0.8 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 107 70 - 130 32.2 30.0 3.0 1.00
QC Sample ID: BYH1214-BS1 Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 115 70 - 130 0.01 0.0100 0.0004 1.00
Ethylbenzene 118 70 - 130 0.01 0.0100 0.001 1.00
Methyl tert-Butyl Ether (MTBE)52.1 70 - 130 0.005 0.0100 0.0006 1.00
J-LOW-L - Estimated low due to low recovery of LCS
Naphthalene 105 70 - 130 0.01 0.0100 0.001 1.00
Toluene 112 70 - 130 0.01 0.0100 0.001 1.00
Xylenes, total 121 70 - 130 0.04 0.0300 0.003 1.00
Matrix Spike - EPA 8260D
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 108 70 - 130 54.0 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 106 70 - 130 53.2 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 106 70 - 130 52.8 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 106 70 - 130 53.2 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 112 70 - 130 56.2 ND 50.0 5.0 1.00
1,1-Dichloroethane 111 70 - 130 55.3 ND 50.0 5.0 1.00
1,1-Dichloroethene 97.5 70 - 130 48.8 ND 50.0 5.0 1.00
1,1-Dichloropropene 104 70 - 130 52.2 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 110 70 - 130 55.1 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 117 70 - 130 58.6 ND 50.0 5.0 1.00
1,2,4-Trichlorobenzene 99.3 70 - 130 49.6 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 106 70 - 130 53.0 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 100 70 - 130 50.2 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)110 70 - 130 54.9 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 107 70 - 130 53.4 ND 50.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 24 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,2-Dichloroethane 107 70 - 130 53.4 ND 50.0 5.0 1.00
1,2-Dichloropropane 102 70 - 130 50.8 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 99.0 70 - 130 49.5 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 109 70 - 130 54.6 ND 50.0 5.0 1.00
1,3-Dichloropropane 116 70 - 130 58.2 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 103 70 - 130 51.6 ND 50.0 5.0 1.00
2,2-Dichloropropane 99.4 70 - 130 49.7 ND 50.0 5.0 1.00
2-Chlorotoluene 107 70 - 130 53.3 ND 50.0 5.0 1.00
2-Hexanone 132 70 - 130 65.8 ND 50.0 50.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
2-Nitropropane 53.4 70 - 130 80.1 ND 150 10.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
4-Chlorotoluene 105 70 - 130 52.4 ND 50.0 5.0 1.00
Acetone 89.6 70 - 130 448 ND 500 100 1.00
Acrylonitrile 109 70 - 130 271 ND 250 25.0 1.00
Benzene 108 70 - 130 54.0 ND 50.0 2.0 1.00
Bromobenzene 102 70 - 130 51.2 ND 50.0 5.0 1.00
Bromochloromethane 114 70 - 130 57.0 ND 50.0 5.0 1.00
Bromodichloromethane 98.8 70 - 130 49.4 ND 50.0 5.0 1.00
Bromoform 115 70 - 130 57.3 ND 50.0 5.0 1.00
Bromomethane 167 70 - 130 83.7 ND 50.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 128 70 - 130 64.1 ND 50.0 10.0 1.00
Carbon Tetrachloride 106 70 - 130 53.0 ND 50.0 5.0 1.00
Chlorobenzene 105 70 - 130 52.7 ND 50.0 5.0 1.00
Chloroethane 116 70 - 130 58.0 ND 50.0 5.0 1.00
Chloroform 102 70 - 130 51.2 ND 50.0 5.0 1.00
Chloromethane 135 70 - 130 67.4 ND 50.0 5.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
cis-1,2-Dichloroethene 105 70 - 130 52.7 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 98.7 70 - 130 49.4 ND 50.0 5.0 1.00
Cyclohexanone 25.2 70 - 130 126 ND 500 50.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Dibromochloromethane 113 70 - 130 56.4 ND 50.0 5.0 1.00
Dibromomethane 112 70 - 130 56.1 ND 50.0 5.0 1.00
Dichlorodifluoromethane 129 70 - 130 64.5 ND 50.0 5.0 1.00
Ethyl Acetate 107 70 - 130 107 ND 100 10.0 1.00
Ethyl Ether 103 70 - 130 51.6 ND 50.0 5.0 1.00
Ethylbenzene 106 70 - 130 53.2 ND 50.0 5.0 1.00
Hexachlorobutadiene 107 70 - 130 53.5 ND 50.0 5.0 1.00
Isobutanol 147 70 - 130 1470 ND 1000 100 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 99.2 70 - 130 49.6 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 159 70 - 130 79.4 ND 50.0 10.0 1.00
MS-High - Estimated high due to Matrix Spike recovery.
Methyl Isobutyl Ketone 112 70 - 130 55.8 ND 50.0 25.0 1.00
Methylene Chloride 97.1 70 - 130 48.6 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)192 70 - 130 95.9 ND 50.0 3.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 25 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike - EPA 8260D (cont.)
QC Sample ID: BYH1199-MS1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 104 70 - 130 51.8 ND 50.0 5.0 1.00
n-Butyl Alcohol 84.5 70 - 130 422 ND 500 250 1.00
n-Butylbenzene 98.4 70 - 130 49.2 ND 50.0 5.0 1.00
n-Propyl Benzene 103 70 - 130 51.6 ND 50.0 5.0 1.00
Pentachloroethane 93.7 70 - 130 46.8 ND 50.0 5.0 1.00
p-Isopropyltoluene 103 70 - 130 51.7 ND 50.0 5.0 1.00
sec-Butyl Benzene 102 70 - 130 50.8 ND 50.0 5.0 1.00
Styrene 105 70 - 130 52.3 ND 50.0 5.0 1.00
tert-Butylbenzene 102 70 - 130 50.8 ND 50.0 5.0 1.00
Tetrachloroethene 106 70 - 130 53.2 ND 50.0 5.0 1.00
Toluene 97.9 70 - 130 49.0 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 107 70 - 130 53.5 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 104 70 - 130 52.0 ND 50.0 5.0 1.00
Trichloroethene 115 70 - 130 57.4 ND 50.0 5.0 1.00
Trichlorofluoromethane 110 70 - 130 55.0 ND 50.0 5.0 1.00
Vinyl Chloride 150 70 - 130 75.2 ND 50.0 4.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 102 70 - 130 154 ND 150 15.0 1.00
QC Sample ID: BYH1214-MS1 QC Source Sample: 24H2214-08Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 101 70 - 130 3.06 ND 3.03 0.12 1.00
Ethylbenzene 102 50 - 150 3.10 ND 3.03 0.30 1.00
Methyl tert-Butyl Ether (MTBE)55.4 50 - 150 1.68 ND 3.03 0.18 1.00
Naphthalene 102 50 - 150 3.11 ND 3.03 0.30 1.00
Toluene 98.3 70 - 130 2.98 ND 3.03 0.30 1.00
Xylenes, total 107 70 - 130 9.72 ND 9.10 0.91 1.00
QC Sample ID: BYH1214-MS2 QC Source Sample: XXXXXXX-XXBatch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 103 70 - 130 0.28 ND 0.271 0.01 1.00
Ethylbenzene 101 50 - 150 0.27 ND 0.271 0.03 1.00
Methyl tert-Butyl Ether (MTBE)55.6 50 - 150 0.15 ND 0.271 0.02 1.00
Naphthalene 110 50 - 150 0.30 ND 0.271 0.03 1.00
Toluene 100 70 - 130 0.27 ND 0.271 0.03 1.00
Xylenes, total 106 70 - 130 0.86 ND 0.813 0.08 1.00
Matrix Spike Dup - EPA 8260D
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,1,1,2-Tetrachloroethane 108 0.278 70 - 130 20 53.9 ND 50.0 5.0 1.00
1,1,1-Trichloroethane 101 5.41 70 - 130 20 50.4 ND 50.0 5.0 1.00
1,1,2,2-Tetrachloroethane 106 0.754 70 - 130 20 53.2 ND 50.0 5.0 1.00
1,1,2-Trichloroethane 102 4.12 70 - 130 20 51.0 ND 50.0 5.0 1.00
1,1,2-Trichlorotrifluoroethane 106 5.86 70 - 130 20 53.0 ND 50.0 5.0 1.00
1,1-Dichloroethane 104 6.34 70 - 130 20 51.9 ND 50.0 5.0 1.00
1,1-Dichloroethene 89.7 8.33 70 - 130 20 44.8 ND 50.0 5.0 1.00
1,1-Dichloropropene 99.2 5.20 70 - 130 20 49.6 ND 50.0 5.0 1.00
1,2,3-Trichlorobenzene 115 4.26 70 - 130 20 57.5 ND 50.0 5.0 1.00
1,2,3-Trichloropropane 117 0.0854 70 - 130 20 58.6 ND 50.0 5.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 26 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
1,2,4-Trichlorobenzene 105 5.68 70 - 130 20 52.6 ND 50.0 5.0 1.00
1,2,4-Trimethylbenzene 101 5.02 70 - 130 20 50.4 ND 50.0 5.0 1.00
1,2-Dibromo-3-chloropropane 107 6.64 70 - 130 20 53.6 ND 50.0 5.0 1.00
1,2-Dibromoethane (EDB)111 1.09 70 - 130 20 55.5 ND 50.0 5.0 1.00
1,2-Dichlorobenzene 104 2.56 70 - 130 20 52.1 ND 50.0 5.0 1.00
1,2-Dichloroethane 106 0.658 70 - 130 20 53.0 ND 50.0 5.0 1.00
1,2-Dichloropropane 98.5 3.00 70 - 130 20 49.2 ND 50.0 5.0 1.00
1,3,5-Trimethylbenzene 96.9 2.14 70 - 130 20 48.4 ND 50.0 5.0 1.00
1,3-Dichlorobenzene 99.4 9.49 70 - 130 20 49.7 ND 50.0 5.0 1.00
1,3-Dichloropropane 112 3.58 70 - 130 20 56.2 ND 50.0 5.0 1.00
1,4-Dichlorobenzene 118 13.4 70 - 130 20 59.0 ND 50.0 5.0 1.00
2,2-Dichloropropane 99.0 0.403 70 - 130 20 49.5 ND 50.0 5.0 1.00
2-Chlorotoluene 90.1 16.8 70 - 130 20 45.0 ND 50.0 5.0 1.00
2-Hexanone 122 7.89 70 - 130 20 60.8 ND 50.0 50.0 1.00
2-Nitropropane 60.0 11.6 70 - 130 20 90.0 ND 150 10.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
4-Chlorotoluene 104 0.767 70 - 130 20 52.0 ND 50.0 5.0 1.00
Acetone 89.4 0.268 70 - 130 20 447 ND 500 100 1.00
Acrylonitrile 108 0.647 70 - 130 20 270 ND 250 25.0 1.00
Benzene 103 4.74 70 - 130 20 51.4 ND 50.0 2.0 1.00
Bromobenzene 99.1 3.18 70 - 130 20 49.6 ND 50.0 5.0 1.00
Bromochloromethane 112 1.86 70 - 130 20 56.0 ND 50.0 5.0 1.00
Bromodichloromethane 96.4 2.46 70 - 130 20 48.2 ND 50.0 5.0 1.00
Bromoform 110 4.19 70 - 130 20 55.0 ND 50.0 5.0 1.00
Bromomethane 171 2.30 70 - 130 20 85.6 ND 50.0 10.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Carbon Disulfide 122 5.28 70 - 130 20 60.8 ND 50.0 10.0 1.00
Carbon Tetrachloride 101 4.73 70 - 130 20 50.6 ND 50.0 5.0 1.00
Chlorobenzene 105 0.285 70 - 130 20 52.6 ND 50.0 5.0 1.00
Chloroethane 107 8.25 70 - 130 20 53.4 ND 50.0 5.0 1.00
Chloroform 96.8 5.62 70 - 130 20 48.4 ND 50.0 5.0 1.00
Chloromethane 125 7.47 70 - 130 20 62.5 ND 50.0 5.0 1.00
cis-1,2-Dichloroethene 99.0 6.26 70 - 130 20 49.5 ND 50.0 5.0 1.00
cis-1,3-Dichloropropene 100 1.51 70 - 130 20 50.1 ND 50.0 5.0 1.00
Cyclohexanone 21.2 17.3 70 - 130 20 106 ND 500 50.0 1.00
MS-Low - Estimated low due to Matrix Spike recovery.
Dibromochloromethane 114 0.883 70 - 130 20 56.8 ND 50.0 5.0 1.00
Dibromomethane 110 2.34 70 - 130 20 54.8 ND 50.0 5.0 1.00
Dichlorodifluoromethane 116 10.4 70 - 130 20 58.2 ND 50.0 5.0 1.00
Ethyl Acetate 104 2.46 70 - 130 20 104 ND 100 10.0 1.00
Ethyl Ether 103 0.486 70 - 130 20 51.4 ND 50.0 5.0 1.00
Ethylbenzene 101 5.31 70 - 130 20 50.4 ND 50.0 5.0 1.00
Hexachlorobutadiene 104 2.94 70 - 130 20 52.0 ND 50.0 5.0 1.00
Isobutanol 141 4.22 70 - 130 20 1410 ND 1000 100 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Isopropylbenzene 93.4 6.02 70 - 130 20 46.7 ND 50.0 5.0 1.00
Methyl Ethyl Ketone 142 11.2 70 - 130 20 70.9 ND 50.0 10.0 1.00
MS-High - Estimated high due to Matrix Spike recovery.
Methyl Isobutyl Ketone 104 7.25 70 - 130 20 51.8 ND 50.0 25.0 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 27 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Matrix Spike Dup - EPA 8260D (cont.)
QC Sample ID: BYH1199-MSD1 QC Source Sample: XXXXXXX-XXBatch: BYH1199
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Methylene Chloride 93.9 3.35 70 - 130 20 47.0 ND 50.0 5.0 1.00
Methyl-tert-butyl ether (MTBE)202 4.93 70 - 130 20 101 ND 50.0 3.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Naphthalene 112 7.62 70 - 130 20 55.8 ND 50.0 5.0 1.00
n-Butyl Alcohol 86.4 2.32 70 - 130 20 432 ND 500 250 1.00
n-Butylbenzene 98.2 0.203 70 - 130 20 49.1 ND 50.0 5.0 1.00
n-Propyl Benzene 98.1 4.97 70 - 130 20 49.0 ND 50.0 5.0 1.00
Pentachloroethane 88.9 5.26 70 - 130 20 44.4 ND 50.0 5.0 1.00
p-Isopropyltoluene 93.0 10.6 70 - 130 20 46.5 ND 50.0 5.0 1.00
sec-Butyl Benzene 97.6 3.92 70 - 130 20 48.8 ND 50.0 5.0 1.00
Styrene 103 1.44 70 - 130 20 51.6 ND 50.0 5.0 1.00
tert-Butylbenzene 99.5 2.09 70 - 130 20 49.8 ND 50.0 5.0 1.00
Tetrachloroethene 99.3 6.81 70 - 130 20 49.6 ND 50.0 5.0 1.00
Toluene 95.8 2.17 70 - 130 20 47.9 ND 50.0 5.0 1.00
trans-1,2-Dichloroethene 99.2 7.57 70 - 130 20 49.6 ND 50.0 5.0 1.00
trans-1,3-Dichloropropene 104 0.288 70 - 130 20 52.2 ND 50.0 5.0 1.00
Trichloroethene 108 6.65 70 - 130 20 53.8 ND 50.0 5.0 1.00
Trichlorofluoromethane 98.8 10.7 70 - 130 20 49.4 ND 50.0 5.0 1.00
Vinyl Chloride 140 6.81 70 - 130 20 70.2 ND 50.0 4.0 1.00
HB - Recovery for this parameter exceeded the upper acceptance limit. Associated sample(s) were all non-detect and therefore
accepted and reported for this parameter.
Xylenes, total 100 2.27 70 - 130 20 150 ND 150 15.0 1.00
QC Sample ID: BYH1214-MSD1 QC Source Sample: 24H2214-08Batch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 97.6 3.23 70 - 130 20 2.96 ND 3.03 0.12 1.00
Ethylbenzene 96.8 5.52 50 - 150 25 2.93 ND 3.03 0.30 1.00
Methyl tert-Butyl Ether (MTBE)59.1 6.46 50 - 150 25 1.79 ND 3.03 0.18 1.00
Naphthalene 96.6 5.93 50 - 150 25 2.93 ND 3.03 0.30 1.00
Toluene 95.0 3.41 70 - 130 20 2.88 ND 3.03 0.30 1.00
Xylenes, total 101 5.18 70 - 130 20 9.23 ND 9.10 0.91 1.00
QC Sample ID: BYH1214-MSD2 QC Source Sample: XXXXXXX-XXBatch: BYH1214
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Benzene 102 3.89 70 - 130 20 0.27 ND 0.264 0.01 1.00
Ethylbenzene 98.7 4.63 50 - 150 25 0.26 ND 0.264 0.03 1.00
Methyl tert-Butyl Ether (MTBE)57.2 0.217 50 - 150 25 0.15 ND 0.264 0.02 1.00
Naphthalene 117 3.53 50 - 150 25 0.31 ND 0.264 0.03 1.00
Toluene 98.3 4.63 70 - 130 20 0.26 ND 0.264 0.03 1.00
Xylenes, total 104 4.72 70 - 130 20 0.82 ND 0.792 0.08 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 28 of 31
QC Report for Work Order (WO) - 24H2214
% Rec RPD RPD Max MRL DFResultSpk ValueLimitsSource ConcAnalyte
Blank - SM 2540 C
QC Sample ID: BYH1211-BLK1 Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)ND 10 1.00
Duplicate - SM 2540 C
QC Sample ID: BYH1211-DUP1 QC Source Sample: XXXXXXX-XXBatch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)0.8 10 1260 1250 20 1.00
QC Sample ID: BYH1211-DUP2 QC Source Sample: 24H2214-11Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)2 10 1010 1030 20 1.00
LCS - SM 2540 C
QC Sample ID: BYH1211-BS1 Batch: BYH1211
Date Prepared: 08/23/2024 Date Analyzed: 08/23/2024
Total Dissolved Solids (TDS)102 90 - 110 408 400 20 1.00
CtF WO#: 24H2214
www.ChemtechFord.com Page 29 of 31
Surrogates Report for Work Order (WO) - 24H2214
Spk ValueResultUCL DF BatchLCL% RecAnalyteQC ID
Blank - EPA 8015 C
BYH1227-BLK1 Bromofluorobenzene 101 50 BYH1227 1.00150 203 200
BYH1227-BLK1 Capric Acid 0 BYH1227 1.0010.00 500
LCS - EPA 8015 C
BYH1227-BS1 Bromofluorobenzene 118 50 BYH1227 1.00150 236 200
BYH1227-BS1 Capric Acid 0 BYH1227 1.0010.00 500
Matrix Spike - EPA 8015 C
BYH1227-MS1 Bromofluorobenzene 100 50 BYH1227 1.00150 243 243
BYH1227-MS1 Capric Acid 0 BYH1227 1.0010.00 606
Matrix Spike Dup - EPA 8015 C
BYH1227-MSD1 Bromofluorobenzene 99.5 50 BYH1227 1.00150 241 243
BYH1227-MSD1 Capric Acid 0 BYH1227 1.0010.00 606
Blank - EPA 8260D
BYH1199-BLK1 1,2-Dichloroethane-d4 102 64.2 BYH1199 1.0012610.2 10.0
BYH1199-BLK1 4-Bromofluorobenzene 99.0 71.4 BYH1199 1.001259.90 10.0
BYH1199-BLK1 Toluene-d8 94.6 63.2 BYH1199 1.001299.46 10.0
BYH1214-BLK1 Toluene-d8 100 82 BYH1214 1.001260.0100 0.0100
LCS - EPA 8260D
BYH1199-BS1 1,2-Dichloroethane-d4 96.4 64.2 BYH1199 1.001269.64 10.0
BYH1199-BS1 4-Bromofluorobenzene 98.1 71.4 BYH1199 1.001259.81 10.0
BYH1199-BS1 Toluene-d8 91.1 63.2 BYH1199 1.001299.11 10.0
BYH1214-BS1 Toluene-d8 99.9 82 BYH1214 1.001260.00999 0.0100
Matrix Spike - EPA 8260D
BYH1199-MS1 1,2-Dichloroethane-d4 100 64.2 BYH1199 1.0012650.1 50.0
BYH1199-MS1 4-Bromofluorobenzene 95.5 71.4 BYH1199 1.0012547.8 50.0
BYH1199-MS1 Toluene-d8 92.8 63.2 BYH1199 1.0012946.4 50.0
BYH1214-MS1 Toluene-d8 101 82 BYH1214 1.001263.06 3.03
BYH1214-MS2 Toluene-d8 102 82 BYH1214 1.001260.276 0.271
Matrix Spike Dup - EPA 8260D
BYH1199-MSD1 1,2-Dichloroethane-d4 102 64.2 BYH1199 1.0012650.9 50.0
BYH1199-MSD1 4-Bromofluorobenzene 98.8 71.4 BYH1199 1.0012549.4 50.0
BYH1199-MSD1 Toluene-d8 91.8 63.2 BYH1199 1.0012945.9 50.0
BYH1214-MSD1 Toluene-d8 101 82 BYH1214 1.001263.07 3.03
BYH1214-MSD2 Toluene-d8 101 82 BYH1214 1.001260.268 0.264
CtF WO#: 24H2214
www.ChemtechFord.com Page 30 of 31
UCLLCL%RecResultAnalyteLabNumber
Surrogate Recoveries (Field Samples)
SpkLvl Qualifier
DRO with silica gel cleanup
24H2214-08 Capric Acid 0.00 0 1606
24H2214-08 Bromofluorobenzene 165 68.2 50 150243
MBTEXN-GRO
24H2214-08 Toluene-d8 3.08 102 82 1263.03
8260 Low Level Volatiles
24H2214-10 Toluene-d8 9.56 95.6 63.2 12910.0
24H2214-10 4-Bromofluorobenzene 9.61 96.1 71.4 12510.0
24H2214-10 1,2-Dichloroethane-d4 10.2 102 64.2 12610.0
CtF WO#: 24H2214
www.ChemtechFord.com Page 31 of 31

Appendix K
Data Validation Reports

Data Validation Report

Sample Delivery Group (SDG): 24F1419, 24H0986, 24H1461, 24H1665, 24H1959, 24H2214, 24I1821,
24J0550
Laboratory: Chemtech-Ford Analytical, Salt Lake City, Utah
Project/Site Name: Former Sommers Auto, Job # 2469-002F
AQS Report Date: 12/2/2024
Matrix: Water & Soil
Validation Level: Level III
Validated By: J. Workman

1.0 Introduction

This Sample Delivery Group (SDG) includes the samples listed below.

Sample ID Lab ID Matrix Sample Date VO
C
/
G
R
O

82
6
0
D
,

8
0
1
5

SV
O
C
/
D
R
O
/
O
&
G

82
7
0
,

8
0
1
5
C
,

1
6
6
4
B

Me
t
a
l
s

60
1
0
,

6
0
2
0
,

7
4
7
X

Ot
h
e
r

TP - 1 (2'-3') 24F1419-01 Solid 6/17/2024 x x
TP - 2 ( 5'-6') 24F1419-02 Solid 6/17/2024 x x
TP - 3 ( 2'-3') 24F1419-03 Solid 6/17/2024 x x
TP - 4 ( 2'-3') 24F1419-04 Solid 6/17/2024 x x
TP - 5 ( 4'-5') 24F1419-05 Solid 6/17/2024 x x
TP - 6 ( 4'-5') 24F1419-06 Solid 6/17/2024 x x
TP - 60 ( 4'-5') 24F1419-07 Solid 6/17/2024 x x
DU-1 24F1419-08 Solid 6/17/2024 x
DU-2 24F1419-09 Solid 6/17/2024 x
DU-10 24F1419-10 Solid 6/17/2024 x
Test Pit WCS 24F1419-11 Solid/Ext 6/17/2024 x
EXC 1-3 WCS 24F1419-12 Solid/Ext 6/17/2024 x x
Trip Blank 24F1419-13 Water 6/17/2024 x
Equip Blank 24F1419-14 Water 6/17/2024 x x x
AQS, Inc. Data Validation Report

Page 2
Sample ID Lab ID Matrix Sample Date VO
C
/
G
R
O

82
6
0
D
,

8
0
1
5

SV
O
C
/
D
R
O
/
O
&
G

82
7
0
,

8
0
1
5
C
,

1
6
6
4
B

Me
t
a
l
s

60
1
0
,

6
0
2
0
,

7
4
7
X

Ot
h
e
r

EXC-4-SW 24H0986-01 Solid 8/7/2024 x x
EXC-4-SE 24H0986-02 Solid 8/12/2024 x x
EXC-4-West 1 24H0986-03 Solid 8/12/2024 x x
Trip Blank 24H0986-04 Water 8/7/2024 x x

EXC-4-Floor1 24H1461-01 Solid 8/13/2024 x x
EXC-4-Floor2 24H1461-02 Solid 8/13/2024 x x
EXC-4-East1 24H1461-03 Solid 8/14/2024 x x
EXC-4-East10 24H1461-04 Solid 8/14/2024 x x
EXC-4-West2 24H1461-05 Solid 8/15/2024 x x
EXC-4-NW 24H1461-06 Solid 8/15/2024 x x
EXC-4-Floor3 24H1461-07 Solid 8/15/2024 x x
EXC-4-West3 24H1461-08 Solid 8/15/2024 x x
Trip Blank 24H1461-09 Water 8/13/2024 x x

EXC-4-West 4 24H1665-01 Solid 8/19/2024 x x
EXC-4- NE 24H1665-02 Solid 8/19/2024 x x
EXC-4- East 2 24H1665-03 Solid 8/19/2024 x x
EXC-4- Floor 4 24H1665-04 Solid 8/19/2024 x x
EXC-4- Floor 40 24H1665-05 Solid 8/19/2024 x x
EXC-4- Floor 5 24H1665-06 Solid 8/19/2024 x x
EXC-4-GW1 24H1665-07 Water 8/19/2024 x x
EXC-4-GW2 24H1665-08 Water 8/19/2024 x x
Trip Blank 24H1665-09 Water 8/19/2024 x x
Equip Blank 24H1665-10 Water 8/19/2024 x x

EXC-2-N 24H1959-01 Solid 8/20/2024 x
EXC-2-E 24H1959-02 Solid 8/20/2024 x
EXC-2-SE 24H1959-03 Solid 8/20/2024 x
EXC-2-S 24H1959-04 Solid 8/20/2024 x
EXC-2-W 24H1959-05 Solid 8/20/2024 x
EXC-2-Floor 24H1959-06 Solid 8/20/2024 x
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Sample ID Lab ID Matrix Sample Date VO
C
/
G
R
O

82
6
0
D
,

8
0
1
5

SV
O
C
/
D
R
O
/
O
&
G

82
7
0
,

8
0
1
5
C
,

1
6
6
4
B

Me
t
a
l
s

60
1
0
,

6
0
2
0
,

7
4
7
X

Ot
h
e
r

EXC-2-W2 24H1959-07 Solid 8/20/2024 x
Frac Tank 24H1959-08 Water 8/21/2024 x x x x

EXC-3-N 24H2214-01 Solid 8/22/2024 x
EXC-3-E 24H2214-02 Solid 8/22/2024 x
EXC-3-S 24H2214-03 Solid 8/22/2024 x
EXC-3-W 24H2214-04 Solid 8/22/2024 x
EXC-3-Floor 24H2214-05 Solid 8/22/2024 x
EXC-3-Floor 10 24H2214-06 Solid 8/22/2024 x
Equip Blank 24H2214-07 Water 8/22/2024 x
EXC-4-NE2 24H2214-08 Solid 8/22/2024 x x
EXC-1-Comp 24H2214-09 Solid 8/22/2024 x
Trip Blank 24H2214-10 Water 8/22/2024 x
Frack Tank 2 24H2214-11 Water 8/23/2024 x x

EXC-1-1 24I1821-01 Solid 9/20/2024 x
EXC-1-2 24I1821-02 Solid 9/20/2024 x
EXC-1-3 24I1821-03 Solid 9/20/2024 x
EXC-1-4 24I1821-04 Solid 9/20/2024 x
EXC-1-5 24I1821-05 Solid 9/20/2024 x
EXC-1-6 24I1821-06 Solid 9/20/2024 x
EXC-1-7 24I1821-07 Solid 9/20/2024 x
EXC-1-8 24I1821-08 Solid 9/20/2024 x
EXC-1-9 24I1821-09 Solid 9/20/2024 x
EXC-1-10 24I1821-10 Solid 9/20/2024 x
EXC-1-11 24I1821-11 Solid 9/20/2024 x
EXC-1-12 24I1821-12 Solid 9/20/2024 x
EXC-1-13 24I1821-13 Solid 9/20/2024 x
EXC-1-130 24I1821-14 Solid 9/20/2024 x
EXC-1-14 24I1821-15 Solid 9/20/2024 x
EXC-1-15 24I1821-16 Solid 9/20/2024 x
EXC-1-16 24I1821-17 Solid 9/20/2024 x
EXC-1-160 24I1821-18 Solid 9/20/2024 x
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Sample ID Lab ID Matrix Sample Date VO
C
/
G
R
O

82
6
0
D
,

8
0
1
5

SV
O
C
/
D
R
O
/
O
&
G

82
7
0
,

8
0
1
5
C
,

1
6
6
4
B

Me
t
a
l
s

60
1
0
,

6
0
2
0
,

7
4
7
X

Ot
h
e
r

MW-6 24J0550-01 Water 10/7/2024 x x
MW-7 24J0550-02 Water 10/7/2024 x x
MW-70 24J0550-03 Water 10/7/2024 x x
Trip Blank 24J0550-04 Water 10/7/2024 x
Equip Blank 24J0550-05 Water 10/7/2024 x x
Note: Highlighted samples are field duplicates.

1.1 Project Overview

Data validation was based on the US Environmental Protection Agency’s National Functional Guidelines
for Organic and Inorganic Data Review (EPA 1999 and 2004), the referenced EPA methods and project-
specific control limits, where applicable. Where specific guidance is not available, the data has been
evaluated in a conservative manner consistent with industry standards using professional experience.

This review was based exclusively on data reports, Quality Control (QC) summaries and raw data
provided by the laboratory. The following are definitions of the data qualifiers, in addition to the
laboratory qualifiers, that may be used in this report.

J+ Data are qualified as estimated, with a high bias likely to occur. False positives or false
negatives are unlikely to have been reported.
J- Data are qualified as estimated, with a low bias likely to occur. False positives or false negatives
are unlikely to have been reported.
J Data are qualified as estimated; it is not possible to assess the direction of the potential bias.
False positives or false negatives are unlikely to have been reported.
R Data are qualified as rejected. There is a significant potential for the reporting of false
negatives or false positives.
UJ Indicates the compound or analyte was analyzed for but not detected. The sample detection
limit is an estimated value.
B The compound or analyte was found in an associated blank as well as in the sample.
None Indicates the data was not significantly impacted by the finding, therefore qualification was not
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required.

2.0 Data Review

2.1 Sample Receipt

Copies of the chain-of-custody (COC) forms were included in the laboratory data package. COCs were
reviewed for accuracy, completeness, and evidence of correct sample preservation. No sample receipt
problems were noted.

2.2 Holding Times

All samples were analyzed within required holding times.

2.3 Reporting Levels

The data user should ensure that all reporting levels meet project requirements. All samples were run
undiluted, at normal laboratory reporting levels, with the following exceptions:

Sample(s) Analyte(s) Notes Qualifiers
Test Pit WCS Selenium, Total These analytes were reported as
non-detect but were run diluted –
elevating the detection limit.

The data user should ensure that
detection limits for non-detect
results meet project
requirements.
None required
TP - 3 ( 2'-3')
TP - 4 ( 2'-3')
DU-1
DU-2
DU-10
8270 TPH Fractionation
(several ND analytes run at
20x dilution)
These analytes were reported as
non-detect but were run diluted –
elevating the detection limit.

The data user should ensure that
detection limits for non-detect
results meet project
requirements.
None required
24H1461
EXC-4-West2
EXC-4-West3
8270 TPH Fractionation
(several ND analytes run at
10x dilution)
These analytes were reported as
non-detect but were run diluted –
elevating the detection limit.

The data user should ensure that
None required
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detection limits for non-detect
results meet project
requirements.

2.4 Initial and Continuing Calibration

The laboratory did not provide initial or continuing calibration information. It is assumed that all initial
and ongoing calibration requirements were met.

2.5 Blanks

Field and method blanks were free of contamination.

Sample(s) Analyte(s) Notes Qualifiers
TP - 1 (2'-3')
TP - 2 ( 5'-6')
TP - 3 ( 2'-3')
TP - 4 ( 2'-3')
TP - 5 ( 4'-5')
TP - 6 ( 4'-5')
TP - 60 ( 4'-5')
DU-1
DU-2
DU-10
Test Pit WCS
EXC 1-3 WCS
Bromodichloromethane
10.7
Chloroform 40.2
Dibromochloromethane 2.2
These analytes were detected in
the trip blank at the levels
indicated.
Flag detects as
estimated (J)
TP - 1 (2'-3')
TP - 2 ( 5'-6')
TP - 3 ( 2'-3')
TP - 4 ( 2'-3')
TP - 5 ( 4'-5')
TP - 6 ( 4'-5')
TP - 60 ( 4'-5')
DU-1
DU-2
DU-10
Test Pit WCS
EXC 1-3 WCS
C11-12 Aliphatic
hydrocarbons 54
C13-C16 Aliphatic
hydrocarbons 655
C17-C21 Aliphatic
hydrocarbons 60
C22-C35 Aliphatic
hydrocarbons 596
These analytes were detected in
the equipment blank at the levels
indicated.
Flag detects as
estimated (J)
EXC-2-N
EXC-2-E
EXC-2-SE
Arsenic, Total 0.106
Lead, Total 0.110
These analytes were detected in
the method blank at the levels
indicated.
Flag low-level
detects as
estimated (J)
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EXC-2-S
EXC-2-W
EXC-2-Floor
EXC-2-W2
EXC-3-N
EXC-3-E
EXC-3-S
EXC-3-W
EXC-3-Floor
EXC-3-Floor 10
Equipment
Blank
EXC-4-NE2
EXC-1-Comp
Frack Tank 2
Bromodichloromethane 2.4
Chloroform 8.0
These analytes were detected in
the trip blank at the levels
indicated.
Flag detects as
estimated (J)

2.6 Surrogate Recoveries

Surrogate recoveries were within method limits.

2.7 Laboratory Control Samples (LCSs)

The laboratory did not provide LCS information. The case narrative indicated that, except as noted, all
method QC requirements were met.

Sample(s) Analyte(s) Notes Qualifiers
TP - 1 (2'-3')
TP - 2 ( 5'-6')
TP - 3 ( 2'-3')
TP - 4 ( 2'-3')
TP - 5 ( 4'-5')
TP - 6 ( 4'-5')
TP - 60 ( 4'-5')
Test Pit WCS
Carbon Disulfide
2-Nitropropane
1,1,2-
Trichlorotrifluoroethane
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
24F1419
Trip Blank
Equip Blank
Methyl-tert-butyl ether
(MTBE)
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
TP - 1 (2'-3')
TP - 2 ( 5'-6')
TP - 3 ( 2'-3')
Cyclohexanone LCS recovery was high. Flag detects as
estimated (J)
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TP - 4 ( 2'-3')
TP - 5 ( 4'-5')
TP - 6 ( 4'-5')
TP - 60 ( 4'-5')
Test Pit WCS
24F1419
Trip Blank
Equip Blank
Cyclohexanone LCS recovery was high. Flag detects as
estimated (J)
EXC-4-SE
EXC-4-West 1
Bromomethane
Methyl-tert-butyl ether
(MTBE)
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
24H1461
Trip Blank
Bromomethane
Methyl-tert-butyl ether
(MTBE)
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
EXC-4-Floor1
EXC-4-Floor2
EXC-4-East1
EXC-4-East10
EXC-4-West2
EXC-4-NW
EXC-4-Floor3
EXC-4-West3
Methyl tert-Butyl Ether
(MTBE)
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
24H1461
Trip Blank
Isobutanol
2-Hexanone
LCS recovery was high. Flag detects as
estimated (J)
EXC-4- NE Methyl tert-Butyl Ether
(MTBE)
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
24H1665
Trip Blank
1,1,2-
Trichlorotrifluoroethane
1,1-Dichloroethene
1,1-Dichloropropene
2,2-Dichloropropane
2-Nitropropane
Bromomethane
Carbon Disulfide
Chloroethane
Chloromethane
cis-1,2-Dichloroethene
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
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Dichlorodifluoromethane
Methylene Chloride
Methyl-tert-butyl ether
(MTBE)
Pentachloroethane
trans-1,2-Dichloroethene
Trichlorofluoromethane
Vinyl Chloride
EXC-4- Floor 4
EXC-4- Floor 40
Benzene
Ethylbenzene
Methyl tert-Butyl Ether
(MTBE)
Naphthalene
Toluene
Xylenes, total
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
Frac Tank Methyl tert-Butyl Ether
(MTBE)
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
24H2214
Trip Blank
Cyclohexanone
2-Nitropropane
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)

EXC-4-NE2
Methyl tert-Butyl Ether
(MTBE)
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
24H2214
Trip Blank
2-Hexanone
Carbon Disulfide
Dichlorodifluoromethane
Chloromethane
Methyl Ethyl Ketone
Vinyl Chloride
Isobutanol
Bromomethane
Methyl-tert-butyl ether
(MTBE)
LCS recovery was high. Flag detects as
estimated (J)
24J0550
Trip Blank
2,2-Dichloropropane
Bromomethane
Trichlorofluoromethane
n-Butyl Alcohol
LCS recovery was low. Flag detects and
non-detects as
estimated (J and
UJ)
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1,1,2-
Trichlorotrifluoroethane

2.8 Matrix Spikes (MSs)

Matrix spike recoveries were within method limits with the following exceptions:

Sample(s) Analyte(s) Notes Qualifiers
TP - 2 ( 5'-6') 1,1,2-Trichlorotrifluoroethane
Benzene
Carbon Disulfide
Cyclohexanone
Ethylbenzene
Hexachlorobutadiene
Xylenes, total
Fluorene
Phenanthrene
MS and/or MSD recovery was
low.
Flag detects and
non-detects as
estimated (J
and UJ)
Test Pit WCS 1,1,1-Trichloroethane
1,1,2-Trichlorotrifluoroethane
1,1-Dichloroethene
2-Nitropropane
Carbon Disulfide
Carbon Tetrachloride
Chloroform
Cyclohexanone
Hexachlorobutadiene
Isobutanol
Methylene Chloride
Trichlorofluoromethane
Vinyl Chloride
Barium, Total
Selenium, Total
MS and/or MSD recovery was
low.
Flag detects and
non-detects as
estimated (J
and UJ)
TP - 2 ( 5'-6') Ethyl Acetate
Isobutanol
n-Butyl Alcohol
Tetrachloroethene
MS and/or MSD recovery was
high.
Flag detects as
estimated (J)
Test Pit WCS Mercury, Total
Trichloroethene
MS and/or MSD recovery was
high.
Flag detects as
estimated (J)
TP - 2 ( 5'-6') Xylenes, total
Cyclohexanone
Trichloroethene
MS/MSD RPD was high. Flag detects and
non-detects as
estimated (J
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and UJ)
EXC-4-Floor1
EXC-4-Floor2
EXC-4-East1
EXC-4-East10
EXC-4-West2
EXC-4-NW
EXC-4-Floor3
EXC-4-West3
N/A There were some low recoveries
for the MS/MSD associated with
this SDG, but the spiked sample
was not in this data set.
None required
EXC-4-West 4 Diesel Range Organics
Phenanthrene
Fluorene
Acenaphthene
Xylenes, total
MS and/or MSD recovery was
low, but the spiked amount was
less than 4x the sample
concentration.
None required
EXC-2-N Arsenic, Total MS and/or MSD recovery was
low, but the spiked amount was
less than 4x the sample
concentration.
None required
EXC-2-N Lead, Total MS and/or MSD recovery was
high, but the spiked amount was
less than 4x the sample
concentration.
None required
Frac Tank Methyl tert-Butyl Ether (MTBE) MS and/or MSD recovery was
low.
Flag detects and
non-detects as
estimated (J
and UJ)
EXC-3-N Arsenic, Total
Lead, Total
MS and/or MSD recovery was
high, but the spiked amount was
less than 4x the sample
concentration.
None required
EXC-1-1 Lead, Total MS and/or MSD recovery was
low, but the spiked amount was
less than 4x the sample
concentration.
None required
MW-6 Benzene MS and/or MSD recovery was
high.
Flag detects as
estimated (J)

2.9 Field Duplicates

Field duplicates are shown in Appendix 1. Duplicate recovery is only evaluated for analyte
concentrations greater than the laboratory quantitation (reporting) limit. For groundwater field
AQS, Inc. Data Validation Report

Page 12
duplicates, a calculated RPD of 20% is considered acceptable. For soil duplicates, a calculated RPD of
50% is considered acceptable. Duplicate RPDs met project requirements.

Sample(s) Analyte(s) Notes Qualifiers
TP - 6 ( 4'-5')
TP - 60 ( 4'-5')
C17-C21 Aliphatic
hydrocarbons
C22-C35 Aliphatic
hydrocarbons
Field duplicate RPD was outside
project limits for these analytes.
Flag detects and
non-detects as
estimated (J and
UJ)
DU-1
DU-10
C17-C21 Aliphatic
hydrocarbons
C22-C35 Aliphatic
hydrocarbons
Field duplicate RPD was outside
project limits for these analytes.
Flag detects and
non-detects as
estimated (J and
UJ)
EXC-4-East1
EXC-4-East10
Benzene
Gasoline Range Organics
Field duplicate RPD was outside
project limits for these analytes.
Flag detects and
non-detects as
estimated (J and
UJ)
EXC-4- Floor 4
EXC-4- Floor 40
Gasoline Range Organics
Xylenes, total
Field duplicate RPD was outside
project limits for these analytes.
Flag detects and
non-detects as
estimated (J and
UJ)
EXC-3-Floor
EXC-3-Floor 10
Lead, Total Field duplicate RPD was outside
project limits for these analytes.
Flag detects and
non-detects as
estimated (J and
UJ)
EXC-1-13
EXC-1-130
Lead, Total Field duplicate RPD was outside
project limits for these analytes.
Flag detects and
non-detects as
estimated (J and
UJ)

2.10 Other QC Elements

No other QC problems were noted.

3.0 Validation Summary

As determined by this evaluation, all analyses in these SDGs appear to have been conducted according
to method requirements. Some results have been qualified as estimated (J flags). As qualified, all data
are acceptable for use.

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APPENDIX 1. Field Duplicate Summary

TP - 6 ( 4'-5') TP - 60 ( 4'-5')
Analyte 24F1419-06 24F1419-07 Units RPD Q
Total Solids 75.6 82.4 % 9%
C5-C6 Aliphatic hydrocarbons ND ND mg/kg dry ---
C7-C8 Aliphatic hydrocarbons ND ND mg/kg dry ---
C9-C10 Aliphatic hydrocarbons ND ND mg/kg dry ---
C9-C10 Alkyl Benzenes ND ND mg/kg dry ---
Benzene ND ND mg/kg dry ---
Ethylbenzene ND ND mg/kg dry ---
Methyl tert-Butyl Ether (MTBE) ND ND mg/kg dry ---
Naphthalene ND ND mg/kg dry ---
Toluene ND ND mg/kg dry ---
Xylenes, total ND ND mg/kg dry ---
C11-12 Aliphatic hydrocarbons 0.67 0.57 mg/kg dry 16%
C13-C16 Aliphatic hydrocarbons 13.7 13.7 mg/kg dry 0%
C17-C21 Aliphatic hydrocarbons 1.66 7.07 mg/kg dry 124% J
C22-C35 Aliphatic hydrocarbons 12.1 31.8 mg/kg dry 90% J
C11-C13 Alkyl Naphthalenes ND ND mg/kg dry ---
Total C12-C22 PAH ND ND mg/kg dry ---
Acenaphthene ND ND mg/kg dry ---
Acenaphthylene ND ND mg/kg dry ---
Anthracene ND ND mg/kg dry ---
Benzo (a) anthracene ND ND mg/kg dry ---
Benzo (a) pyrene ND ND mg/kg dry ---
Benzo (b) fluoranthene ND ND mg/kg dry ---
Benzo (g,h,i) perylene ND ND mg/kg dry ---
Benzo (k) fluoranthene ND ND mg/kg dry ---
Chrysene ND ND mg/kg dry ---
Fluoranthene ND ND mg/kg dry ---
Fluorene ND ND mg/kg dry ---
Indeno (1,2,3-cd) pyrene ND ND mg/kg dry ---
Phenanthrene ND ND mg/kg dry ---
Pyrene ND ND mg/kg dry ---

DU-1 DU-10
Analyte 24F1419-08 24F1419-10 Units RPD Q
Total Solids 99.8 100 % 0%
C11-12 Aliphatic hydrocarbons 5.11 5.79 mg/kg dry 12%
C13-C16 Aliphatic hydrocarbons 149 167 mg/kg dry 11%
C17-C21 Aliphatic hydrocarbons 44.5 121 mg/kg dry 92% J
C22-C35 Aliphatic hydrocarbons 262 695 mg/kg dry 90% J
C11-C13 Alkyl Naphthalenes ND ND mg/kg dry ---
Total C12-C22 PAH ND ND mg/kg dry ---
Acenaphthene ND ND mg/kg dry ---
Acenaphthylene ND ND mg/kg dry ---
Anthracene ND ND mg/kg dry ---
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Benzo (a) anthracene ND ND mg/kg dry ---
Benzo (a) pyrene ND ND mg/kg dry ---
Benzo (b) fluoranthene ND ND mg/kg dry ---
Benzo (g,h,i) perylene ND ND mg/kg dry ---
Benzo (k) fluoranthene ND ND mg/kg dry ---
Chrysene ND ND mg/kg dry ---
Fluoranthene ND ND mg/kg dry ---
Fluorene ND ND mg/kg dry ---
Indeno (1,2,3-cd) pyrene ND ND mg/kg dry ---
Phenanthrene ND ND mg/kg dry ---
Pyrene ND ND mg/kg dry ---

EXC-4-East1 EXC-4-East10
Analyte 24H1461-03 24H1461-04 Units RPD Q
Total Solids 79.2 80.3 % 1%
Diesel Range Organics ND ND mg/kg dry ---
Benzene 0.04 0.02 mg/kg dry 67% J
Ethylbenzene ND ND mg/kg dry ---
Methyl tert-Butyl Ether (MTBE) 0.02 0.01 mg/kg dry 67% <4x
Naphthalene ND ND mg/kg dry ---
Toluene ND ND mg/kg dry ---
Xylenes, total ND ND mg/kg dry ---
Gasoline Range Organics 0.33 0.17 mg/kg dry 64% J

EXC-4- Floor 4 EXC-4- Floor 40
Analyte 24H1665-04 24H1665-05 Units RPD Q
Total Solids 78.8 79.8 % 1%
Diesel Range Organics ND ND mg/kg dry ---
Gasoline Range Organics 0.889 0.154 mg/kg dry 141% J
Benzene ND ND mg/kg dry ---
Ethylbenzene 0.008 ND mg/kg dry ---
Methyl tert-Butyl Ether (MTBE) 0.004 0.005 mg/kg dry 22%
Naphthalene 0.01 ND mg/kg dry ---
Toluene ND ND mg/kg dry ---
Xylenes, total 0.07 0.02 mg/kg dry 111% J

EXC-2-W EXC-2-W2
Analyte 24H1959-05 24H1959-07 Units RPD Q
Total Solids 94.4 94.5 % 0%
Arsenic, Total 16.8 13.9 mg/kg dry 19%
Lead, Total 352 293 mg/kg dry 18%

EXC-3-Floor EXC-3-Floor 10
Analyte 24H2214-05 24H2214-06 Units RPD Q
Total Solids 86.6 84.7 % 2%
Arsenic, Total 11.0 11.6 mg/kg dry 5%
Lead, Total 47.5 107 mg/kg dry 77% J

AQS, Inc. Data Validation Report

Page 15
EXC-1-13 EXC-1-130
Analyte 24I1821-13 24I1821-14 Units RPD Q
Total Solids 98.0 97.5 % 1%
Lead, Total 303 420 mg/kg dry 32% J

EXC-1-16 EXC-1-160
Analyte 24I1821-17 24I1821-18 Units RPD Q
Total Solids 96.9 98.1 % 1%
Lead, Total 188 213 mg/kg dry 12%

MW-7 MW-70
Analyte 24J0550-02 24J0550-03 Units RPD Q
Bromofluorobenzene 2.79 2.92 mg/L 5%
Diesel Range Organics 1.4 1.2 mg/L 15%
Gasoline Range Organics 1.78 1.73 mg/L 3%
Benzene ND ND mg/L ---
Ethylbenzene 0.055 0.055 mg/L 0%
Methyl tert-Butyl Ether (MTBE) ND ND mg/L ---
Naphthalene 0.048 0.041 mg/L 16%
Toluene ND ND mg/L ---
Xylenes, total 0.190 0.168 mg/L 12%
Note: <4x = sample concentration was less than 4x the detection limit.

Data Validation Report

Sample Delivery Group (SDG): L1766673, L1770255, L1771052, L1771237
Laboratory: Pace Analytical, Mount Juliet, TN
Project/Site Name: Former Sommers Auto, Job # 2469-002F
AQS Report Date: 12/3/2024
Matrix: Soil
Validation Level: Level III
Validated By: J. Workman

1.0 Introduction

This Sample Delivery Group (SDG) includes the samples listed below.

Sample ID Lab ID Matrix Sample Date VO
C
/
G
R
O

82
6
0
D
,

8
0
1
5

SV
O
C
/
D
R
O
/
O
&
G

82
7
0
,

8
0
1
5
C
,

1
6
6
4
B

Me
t
a
l
s

60
1
0
,

6
0
2
0
,

7
4
7
X

Ot
h
e
r

EXC-4 L1766673-01 SS 8/12/2024 x
EXC- L1766673-02 SS 8/12/2024 x

EXC-2 L1770255-01 SS 8/21/2024 x

EXC-3 L1771052-01 SS 8/22/2024 x

EXC-1 L1771237-01 SS 8/23/2024 x
Note: Highlighted samples are field duplicates.

1.1 Project Overview

Data validation was based on the US Environmental Protection Agency’s National Functional Guidelines
for Organic and Inorganic Data Review (EPA 1999 and 2004), the referenced EPA methods and project-
AQS, Inc. Data Validation Report

Page 2
specific control limits, where applicable. Where specific guidance is not available, the data has been
evaluated in a conservative manner consistent with industry standards using professional experience.

This review was based exclusively on data reports, Quality Control (QC) summaries and raw data
provided by the laboratory. The following are definitions of the data qualifiers, in addition to the
laboratory qualifiers, that may be used in this report.

J+ Data are qualified as estimated, with a high bias likely to occur. False positives or false
negatives are unlikely to have been reported.
J- Data are qualified as estimated, with a low bias likely to occur. False positives or false negatives
are unlikely to have been reported.
J Data are qualified as estimated; it is not possible to assess the direction of the potential bias.
False positives or false negatives are unlikely to have been reported.
R Data are qualified as rejected. There is a significant potential for the reporting of false
negatives or false positives.
UJ Indicates the compound or analyte was analyzed for but not detected. The sample detection
limit is an estimated value.
B The compound or analyte was found in an associated blank as well as in the sample.
None Indicates the data was not significantly impacted by the finding, therefore qualification was not
required.

2.0 Data Review

2.1 Sample Receipt

Copies of the chain-of-custody (COC) forms were included in the laboratory data package. COCs were
reviewed for accuracy, completeness, and evidence of correct sample preservation. No sample receipt
problems were noted.

2.2 Holding Times

All samples were analyzed within required holding times.

2.3 Reporting Levels

The data user should ensure that all reporting levels meet project requirements. All samples were run
undiluted, at normal laboratory reporting levels, with the following exceptions:

AQS, Inc. Data Validation Report

Page 3
Sample(s) Analyte(s) Notes Qualifiers
EXC- Methyl tert-butyl ether
Naphthalene
Toluene
TPH (GC/MS) Low Fraction
These analytes were reported as
non-detect but were run diluted –
elevating the detection limit.

The data user should ensure that
detection limits for non-detect
results meet project
requirements.
None required

2.4 Initial and Continuing Calibration

The laboratory did not provide initial or continuing calibration information. It is assumed that all initial
and ongoing calibration requirements were met.

2.5 Blanks

Field and method blanks were free of contamination.

Sample(s) Analyte(s) Notes Qualifiers
EXC-3 Lead, Total 0.138 These analytes were detected in
the trip blank at the levels
indicated.
Flag detects as
estimated (J)

2.6 Surrogate Recoveries

Surrogate recoveries were within method limits.

2.7 Laboratory Control Samples (LCSs)

The laboratory did not provide LCS information. The case narrative indicated that, except as noted, all
method QC requirements were met.

Sample(s) Analyte(s) Notes Qualifiers
EXC- Toluene LCS recovery was high. Flag detects as
estimated (J)

2.8 Matrix Spikes (MSs)

Matrix spike recoveries were within method limits with the following exceptions:

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Page 4
Sample(s) Analyte(s) Notes Qualifiers
EXC-3 Lead, Total MS and/or MSD recovery was
high.
Flag detects as
estimated (J)

2.9 Field Duplicates

Field duplicates were not collected with this data set.

2.10 Other QC Elements

No other QC problems were noted.

3.0 Validation Summary

As determined by this evaluation, all analyses in these SDGs appear to have been conducted according
to method requirements. Some results have been qualified as estimated (J flags). As qualified, all data
are acceptable for use.

Data Quality Summary
for
Former Sommers Auto

Prepared for:

Wasatch Environmental, Inc.
2410 West California Ave.
Salt Lake City, Utah 84104

Prepared by:

AQS, Inc.
2112 Deer Run Drive
South Weber, Utah 84405

3 December 2024

Data Quality Summary AQS, Inc.

2

Introduction

This data quality summary is prepared for Wasatch Environmental, Inc. and summarizes the precision,
accuracy, representativeness, completeness, and comparability (PARCC) results for Former Sommers
Auto, Job # 2469-002F.

A data validation report for each data set is provided separately. Data quality parameters and objectives
are defined in the project Quality Assurance Project Plan

Project samples are listed in Table 1. Acronyms used in this report are listed in Table 2.

Table 1. Project Samples

Sample ID Lab ID Matrix Sample Date
CHEMTECH
TP - 1 (2'-3') 24F1419-01 Solid 6/17/2024
TP - 2 ( 5'-6') 24F1419-02 Solid 6/17/2024
TP - 3 ( 2'-3') 24F1419-03 Solid 6/17/2024
TP - 4 ( 2'-3') 24F1419-04 Solid 6/17/2024
TP - 5 ( 4'-5') 24F1419-05 Solid 6/17/2024
TP - 6 ( 4'-5') 24F1419-06 Solid 6/17/2024
TP - 60 ( 4'-5') 24F1419-07 Solid 6/17/2024
DU-1 24F1419-08 Solid 6/17/2024
DU-2 24F1419-09 Solid 6/17/2024
DU-10 24F1419-10 Solid 6/17/2024
Test Pit WCS 24F1419-11 Solid/Ext 6/17/2024
EXC 1-3 WCS 24F1419-12 Solid/Ext 6/17/2024
Trip Blank 24F1419-13 Water 6/17/2024
Equip Blank 24F1419-14 Water 6/17/2024

EXC-4-SW 24H0986-01 Solid 8/7/2024
EXC-4-SE 24H0986-02 Solid 8/12/2024
EXC-4-West 1 24H0986-03 Solid 8/12/2024
Trip Blank 24H0986-04 Water 8/7/2024

EXC-4-Floor1 24H1461-01 Solid 8/13/2024
EXC-4-Floor2 24H1461-02 Solid 8/13/2024
EXC-4-East1 24H1461-03 Solid 8/14/2024
EXC-4-East10 24H1461-04 Solid 8/14/2024
EXC-4-West2 24H1461-05 Solid 8/15/2024
EXC-4-NW 24H1461-06 Solid 8/15/2024
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Sample ID Lab ID Matrix Sample Date
EXC-4-Floor3 24H1461-07 Solid 8/15/2024
EXC-4-West3 24H1461-08 Solid 8/15/2024
Trip Blank 24H1461-09 Water 8/13/2024

EXC-4-West 4 24H1665-01 Solid 8/19/2024
EXC-4- NE 24H1665-02 Solid 8/19/2024
EXC-4- East 2 24H1665-03 Solid 8/19/2024
EXC-4- Floor 4 24H1665-04 Solid 8/19/2024
EXC-4- Floor 40 24H1665-05 Solid 8/19/2024
EXC-4- Floor 5 24H1665-06 Solid 8/19/2024
EXC-4-GW1 24H1665-07 Water 8/19/2024
EXC-4-GW2 24H1665-08 Water 8/19/2024
Trip Blank 24H1665-09 Water 8/19/2024
Equip Blank 24H1665-10 Water 8/19/2024

EXC-2-N 24H1959-01 Solid 8/20/2024
EXC-2-E 24H1959-02 Solid 8/20/2024
EXC-2-SE 24H1959-03 Solid 8/20/2024
EXC-2-S 24H1959-04 Solid 8/20/2024
EXC-2-W 24H1959-05 Solid 8/20/2024
EXC-2-Floor 24H1959-06 Solid 8/20/2024
EXC-2-W2 24H1959-07 Solid 8/20/2024
Frac Tank 24H1959-08 Water 8/21/2024

EXC-3-N 24H2214-01 Solid 8/22/2024
EXC-3-E 24H2214-02 Solid 8/22/2024
EXC-3-S 24H2214-03 Solid 8/22/2024
EXC-3-W 24H2214-04 Solid 8/22/2024
EXC-3-Floor 24H2214-05 Solid 8/22/2024
EXC-3-Floor 10 24H2214-06 Solid 8/22/2024
Equip Blank 24H2214-07 Water 8/22/2024
EXC-4-NE2 24H2214-08 Solid 8/22/2024
EXC-1-Comp 24H2214-09 Solid 8/22/2024
Trip Blank 24H2214-10 Water 8/22/2024
Frack Tank 2 24H2214-11 Water 8/23/2024

EXC-1-1 24I1821-01 Solid 9/20/2024
EXC-1-2 24I1821-02 Solid 9/20/2024
EXC-1-3 24I1821-03 Solid 9/20/2024
EXC-1-4 24I1821-04 Solid 9/20/2024
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Sample ID Lab ID Matrix Sample Date
EXC-1-5 24I1821-05 Solid 9/20/2024
EXC-1-6 24I1821-06 Solid 9/20/2024
EXC-1-7 24I1821-07 Solid 9/20/2024
EXC-1-8 24I1821-08 Solid 9/20/2024
EXC-1-9 24I1821-09 Solid 9/20/2024
EXC-1-10 24I1821-10 Solid 9/20/2024
EXC-1-11 24I1821-11 Solid 9/20/2024
EXC-1-12 24I1821-12 Solid 9/20/2024
EXC-1-13 24I1821-13 Solid 9/20/2024
EXC-1-130 24I1821-14 Solid 9/20/2024
EXC-1-14 24I1821-15 Solid 9/20/2024
EXC-1-15 24I1821-16 Solid 9/20/2024
EXC-1-16 24I1821-17 Solid 9/20/2024
EXC-1-160 24I1821-18 Solid 9/20/2024

MW-6 24J0550-01 Water 10/7/2024
MW-7 24J0550-02 Water 10/7/2024
MW-70 24J0550-03 Water 10/7/2024
Trip Blank 24J0550-04 Water 10/7/2024
Equip Blank 24J0550-05 Water 10/7/2024

PACE ANALYTICAL
EXC-4 L1766673-01 SS 8/12/2024
EXC- L1766673-02 SS 8/12/2024

EXC-2 L1770255-01 SS 8/21/2024

EXC-3 L1771052-01 SS 8/22/2024

EXC-1 L1771237-01 SS 8/23/2024
Note: Highlighted samples are field duplicates.

Table 2. Acronyms

Acronym Definition
%R Percent Recovery
EB Equipment Blank
FD Field Duplicate
LCS Laboratory Control Sample
MS Matrix Spike
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Acronym Definition
MSD Matrix Spike Duplicate
PARCC Precision, Accuracy, Representativeness, Completeness, Comparability
QC Quality Control
RPD Relative Percent Difference
TB Trip Blank
VOC Volatile Organic Compound

Data Quality Objectives

The overall QA/QC objective for this project is to develop and implement procedures for field sampling,
chain-of-custody (COC), laboratory analyses, and reporting that will provide results which are valid and
legally defensible in a court of law. The purpose of implementing these procedures is to assess the data
obtained with respect to the data quality parameters of precision, representativeness, accuracy,
completeness, and comparability for both the laboratory analytical program and field sample collection
activities. The primary goal of the program is to ensure that the data generated are representative of
environmental conditions at the Site. To achieve this goal, a combination of quantitative procedures and
qualitative evaluations will be used to assess the data quality.
Precision

Precision is a measure of mutual agreement among individual measurements of the same property,
usually under prescribed similar conditions, and typically expressed in terms of the standard deviation or
relative percent difference (RPD).

Field Data Precision

Field precision is assessed through the collection and analysis of field duplicates and comparing the
analytical results of the field duplicates to the analytical results of the environmental samples.

For groundwater field duplicates, a calculated RPD of 20% is deemed acceptable. For soil and indoor air
duplicates, a calculated RPD of 50% is deemed acceptable.

FIELD DUPLICATE RPD
SDG # FD RPD # Unacceptable # Acceptable % Acceptable
24F1419 52 4 48 92.3%
24H0986 --- --- --- ---
24H1461 9 2 7 77.8%
24H1665 9 2 7 77.8%
24H1959 3 0 3 100.0%
24H2214 3 1 2 66.7%
Data Quality Summary AQS, Inc.

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24I1821 4 1 3 75.0%
24J0550 9 0 9 100.0%
L1766673 --- --- --- ---
L1770255 --- --- --- ---
L1771052 --- --- --- ---
L1771237 --- --- --- ---
Overall 89 10 79 88.8%

For this project, 88.8% of field duplicate results were acceptable.

Laboratory Data Precision

Laboratory precision will be assessed through the calculation of RPD and/or relative standard deviations
(RSD) for duplicate samples. Analytical precision will be measured by comparing analytical results for
matrix spike (MS) and matrix spike duplicate (MSD) samples and internal laboratory samples that may
be analyzed according to analytical method or laboratory standard operating procedure requirements.
Acceptance criteria for analytical precision will be based on established laboratory quality control limits
for individual analytes. Applicable control limits are based on statistically valid historical data compiled
by the laboratory which meet or exceed precision requirements specified by the analytical method.
Standard operating procedures are on file with the selected project laboratory.

For laboratory duplicates, the RPDs within established laboratory control limits for each analyte are
acceptable.

MS/MSD RPD
SDG # MS RPD # Unacceptable # Acceptable % Acceptable
24F1419 89 3 86 96.6%
24H0986 7 0 7 100.0%
24H1461 90 1 89 98.9%
24H1665 30 0 30 100.0%
24H1959 15 0 15 100.0%
24H2214 11 0 11 100.0%
24I1821 2 0 2 100.0%
24J0550 7 0 7 100.0%
L1766673 --- --- --- ---
L1770255 4 0 4 100.0%
L1771052 2 0 2 100.0%
L1771237 1 0 1 100.0%
Overall 258 4 254 98.4%

For this project, 98.4% of MS/MSD duplicate results were acceptable.

Data Quality Summary AQS, Inc.

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Precision Assessment

Overall, 93.6% of the field and laboratory duplicates met project requirements. Precision for the project
is considered acceptable and under control.
Accuracy

Accuracy is the degree of agreement of a measurement with an accepted reference or true value. The
accuracy of the analytical data is assessed by examining possible sources of error that may bias the
analytical results.

Field Data Accuracy

Sources of the errors in the field can occur during sampling (i.e., cross contamination from sampling
equipment, etc.), field handling, and transportation. Accuracy in the field will be assessed by
documenting adherence to standard operating procedures for sample collection, preservation, and
handling, and through preparation and analysis of trip blanks and equipment blanks.

It is presumed that field operating procedures were followed. Sample receiving documentation indicates
that proper sample collection, preservation and handling procedures were followed.

FIELD BLANKS
SDG # Blank Results # Unacceptable # Acceptable % Acceptable
24F1419 104 7 97 93.3%
24H0986 73 0 73 100.0%
24H1461 73 0 73 100.0%
24H1665 81 0 81 100.0%
24H1959 --- --- --- ---
24H2214 75 2 73 97.3%
24I1821 --- --- --- ---
24J0550 81 0 81 100.0%
L1766673 --- --- --- ---
L1770255 --- --- --- ---
L1771052 --- --- --- ---
L1771237 --- --- --- ---
Overall 487 9 478 98.2%

For this project, 98.2% of the field blank results were acceptable.

Data Quality Summary AQS, Inc.

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Laboratory Data Accuracy

Sources of errors in the laboratory can occur during sample preparation and analysis, duplicate and
control sample preparation, and due to instrument and quantification errors. Laboratory accuracy is
assessed through the analysis of standard reference materials (SRMs) in laboratory control samples,
MSs, MSDs, and surrogate compounds and the determination of their recoveries in terms of percentage.
Control limits are established by the laboratory for each analyte based on statistically valid historical
recovery results, which meet or exceed the requirements specified by the analytical method. In addition,
the project laboratory will analyze method blanks to determine the potential for contamination
introduced at any stage of sample preparation or analysis. Laboratory control limits and frequency for
spike recovery and method blank analysis are specified in standard operating procedures for each
analytical method, which are on file with the selected project laboratory.

Spike recoveries from laboratory control samples (LCSs) and MS/MSDs that are within established
laboratory control limits for each analyte are considered acceptable.

MS %R
SDG # MS/MSD %R # Unacceptable # Acceptable % Acceptable
24F1419 178 30 148 83.1%
24H0986 172 0 172 100.0%
24H1461 162 0 162 100.0%
24H1665 60 5 55 91.7%
24H1959 30 3 27 90.0%
24H2214 22 2 20 90.9%
24I1821 3 1 2 66.7%
24J0550 17 0 17 100.0%
L1766673 --- --- --- ---
L1770255 8 0 8 100.0%
L1771052 4 1 3 75.0%
L1771237 2 0 2 100.0%
Overall 658 42 616 93.6%

LCS %R
SDG # LCS %R # Unacceptable # Acceptable % Acceptable
24F1419 148 6 142 95.9%
24H0986 86 2 84 97.7%
24H1461 104 5 99 95.2%
24H1665 115 24 91 79.1%
24H1959 19 0 19 100.0%
24H2214 83 13 70 84.3%
24I1821 --- --- --- ---
24J0550 79 5 74 93.7%
Data Quality Summary AQS, Inc.

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L1766673 36 1 35 97.2%
L1770255 3 0 3 100.0%
L1771052 3 0 3 100.0%
L1771237 2 0 2 100.0%
Overall 678 56 622 91.7%

For this project, 93.6% of MS results and 91.7% of LCS results were acceptable.

Accuracy Assessment

Overall, 92.7% of the accuracy-related parameters met project requirements. Accuracy for the project is
considered acceptable and under control.
Representativeness

Representativeness is a qualitative parameter that expresses the degree to which sample data
accurately and precisely represent a characteristic of a population, parameter variations at a sampling
point, or an environmental condition. As such, representativeness requires the selection of appropriate
analytical methods, sampling protocols, and sampling locations such that results are representative of
the media being sampled and conditions being measured.

Field Data Representativeness

Representativeness is dependent upon the proper design of the sampling program and will be satisfied
by ensuring that project requirements are followed.

For this project, it is presumed that environmental samples are collected from locations either
reasonably believed to be, or established to be, representative to identify source areas, evaluate the
nature of the release(s), and delineate the extent of contamination.

Laboratory Data Representativeness

Representativeness in the laboratory is ensured by carefully following standard laboratory analytical
methods and procedures, meeting sample holding times, specifying detection limits that are at or below
regulatory standards, and analyzing method blanks to check for laboratory contamination. Sample
results will not be considered representative if contaminants are detected in the method blanks, or if
the reporting limits are above the specified screening levels.

LABORATORY BLANKS
SDG # Blank Results # Unacceptable # Acceptable % Acceptable
24F1419 194 0 194 100.0%
24H0986 86 0 86 100.0%
Data Quality Summary AQS, Inc.

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24H1461 116 0 116 100.0%
24H1665 129 0 129 100.0%
24H1959 25 2 23 92.0%
24H2214 85 0 85 100.0%
24I1821 1 0 1 100.0%
24J0550 80 0 80 100.0%
L1766673 6 0 6 100.0%
L1770255 3 0 3 100.0%
L1771052 3 1 2 66.7%
L1771237 2 0 2 100.0%
Overall 730 3 727 99.6%

For this project, 99.6% of the method blank results were acceptable. Sample holding times were not
exceeded, all samples were properly preserved, receiving temperatures were not exceeded.

Representativeness Assessment

Overall, 99.6% of the representativeness-related parameters met project requirements.
Completeness

Completeness is an assessment of the number of valid measurements obtained in relation to the total
number of measurements planned for the successful achievement of the investigative objectives.
Completeness is expressed as the percentage of valid measurements to the total number of
measurements. The closer the numbers, the more complete the measurement process.

Field Data Completeness

Field completeness evaluates the number of valid measurements obtained from all measurements taken
in the project. The intent of this program is to attempt to achieve a goal of 100 percent field
completeness. Realizing that under normal conditions this goal may not be achievable, the field
completeness goal for this program is 90 percent. This completeness goal is considered adequate to
meet the DQOs for this Site based on prior consideration of PARCC parameters, the sampling plan
designs, and data collection activities proposed for each medium.

Laboratory Data Completeness

Laboratory completeness evaluates the number of valid measurements obtained from all the
measurements taken in the project. The intent of this program is to attempt to achieve a goal of 100
percent laboratory completeness. Realizing that under normal conditions this goal may not be
achievable, the laboratory completeness goal for this program is 90 percent.
Data Quality Summary AQS, Inc.

11

For this project no sample results were rejected, and all were deemed valid (with some data validation
qualifiers) based on method and laboratory acceptance criteria. Some sample dilutions occurred due to
elevated analyte concentrations and were not evaluated for usability.

OVERALL COMPLETENESS
SDG # Sample Results # Unacceptable # Acceptable % Acceptable
24F1419 433 0 433 100.0%
24H0986 100 0 100 100.0%
24H1461 205 0 205 100.0%
24H1665 175 0 175 100.0%
24H1959 43 0 43 100.0%
24H2214 107 0 107 100.0%
24I1821 36 0 36 100.0%
24J0550 105 0 105 100.0%
L1766673 16 0 16 100.0%
L1770255 3 0 3 100.0%
L1771052 3 0 3 100.0%
L1771237 2 0 2 100.0%
Overall 1228 0 1228 100.0%

Completeness Assessment

100% of collected samples were deemed valid based on independent data validation. Completeness for
the project is considered acceptable and under control.
Comparability

Comparability is a qualitative parameter expressing the confidence with which one data set may be
compared to another. Data sets will be compared only when precision and accuracy meet the specified
acceptance criteria established in this section. Samples will be collected, and analytical results will be
reported according to standard procedures and methods to ensure comparability with other similar data
and results. The comparability goal will be achieved by following the SAP and the RAP, and the specific
procedures contained therein, and by collecting and analyzing representative samples, specifying
analysis by similar analytical procedures with comparable reporting limits and by reporting analytical
results in appropriate and consistent units.

Field Data Comparability

Comparability is dependent upon the proper design of the sampling program and will be satisfied by
ensuring that the SAP and RAP are followed and that proper sampling procedures are used.

Data Quality Summary AQS, Inc.

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For this project, field QC included sample duplicates only.

Laboratory Data Comparability

Analytical data will be considered comparable when similar sampling and analytical methods are used
and documented. Similar QA objectives will be used throughout the project to ensure comparability. At
the discretion of the Utah DERR, split samples may be collected for submittal to a third-party analytical
laboratory to assist in evaluation of comparability. The frequency at which split samples are collected
and analyzed will be specified by the Utah DERR following the receipt and approval of individual work
plans for the project.

For this project, both laboratories used standard analytical methods and standard units of measure.
Reporting limits were consistent except when high analyte concentrations required sample dilution.

Comparability Assessment

Comparability for the project is considered acceptable and under control.
Sensitivity

Sensitivity is the capability of a method or instrument to discriminate between measurement
response(s) representing differing levels of the variable of interest. The analytical laboratory, as part of
their standard operating procedures, follows published, approved analytical methods which validate the
methods including an evaluation of sensitivity, precision, and accuracy to ensure that the equipment can
operate properly prior to sample analysis. Wasatch will review the laboratory detection and/or
reporting limits to verify these limits are below applicable screening levels.

Reporting limits used by the laboratory were typical for the methods used and it is assumed that these
limits meet project requirements. All samples were run undiluted, at normal laboratory reporting levels,
with the following exceptions:

Sample(s) Analyte(s) Notes Qualifiers
Chemtech
24F1419

Test Pit WCS
Selenium, Total These analytes were reported as
non-detect but were run diluted –
elevating the detection limit.

The data user should ensure that
detection limits for non-detect
results meet project
requirements.
None required
Chemtech
24F1419

8270 TPH Fractionation
(several ND analytes run at
20x dilution)
These analytes were reported as
non-detect but were run diluted –
elevating the detection limit.
None required
Data Quality Summary AQS, Inc.

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TP - 3 ( 2'-3')
TP - 4 ( 2'-3')
DU-1
DU-2
DU-10

The data user should ensure that
detection limits for non-detect
results meet project
requirements.
Chemtech
24H1461

EXC-4-West2
EXC-4-West3
8270 TPH Fractionation
(several ND analytes run at
10x dilution)
These analytes were reported as
non-detect but were run diluted –
elevating the detection limit.

The data user should ensure that
detection limits for non-detect
results meet project
requirements.
None required
Pace
L1766673

EXC-
Methyl tert-butyl ether
Naphthalene
Toluene
TPH (GC/MS) Low Fraction
These analytes were reported as
non-detect but were run diluted –
elevating the detection limit.

The data user should ensure that
detection limits for non-detect
results meet project
requirements.
None required

Sensitivity Assessment

Sensitivity for the project is considered acceptable and under control.