HomeMy WebLinkAboutDERR-2025-000651Stantec Consulting Services Inc.
2890 East Cottonwood Parkway Suite 300, Salt Lake City UT 84121-7283
January 22, 2025
File: 203721870
Attention: Nicole Chavez
Utah Department of Environmental Quality
Division of Environmental Response and Remediation
195 North 1950 West, 1st Floor
P.O. Box 144840
Salt Lake City, Utah 84116
Reference: 7-Eleven Store No. 27074 – Quarterly Groundwater Monitoring Report
3185 Harrison Boulevard, Ogden, Utah
Facility ID 1200120, Release Site NXK
Dear Ms. Chavez,
Stantec is pleased to present this Quarterly Groundwater Monitoring Report on behalf of 7-Eleven, Inc.
(7-Eleven) for 7-Eleven Store No. 27074 (the Site) located at 3185 Harrison Boulevard Ogden, Utah
(Figure 1). The Utah Department of Environmental Quality (UDEQ), Division of Environmental Response
and Remediation (DERR) refers to the Site as Facility ID 1200120, Release Site NXK. This report presents
groundwater monitoring and sampling results for the fourth quarter of 2024.
Four quarterly groundwater monitoring and sampling events were approved under Work Plan and Budget
(WP&B) NXK-07. The objectives of quarterly groundwater monitoring and sampling are to further assess
dissolved petroleum hydrocarbon concentration trends and seasonal groundwater level fluctuations
associated with the Site following the March 2021 remedial excavation. This report also presents additional
desktop study results assessing the possibility of off-site petroleum hydrocarbon sources contributing to the
unexpected dissolved petroleum hydrocarbon concentration increases observed at the Site beginning in
2023.
BACKGROUND
7-Eleven has leased the southern portion of the property since 1986 and operated a 7-Eleven convenience
store with former retail sales of gasoline. The former underground storage tank (UST) system was located
in the southeast side of the property (Figure 1) and consisted of three 10,000-gallon gasoline USTs and
two product dispensers formerly used to distribute various grades of unleaded gasoline fuel.
The northern portion of the property is occupied by an out-of-service automotive service facility, most
recently In’ n’ Out Auto Clinic. The facility was previously operated as a Minit Lube, and a petroleum release
from this facility (Release Site IPT) was discovered during the closure of two 3,000-gallon new oil USTs
and one 3,000-gallon used oil UST on June 24, 1994. The former Minit Lube USTs were in the northwest
portion of the property (behind the automotive service facility) and were closed by removal.
Wasatch Environmental (Wasatch) conducted a limited subsurface investigation (LSI) on April 23, 2020, on
behalf of the Utah Transit Authority (UTA). Residual impacts from Release Site IPT appeared to be present
January 22, 2025
Page 2 of 6
Re: 7-Eleven Store No. 27074 – Quarterly Groundwater Monitoring Report
3185 Harrison Boulevard, Ogden, Utah
Facility ID 1200120, Release Site NXK
based on the analytical results of a groundwater sample collected from a temporary well-point within the
former Minit Lube UST basin (west of the current automotive service facility building). The sample contained
concentrations of total petroleum hydrocarbons as gasoline range organics (TPH-GRO) and TPH as diesel
range organics (TPH-DRO) above the Initial Screening Levels (ISLs) developed by the UDEQ-DERR
Leaking Underground Storage Tank (LUST) Section.
The LSI also identified a release that appeared to be related to the 7-Eleven UST basin, and Stantec
reported a petroleum release to the UDEQ-DERR on May 11, 2020. Soil and groundwater analytical results
presented in the Wasatch LSI report indicated petroleum hydrocarbon concentrations west and south of
the 7-Eleven UST basin exceeded the ISLs and Tier 1 Screening Levels (TSLs) developed by the UDEQ-
DERR LUST Section. Based on these results, the UDEQ-DERR assigned Release Site NXK to the Site
and requested a subsurface investigation
WP&B NXK-01 was approved on September 30, 2020, and Stantec conducted the subsurface investigation
(SI) on October 26 and 27, 2020 (with groundwater sampling conducted on November 12, 2020). Based
on the results of the SI, benzene was reported above the ISL in a soil sample collected from the soil boring
advanced to install monitoring well MW-2. TPH-GRO was reported above the ISL in a soil sample collected
from the soil boring advanced to install MW-4. Groundwater analytical results indicated dissolved
concentrations of benzene, ethylbenzene, TPH-GRO, and TPH-DRO exceeded their respective ISLs and/or
TSLs in samples collected west and south of the UST basin (MW-1, MW-2, MW-3, and MW-4), and
groundwater impacts extended beyond the property boundaries to the south.
The UST system was closed by removal on March 2, 2021. A remedial excavation was then completed
from March 3 through 5 under WP&B NXK-03. Petroleum containing soil (PCS) was removed from the
UST excavation as part of UST closure, and the excavation floor was extended an additional 1.5 to 2 feet
beyond the interface of backfill and native soils to remove additional PCS. Excavated soils were screened
on site using a photoionization detector, and PCS was segregated for disposal. Non-impacted soils were
used as backfill, and additional imported fill was also needed to fill and achieve compaction within the UST
excavation. Approximately 180-tons of PCS were disposed of as non-hazardous waste at the
ET Technologies Soil Regeneration Site at the Salt Lake Valley Landfill.
Under WP&B NXK-02, Stantec conducted quarterly monitoring between the second quarter of 2021 and
the first quarter of 2022. Dissolved petroleum hydrocarbon concentrations generally decreased during this
time but remained above ISLs in MW-1 and MW-4 and TSLs in MW-2.
On April 8, 2022, Stantec oversaw the abandonment of groundwater monitoring wells MW-2, MW-4, MW-5,
and MW-6 to accommodate UTA BRT Project construction. Well abandonment activities were conducted
according to WP&B NXK-04.
As of fall 2022, UTA BRT Project construction had progressed to the point that replacement groundwater
monitoring well locations could be proposed. On February 7 and 8, 2023, Stantec oversaw the installation
of replacement groundwater monitoring wells MW-2R, MW-5R, MW-8, and MW-9 and conducted soil
logging and sampling activities. These activities were conducted according to WP&B NXK-05.
Due to the impacts of the UTA BRT project to the property, 7-Eleven ceased operations at this store in July
2023. The convenience store building is currently vacant. Stantec retains environmental access to manage
Release Site NXK.
January 22, 2025
Page 3 of 6
Re: 7-Eleven Store No. 27074 – Quarterly Groundwater Monitoring Report
3185 Harrison Boulevard, Ogden, Utah
Facility ID 1200120, Release Site NXK
Work conducted under WP&Bs NXK-01 through NXK-06 were previously reported to the UDEQ-DERR in
the following reports.
Subsurface Investigation Report, 7-Eleven Store No. 27074, dated December 15, 2020.
UST System Closure and Remedial Excavation Report, 7-Eleven Store No. 27074, dated April 28,
2021.
Quarterly Groundwater Monitoring Report, 7-Eleven Store No. 27074 documents, dated August 2,
2021, November 2, 2021, February 2, 2022, and May 2, 2022.
Monitoring Well Abandonment Report, 7-Eleven Store No. 27074, dated July 8, 2022.
Groundwater Monitoring Well Installation Report, 7-Eleven Store No. 27074, dated March 30, 2023.
Quarterly Groundwater Monitoring Report, 7-Eleven Store No. 27074, dated April 24, 2023.
Quarterly Groundwater Monitoring Report, 7-Eleven Store No. 27074, dated July 24, 2023.
Quarterly Groundwater Monitoring Report, 7-Eleven Store No. 27074, dated October 24, 2023.
Quarterly Groundwater Monitoring Report, 7-Eleven Store No. 27074, dated January 24, 2024.
Quarterly Groundwater Monitoring Report, 7-Eleven Store No. 27074, dated July 23, 2024.
Quarterly Groundwater Monitoring Report, 7-Eleven Store No. 27074, dated October 22, 2024.
GROUNDWATER MONITORING METHODS
On December 11, 2024, static groundwater levels were gauged to the nearest one hundredth of a foot using
a battery-powered product/water interface probe. Free product was not encountered in any of the
monitoring wells. Monitoring wells MW-3, MW-5R, and MW-7 were sampled on December 11, 2024, and
MW-1, MW-2R, MW-8, and MW-9 were sampled on December 12, 2024.
The pumping rate for each well was determined in the field based on an attempt to limit drawdown within
the well to one foot or less. Parameters were collected using either an AquaTroll 500 equipped with
temperature/ conductivity, potential hydrogen (pH)/oxidation reduction potential (ORP), dissolved oxygen
(DO), and turbidity probes, or a YSI 556 equipped with temperature/conductivity, pH/ORP, and DO probes.
Parameters were recorded on the appropriate time interval necessary to fully replace the volume of the
flow-through cell between readings. Purging continued until three consecutive readings were within the
stabilization conditions detailed in WP&B NXK-07. Purged groundwater was thin spread on the surface
near each well location.
Wells were purged via peristaltic pump and disposable one-quarter inch poly sample tubing. Sample tubing
was disconnected from the flow-through cell prior to sample collection. Groundwater samples were
decanted into five 40-milliliter (mL) glass volatile organic analysis (VOA) containers containing hydrochloric
acid (HCl) preservative. VOAs were filled in a manner to minimize sample volatilization and remove all
headspace. Samples were then labeled with the sample identification, collection date, and time, and placed
into an ice chilled cooler for delivery to the project laboratory under chain-of-custody (COC) documentation.
Stantec also collected/submitted the following quality assurance/quality control (QA/QC) samples.
Blind field duplicate (DUP-01) from MW-1
Trip blank
Samples were submitted for analysis of methyl tertiary-butyl ether, benzene, toluene, ethylbenzene, total
xylenes, and naphthalene (MBTEXN) by United States Environmental Protection Agency (EPA) Method
January 22, 2025
Page 4 of 6
Re: 7-Eleven Store No. 27074 – Quarterly Groundwater Monitoring Report
3185 Harrison Boulevard, Ogden, Utah
Facility ID 1200120, Release Site NXK
8260B and TPH-GRO and TPH-DRO by EPA Method 8015. The trip blank was only analyzed for volatile
organic compounds (VOCs) by EPA Method 8260B. All analyses were performed by Pace Analytical
National (Pace) located in Mount Juliet, Tennessee. Laboratory report and chain-of-custody documentation
are included as Attachment 1.
GROUNDWATER MONITORING RESULTS
On December 11, 2024, shallow groundwater beneath the Site was measured at depths ranging from 10.81
(MW-1) to 13.34 (MW-3) feet below top of casing (TOC). Each depth to groundwater measurement was
converted to a relative groundwater elevation using the calculated relative TOC elevation of the monitoring
well. A groundwater elevation contour map is provided as Figure 2.
Isoconcentration maps for dissolved benzene, TPH-GRO, and TPH-DRO are provided as Figure 3,
Figure 4, and Figure 5, respectively. Groundwater analytical results are summarized in Table 1. The
fourth quarter 2024 field and analytical results are summarized below.
Shallow groundwater beneath the Site appears to flow towards the southwest at a local hydraulic
gradient of approximately 0.06 feet per foot (as estimated between wells MW-5R and MW-7).
Groundwater elevations across the site decreased between the September 2024 and December 2024
monitoring events.
For the groundwater sample collected from MW-1, the dissolved benzene, ethylbenzene, TPH-GRO
and TPH-DRO concentrations exceeded the respective ISLs.
For the groundwater sample collected from MW-2R, the dissolved TPH-DRO concentration exceeded
the ISL. The dissolved benzene and TPH-GRO concentrations were below the respective ISLs.
The dissolved TPH-DRO concentrations in MW-3, MW-7, MW-8, and MW-9 all remain below the ISL.
Relative percent differences calculated between the MW-1 and DUP-01 sample analytical results were
within generally accepted standards except for that of TPH-GRO, which has a relative percent
difference of 43%. The MW-1 and DUP-01 samplers were analyzed in different TPH-GRO batches by
Pace; the MW-1 TPH-GRO result reported by Pace was from an analysis batch ran two days later and
at a dilution of five.
No petroleum hydrocarbons were detected at concentrations above laboratory RLs in the trip blank.
All other petroleum hydrocarbon concentrations were either below ISLs or were not detected above
laboratory RLs.
All laboratory RLs were below the respective ISLs for this sampling event.
CONTINUED OFF-SITE SOURCE DESKTOP STUDY
Three data gaps were identified in the summary of the off-site source desktop study submitted with the
previous quarterly groundwater monitoring report:
The nature of the original commercial structure first observed at the Site as of 1962 aerial photography
could not be distinguished with certainty.
Whether or not diesel was associated with the original commercial structure was unknown.
Whether or not additional petroleum releases were recorded for the former 7-Eleven or former Minit
Lube properties was not researched.
January 22, 2025
Page 5 of 6
Re: 7-Eleven Store No. 27074 – Quarterly Groundwater Monitoring Report
3185 Harrison Boulevard, Ogden, Utah
Facility ID 1200120, Release Site NXK
In an effort to address the first two of these data gaps, Stantec ordered fire insurance maps and city
directories for the Site area from Light Box EDR (EDR), a due diligence data provider. EDR could not
provide fire insurance maps for the Site area, and the receipt of the city directories package was pending
as of the writing of this report. Stantec will include any findings related to the nature of the original on-site
commercial structure and presence of diesel at that structure from review of the city directories in the
groundwater monitoring report for the first quarter of 2025.
As documented in the previous groundwater monitoring report, the UDEQ interactive map did not document
any USTs with significant release histories, petroleum related environmental incidents, voluntary cleanup
program sites, CERCLA sites, or brownfields upgradient of the Site. After additional review of the UDEQ
Environmental Interactive Map, no other on-site releases are documented for either the former 7-Eleven or
former Minit Lube properties.
CONCLUSIONS AND RECOMMENDATIONS
The information compiled for the desktop study to date does not indicate a high potential for an off-site or
separate on-site source of petroleum that may be impacting current Site conditions.
The groundwater levels measured in 2024 followed the seasonal trend of high in the spring and low in early
winter before snowmelt. The overall water levels in 2024 were higher than those in previous years. The
dissolved petroleum hydrocarbon concentrations at MW-1 and MW-2 appeared to respond differently to the
high water levels: the overall concentrations at MW-1 were higher in 2024 than in previous years, whereas
the concentrations at MW-2 have mostly attenuated in 2024. This could be an indication that MW-1 is closer
to the residual petroleum hydrocarbon source mass than MW-2, and the dissolved concentrations at MW-1
tend to go up as the water table rises and comes in contact with the source mass.
Dissolved petroleum hydrocarbon concentrations versus time for select wells are shown in the attached
Graphs. The groundwater table across the Site has shown an increasing trend since March 2023; this is
the same period of time over which dissolved petroleum hydrocarbon concentrations have become more
variable. More consistent dissolved petroleum hydrocarbon concentrations may once again be observed
after the water table stabilizes following the maximum groundwater elevation conditions observed in June
2024.
One quarterly groundwater monitoring event remains under WP&B NXK-07; however, based on the current
dataset, it appears that any upgradient dissolved petroleum hydrocarbon concentrations above screening
levels attenuate before reaching downgradient wells. Stantec will likely recommend closure of Release
Site NXK following the first quarter of 2025 groundwater monitoring event.
LIMITATIONS AND CERTIFICATION
The conclusions in the Report titled 7-Eleven Store No. 27074 – Quarterly Groundwater Monitoring Report
are Stantec’s professional opinion, as of the time of the Report, and concerning the scope described in the
Report. The opinions in the document are based on conditions and information existing at the time the
scope of work was conducted and do not take into account any subsequent changes. The Report relates
solely to the specific project for which Stantec was retained and the stated purpose for which the Report
was prepared. The Report is not to be used or relied on for any variation or extension of the project, or for
any other project or purpose, and any unauthorized use or reliance is at the recipient’s own risk.
January 22, 2025
Page 6 of 6
Re: 7-Eleven Store No. 27074 – Quarterly Groundwater Monitoring Report
3185 Harrison Boulevard, Ogden, Utah
Facility ID 1200120, Release Site NXK
Stantec has assumed all information received from 7-Eleven (the “Client”) and third parties in the
preparation of the Report to be correct. While Stantec has exercised a customary level of judgment or due
diligence in the use of such information, Stantec assumes no responsibility for the consequences of any
error or omission contained therein.
This Report is intended solely for use by the Client in accordance with Stantec’s contract with the Client.
While the Report may be provided by the Client to applicable authorities having jurisdiction and to other
third parties in connection with the project, Stantec disclaims any legal duty based upon warranty, reliance
or any other theory to any third party, and will not be liable to such third party for any damages or losses of
any kind that may result.
If you have any questions or require any additional information, please contact Anna Skinner via the
contact information provided below.
Regards,
Stantec Consulting Services Inc.
Ally Auffermann, PE
Environmental Engineer
Phone: (801) 617 3211
ally.auffermann@stantec.com
Anna Skinner
Project Manager
Certified UST Consultant #CC0271
Phone: (801) 743 4815
anna.skinner@stantec.com
Attachments: Figure 1
Figure 2
Figure 3
Figure 4
Figure 5
Table 1
Graph 1
Graph 2
Graph 3
Graph 4 Graph 5
Graph 6
Graph 7
Attachment 1 Laboratory Report and Chain-of-Custody Documentation
c. File / 7-Eleven Inc.
John Wainwright, Stantec
Site Plan
Groundwater Elevation Contour Map December 2024
Dissolved Benzene Isoconcentration Map December 2024
Dissolved TPH-GRO Isoconcentration Map December 2024
Dissolved TPH-DRO Isoconcentration Map December 2024
Groundwater Analytical Results
MW-1 Select Concentration vs. Time Graphs
MW-2/2R Select Concentration vs. Time Graphs
MW-3 Select Concentration vs. Time Graphs
MW-5/5R Select Concentration vs. Time Graphs MW-7 Select Concentration vs. Time Graphs
MW-8 TPH-DRO Concentration vs. Time Graph
MW-9 TPH-DRO Concentration vs. Time Graph
FIGURES
MW-1
MW-3
MW-7
3200 SOUTH
HA
R
R
I
S
O
N
B
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V
A
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FORMER
CANOPY/
DISPENSERS
CONVENIENCE
STORE
BUILDING
AUTOMOTIVE
SERVICE
FACILITY
T
T
ELEVEN
FORMER
PLANTERPLANTER
UE
UE
UE
UE UE UE UE
UTILITY POLE
STREET LIGHT
PL
A
N
T
E
R
STORE NO. 27074
FORMER
UST BASIN
FORMER
SIGN
FORMER
PLANTER
FORMER
PLANTER
FORMER
PLANTER
FO
R
M
E
R
PL
A
N
T
E
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MW-6
MW-2
MW-2R
MW-9
MW-8
MW-5R MW-5
MW-4
203721870 STA AMS JPW 03/20/23
1SITE PLAN
STORE #27074
3185 HARRISON BOULEVARD
OGDEN, UTAH
FOR:
JOB NUMBER:DRAWN BY:CHECKED BY:APPROVED BY:DATE:
FILEPATH:C:\Users\SAguinaldo\Desktop\2023\SLC\203721870\FIG 2_7-11_27074_SITE PLAN_03-20-2023.dwg | Layout Tab: 1 | Drafter: SAguinaldo | Mar 22, 2023 at 14:43
FIGURE:
No warranty is made by Stantec Consulting Services Inc. as to the accuracy, reliability, or completeness of these data. Original data were
compiled from various sources. This information may not meet National Map Accuracy Standards. This product was developed
electronically, and may be updated without notification. Any reproduction may result in a loss of scale and or information.
N
ELEVEN
PHONE:
2890 E COTTONWOOD PKWY, STE 300
SALT LAKE CITY, UTAH
(801) 261-0090
LEGEND
T
UE
MONITORING WELL LOCATION
TELEPHONE LINE
GAS LINE
OVERHEAD ELECTRICAL LINE
BELOW GROUND ELECTRICAL LINE
WATER LINE
0 30 60
APPROXIMATE SCALE IN FEET
ABANDONED MONITORING WELL LOCATION
3200 SOUTH
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B
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V
A
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FORMER
CANOPY/
DISPENSERS
CONVENIENCE
STORE
BUILDING
AUTOMOTIVE
SERVICE
FACILITY
T
T
PLANTER
UE
UE
UE
UE UE UE UE
PL
A
N
T
E
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STORE NO. 27074
FORMER
UST BASIN
FO
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M
E
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PL
A
N
T
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MW-6
MW-2
MW-5
MW-4
MW-2R
84.34
MW-9
87.33
MW-8
84.01
MW-5R
88.11
MW-7
82.26
MW-1
86.86
MW-3
84.19
203721870 STA AA JPW 01/16/2025
2STORE #27074
3185 HARRISON BOULEVARD
OGDEN, UTAH
FOR:
JOB NUMBER:DRAWN BY:CHECKED BY:APPROVED BY:DATE:
FILEPATH:C:\Users\SAguinaldo\Desktop\2025\SLC\4Q 2024\FIG 2_7-11_27074_GWE CONTOUR MAP.dwg | Layout Tab: 2 | Drafter: SAguinaldo | Jan 17, 2025 at 8:59
FIGURE:
No warranty is made by Stantec Consulting Services Inc. as to the accuracy, reliability, or completeness of these data. Original data were
compiled from various sources. This information may not meet National Map Accuracy Standards. This product was developed
electronically, and may be updated without notification. Any reproduction may result in a loss of scale and or information.
N
ELEVEN
PHONE:
2890 E COTTONWOOD PKWY, STE 300
SALT LAKE CITY, UTAH
(801) 261-0090
ELEVEN
8
5
LEGEND
T
UE
MONITORING WELL LOCATION
TELEPHONE LINE
GAS LINE
OVERHEAD ELECTRICAL LINE
BELOW GROUND ELECTRICAL LINE
WATER LINE 0 30 60
APPROXIMATE SCALE IN FEET
ABANDONED MONITORING WELL LOCATION
GROUNDWATER ELEVATION
CONTOUR MAP
DECEMBER 2024
86.86 GROUNDWATER SURFACE ELEVATION
(FEET ABOVE MEAN SEA LEVEL)
GROUNDWATER ELEVATION CONTOUR
(DASHED WHERE INFERRED)85
8
7
8
4
8
3
83
8
5
8
8
8
6
84
87
88
86
3200 SOUTH
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DISPENSERS
CONVENIENCE
STORE
BUILDING
AUTOMOTIVE
SERVICE
FACILITY
T
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PLANTER
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UE
UE UE UE UE
PL
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STORE NO. 27074
FORMER
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FO
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M
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PL
A
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MW-6
MW-2
MW-5
MW-4
MW-2R
0.00415
MW-9
<0.00100
MW-8
<0.00100
MW-5R
<0.00100
MW-7
<0.00100
MW-1
0.185MW-3
<0.00100
203721870 STA AA AS 01/16/2025
3STORE #27074
3185 HARRISON BOULEVARD
OGDEN, UTAH
FOR:
JOB NUMBER:DRAWN BY:CHECKED BY:APPROVED BY:DATE:
FILEPATH:C:\Users\SAguinaldo\Desktop\2025\SLC\4Q 2024\FIG 3_7-11_27074_BENZENE MAP.dwg | Layout Tab: 3 | Drafter: SAguinaldo | Jan 21, 2025 at 11:04
FIGURE:
No warranty is made by Stantec Consulting Services Inc. as to the accuracy, reliability, or completeness of these data. Original data were
compiled from various sources. This information may not meet National Map Accuracy Standards. This product was developed
electronically, and may be updated without notification. Any reproduction may result in a loss of scale and or information.
N
ELEVEN
PHONE:
2890 E COTTONWOOD PKWY, STE 300
SALT LAKE CITY, UTAH
(801) 261-0090
LEGEND
T
UE
MONITORING WELL LOCATION
TELEPHONE LINE
GAS LINE
OVERHEAD ELECTRICAL LINE
BELOW GROUND ELECTRICAL LINE
WATER LINE
ELEVEN
0 30 60
APPROXIMATE SCALE IN FEET
ABANDONED MONITORING WELL LOCATION
DISSOLVED BENZENE
ISOCONCENTRATION MAP
DECEMBER 2024
0.185 DISSOLVED BENZENE CONCENTRATION
MILLIGRAMS PER LITER (mg/L)
INFERRED BENZENE ISOCONCENTRATION CONTOUR (mg/L)0.005
<ANALYTE NOT DETECTED ABOVE THE SPECIFIED LABORATORY REPORTING LIMIT
ELEVEN
0.005
3200 SOUTH
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FORMER
CANOPY/
DISPENSERS
CONVENIENCE
STORE
BUILDING
AUTOMOTIVE
SERVICE
FACILITY
T
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PLANTER
UE
UE
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UE UE UE UE
PL
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STORE NO. 27074
FORMER
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FO
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PL
A
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MW-6
MW-2
MW-5
MW-4
MW-2R
0.552
MW-9
<0.100
MW-8
<0.100
MW-5R
<0.100
MW-7
0.384
MW-1
2.74MW-3
0.349
203721870 STA AA AS 01/16/2025
4STORE #27074
3185 HARRISON BOULEVARD
OGDEN, UTAH
FOR:
JOB NUMBER:DRAWN BY:CHECKED BY:APPROVED BY:DATE:
FILEPATH:C:\Users\SAguinaldo\Desktop\2025\SLC\4Q 2024\FIG 4_7-11_27074_GRO ISOCON MAP.dwg | Layout Tab: 4 | Drafter: SAguinaldo | Jan 21, 2025 at 11:16
FIGURE:
No warranty is made by Stantec Consulting Services Inc. as to the accuracy, reliability, or completeness of these data. Original data were
compiled from various sources. This information may not meet National Map Accuracy Standards. This product was developed
electronically, and may be updated without notification. Any reproduction may result in a loss of scale and or information.
N
ELEVEN
PHONE:
2890 E COTTONWOOD PKWY, STE 300
SALT LAKE CITY, UTAH
(801) 261-0090
LEGEND
T
UE
MONITORING WELL LOCATION
TELEPHONE LINE
GAS LINE
OVERHEAD ELECTRICAL LINE
BELOW GROUND ELECTRICAL LINE
WATER LINE 0 30 60
APPROXIMATE SCALE IN FEET
ABANDONED MONITORING WELL LOCATION
DISSOLVED TPH-GRO
ISOCONCENTRATION MAP
DECEMBER 2024
2.74 DISSOLVED TPH-GRO CONCENTRATION
MILLIGRAMS PER LITER (mg/L)
INFERRED TPH-GRO ISOCONCENTRATION CONTOUR (mg/L)1
<ANALYTE NOT DETECTED ABOVE THE SPECIFIED LABORATORY REPORTING LIMIT
ELEVEN
1
3200 SOUTH
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FORMER
CANOPY/
DISPENSERS
CONVENIENCE
STORE
BUILDING
AUTOMOTIVE
SERVICE
FACILITY
T
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PLANTER
UE
UE
UE
UE UE UE UE
PL
A
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STORE NO. 27074
FORMER
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FO
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M
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PL
A
N
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MW-6
MW-2
MW-5
MW-2R
1.29
MW-9
0.313
MW-8
0.169
MW-5R
0.213
MW-7
0.600
MW-1
4.07
MW-3
0.790
MW-4
203721870 STA AA AS 01/16/2025
5STORE #27074
3185 HARRISON BOULEVARD
OGDEN, UTAH
FOR:
JOB NUMBER:DRAWN BY:CHECKED BY:APPROVED BY:DATE:
FILEPATH:C:\Users\SAguinaldo\Desktop\2025\SLC\4Q 2024\FIG 5_7-11_27074_DRO ISOCON MAP.dwg | Layout Tab: 5 | Drafter: SAguinaldo | Jan 21, 2025 at 11:23
FIGURE:
No warranty is made by Stantec Consulting Services Inc. as to the accuracy, reliability, or completeness of these data. Original data were
compiled from various sources. This information may not meet National Map Accuracy Standards. This product was developed
electronically, and may be updated without notification. Any reproduction may result in a loss of scale and or information.
N
ELEVEN
PHONE:
2890 E COTTONWOOD PKWY, STE 300
SALT LAKE CITY, UTAH
(801) 261-0090
LEGEND
T
UE
MONITORING WELL LOCATION
TELEPHONE LINE
GAS LINE
OVERHEAD ELECTRICAL LINE
BELOW GROUND ELECTRICAL LINE
WATER LINE 0 30 60
APPROXIMATE SCALE IN FEET
ABANDONED MONITORING WELL LOCATION
DISSOLVED TPH-DRO
ISOCONCENTRATION MAP
DECEMBER 2024
4.07 DISSOLVED TPH-DRO CONCENTRATION
MILLIGRAMS PER LITER (mg/L)
INFERRED TPH-DRO ISOCONCENTRATION CONTOUR (mg/L)1
<ANALYTE NOT DETECTED ABOVE THE SPECIFIED LABORATORY REPORTING LIMIT
ELEVEN
1
TABLE
MTBE
11/12/20 12.64 85.03 <0.0100 0.321 <0.0100 0.646 0.143 0.116 1.97 3.68
06/24/21 13.22 84.45 <0.00250
0.0806 <0.00250 0.370 0.0588 0.0124
1.80 0.954
10/06/21 14.34 83.33 <0.00200 0.0549 <0.00200 0.261 0.0785 0.0159 1.86 0.634
12/20/21 14.78 82.89 <0.00100 0.0320 <0.00100 0.139 0.0357 0.00708 0.898 0.430 1
03/24/22 15.52 82.15 <0.00114 0.0447 <0.00114 0.138 0.0344 <0.00571 <0.571 0.656
03/09/23 14.45 83.22 <0.00100 0.00998 <0.00100 0.0377 0.0102 <0.00500 <0.500 0.895
06/07/23 12.27 85.40 <0.00100 0.00723 <0.00100 0.0259 0.00382 <0.00500 0.501 B 0.745
09/14/23 13.12 84.55 <0.00100 0.0129 <0.00100 0.205 0.0359 0.0379 <0.500 4.78
12/15/23 13.22 84.45 <0.0100 0.0117 <0.0100 0.187 0.0304 <0.0500 <5.00 <0.100 ~
06/27/24 10.48 87.19 <0.0100 0.117 <0.0100 0.932 <0.0300 0.0590 J3 5.52 B 9.40
09/12/24 10.66 87.01 <0.0100 0.462 0.0386 1.97 0.352 0.325
J4 <5.00 8.07
12/12/24 10.81 86.86 <0.00505 0.185 <0.00500 0.959 <0.150 0.0516 Z1 2.74 4.07
11/12/20 12.35 85.03 <0.00250 0.153 0.00437 0.294 0.0440 0.0558 0.846 1.15
06/24/21 13.04 84.34 <0.00500 0.235 <0.00500 0.489 0.0196 0.0818 2.08 1.37
10/06/21 14.09 83.29 <0.0500 0.783 0.124 2.62 2.35 0.476 18.8 5.44
12/20/21 14.22 83.16 <0.0500 0.414 <0.0500 3.17 1.50 0.699 16.2 6.24
03/24/22 15.04 82.34 <0.00114 0.963 0.0282 2.21 0.637 <0.571 4.19 5.77
03/10/23 14.28 83.29 <0.0100 0.540 <0.0100 1.36 0.0738 0.0804 <5.00 8.12
06/07/23 12.26 85.31 <0.0100 0.745 0.0128 1.19 0.361 0.107 5.39 11.3
09/14/23 13.03 84.54 <0.0100 0.305 0.0377 1.18 2.18 0.250 6.17 4.31
12/15/23 13.08 84.49 <0.0100 0.364 0.0240 1.59 3.67 0.580 10.5 <0.100 ~
06/27/24 10.22 87.35 <0.00505 0.0219 Z1 <0.0500 0.465 0.591 0.132
J3,Z1 25.1 B 1.44
09/12/24 10.31 87.26 <0.01000 0.0543 <0.01000 0.454 0.0572 0.0689 <5.00 4.86
12/12/24 13.21 84.36 <0.00500 0.00415 Z1 <0.00500 0.108 <0.0150 <0.0250
0.552 1.29
11/12/20 14.73 82.83 <0.000500 0.00294 <0.000500 <0.000500 <0.000500 <0.00100 0.325 0.357
06/24/21 14.98 82.58 <0.000500 0.00752 <0.000500 <0.000500 <0.000500 <0.00100 0.339 0.491
10/06/21 16.01 81.55 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.374 0.423
12/20/21 16.58 80.98 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.108 0.277
1
03/24/22 17.04 80.52 <0.00114 0.00311 <0.00114 <0.00114 <0.00343 <0.00571 <0.571 0.249
03/09/23 15.73 81.80 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 0.450
06/06/23 13.10 84.43 <0.00100 0.00271 <0.00100 <0.00100 <0.00300 <0.00500 0.950 1.27 J3
09/14/23 14.16 83.37 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 0.786
12/15/23 14.90 82.63 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 0.518 B 5.12 ~
06/26/24 12.36 85.17 <0.00100 0.00221 <0.00100 0.0140 <0.00300 <0.00500
J3 0.616 B 0.786
09/12/24 12.99 84.54 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J4 <0.500 0.822
12/11/24 13.34 84.19 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
0.349 0.790
11/12/20 11.66 84.88 <0.0500 2.29 <0.0500 2.20 0.956 0.283 12.5 6.68
06/24/21 12.37 84.17 <0.0100 0.603 <0.0100 0.812 0.270 0.0300 4.65 4.00
10/06/21 13.69 82.85 <0.0100 0.312 <0.0100 0.741 0.199 0.0221 4.80 3.02
12/20/21 13.96 82.58 <0.00500 0.0449 <0.00500 0.437 0.00959 <0.0100 1.79 2.72
03/24/22 14.86 81.68 <0.00114 0.00768 <0.00114 0.134 <0.00343 <0.00571 <0.571 1.25
11/12/20 13.33 86.06 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.260 0.0515
06/24/21 14.07 85.32 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.178 <0.0517
10/06/21 15.36 84.03 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.298 0.0785
12/20/21 16.15 83.24 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.328 <0.0523
03/24/22 16.90 82.49 <0.00114 <0.00114 <0.00114 <0.00114 <0.00343 <0.00571 <0.571 <0.114
03/10/23 16.18 83.34 <0.00100 <0.00100 <0.00100 0.0173 0.142 0.00877 0.513 1.48
06/07/23 13.26 86.26 <0.00100 <0.00100 <0.00100 0.00778 0.0236 0.00758 0.574 1.80
09/14/23 14.07 85.45 <0.00100 <0.00100 <0.00100 0.00585 0.0297 0.0213 <0.500 1.17
12/15/23 14.35 85.17 <0.00100 <0.00100 <0.00100 0.00164 0.00481 <0.00500 <0.500 <0.100
~
06/26/24 10.77 88.75 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J3 <0.500 0.467
09/12/24 11.34 88.18 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J4 <0.500 0.331
12/11/24 11.41 88.11 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.100 0.213
11/12/20 14.66 85.34 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 <0.0500 <0.0476
06/24/21 15.30 84.70 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 <0.0500 <0.0509
10/06/21 16.36 83.64 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 <0.0500 <0.0537
12/20/21 16.70 83.30 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 <0.0500 <0.0510
03/24/22 17.24 82.76 <0.00114 <0.00114 <0.00114 <0.00114 <0.00343 <0.00571 <0.571 <0.114
0.2 0.005 1.0 0.7 10.0 0.7 1.0 1.0
0.2 0.3 3.0 4.0 10.0 0.7 10 10
Groundwater Analytical Results
Table 1
3185 Harrison Boulevard, Ogden, Utah
7-Eleven Store No. 27074
Sample
Location Date
Depth to
Groundwater
(feet)
Relative
Groundwater
Elevation
(feet)
TPH-DRO
(mg/L)Total Xylenes Ethylbenzene
TPH-GRO
(mg/L)TolueneBenzene
MBTEXN Compounds
(mg/L)
MW-2R
UDEQ DERR Tier 1 Screening Level
MW-4#
MW-5#
MW-6#
UDEQ DERR Initial Screening Level
MW-5R
Naphthalene
MW-1
MW-2#
MW-3
fnl_dbs_27074_20241211-12.xlsx Water 1 of 3 Stantec Consulting Services Inc.
MTBE
Groundwater Analytical Results
Table 1
3185 Harrison Boulevard, Ogden, Utah
7-Eleven Store No. 27074
Sample
Location Date
Depth to
Groundwater
(feet)
Relative
Groundwater
Elevation
(feet)
TPH-DRO
(mg/L)Total Xylenes Ethylbenzene
TPH-GRO
(mg/L)TolueneBenzene
MBTEXN Compounds
(mg/L)
Naphthalene
11/12/20 14.05 81.02 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.386 0.433
06/24/21 14.28 80.79 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.428 0.381
10/06/21 15.08 79.99 <0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.536 0.371
12/20/21 15.43 79.64
<0.000500 <0.000500 <0.000500 <0.000500 <0.000500 <0.00100 0.693 0.479
1
03/24/22 15.79 79.28 <0.00114 <0.00114 <0.00114 <0.00114 <0.00343 <0.00571 0.856 0.458
03/09/23 14.75 80.25 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 0.855 1.24
06/07/23 12.11 82.89 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 0.829 1.09 J3
09/13/23 12.81 82.19 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 1.06
12/15/23 13.84 81.16 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 0.708 B 6.14 ~
06/26/24 11.76 83.24 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J3 0.896 B 0.872
09/12/24 12.42 82.58 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J4 0.766 0.870
12/11/24 12.74 82.26 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 0.384 0.600
03/10/23 14.98 81.29 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 <0.100
06/06/23 12.60 83.67 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 0.258 J3
09/13/23 13.23 83.04 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 0.191
12/15/23 13.90 82.37 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 416 J7,~
06/26/24 11.28 84.99 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J3 <0.500 0.125
09/12/24 11.78 84.49 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J4 <0.500 0.231
12/12/24 12.26 84.01 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.100 0.169
03/10/23 15.05 83.60 <0.00100 <0.00100 <0.00100 0.0132 <0.00300 <0.00500 <0.500 1.56
06/07/23 13.22 85.43 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 0.661
09/13/23 13.93 84.72 <0.00100 <0.00100 <0.00100 0.00785 0.0295 0.00805 <0.500 0.354
12/15/23 14.03 84.62 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.500 0.406 ~
06/26/24 11.08 87.57 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J3 <0.500 0.413
09/12/24 11.11 87.54 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500
J4 <0.500 0.432
12/12/24 11.32 87.33 <0.00100 <0.00100 <0.00100 <0.00100 <0.00300 <0.00500 <0.100 0.313
FD-1 (MW-2)06/24/21 -- --<0.00200 0.0557 <0.00200 0.261 0.0407 0.00665 1.25 0.954
RPD (%)-- -- -- --123%--61% 70% 170% 50% 36%
FD-1 (MW-2)12/20/21 -- --<0.0500 0.533 <0.0500 3.09 1.41 0.832 14.4 5.32
RPD (%)-- -- ---- 25% -- 3% 6% 17% 12% 16%
FD-1 (MW-2)03/24/22 -- --<0.00114 0.888 0.0282 2.06 0.735 0.203 4.08 5.68
RPD (%)-- -- ---- 8% 0% 7% 14% -- 3% 2%
DUP-01 (MW-2R)03/10/23 -- --<0.00100 0.630 0.00531 1.47 0.0779 0.0602
Z1 2.03 7.10
RPD (%)-- -- ---- 15% -- 8% 5% 29% -- 13%
DUP-01 (MW-2R)06/07/23 -- --<0.0500 0.784 <0.0500 1.33 0.366 <0.250 <25.0 12.1
RPD (%)-- -- ---- 5% -- 11% 1% -- -- 7%
DUP-01 (MW-2R)09/14/23 -- --<0.0500 0.243 0.0470 Q 1.05 1.77 0.251 12.50 Q 1.11
RPD (%)-- -- ---- 23% 22% 12% 21% 0% 68% 118%
DUP-01 (MW-2R)12/15/23 -- --<0.00100 0.338 Q,J2 0.0190 J2 1.36 Q,J2 3.00 Q,J2 0.405 10.8 2.97
~
RPD (%)-- -- ---- 7% 23% 16% 20% 36% 3% --
DUP-01 (MW-2R)06/27/24 -- --<0.00100 0.0328 0.00231 0.512
Q 0.662 Q 0.185 J3 4.02 B 2.75
RPD (%)-- -- ---- 40% -- 10% 11% 33% 145% 63%
DUP-01 (MW-2R)09/12/24 -- --<0.00100 0.0460 0.00367 0.420 0.0496 0.0704 <0.500 4.09
RPD (%)-- -- ---- 17% -- 8% 14% 2% -- 17%
DUP-01 (MW-1)12/12/24 -- --<0.00100 0.158 0.00140 1.01 0.0163 0.0456 4.24 4.40
RPD (%)-- -- ---- 16% -- 5% -- 12% 43% 8%
0.2 0.005 1.0 0.7 10.0 0.7 1.0 1.0
0.2 0.3 3.0 4.0 10.0 0.7 10 10
Elevation*
Screened
Interval
(feet)
Total Well
Depth
(feet)
5 to 20
5 to 20
97.57
97.67
Relative Top
(feet)
of Casing
20
20
98.65
96.27
95.00
99.52
97.53
5 to 20
5 to 20
5 to 20
5 to 20
5 to 20
20
20
20
20
20
Well ID
MW-9
MW-8
MW-7
UDEQ DERR Tier 1 Screening Level
UDEQ DERR Initial Screening Level
Q,Z1,J
2
MW-9
MW-8
MW-7
MW-5R
MW-3
MW-2R
MW-1
fnl_dbs_27074_20241211-12.xlsx Water 2 of 3 Stantec Consulting Services Inc.
Groundwater Analytical Results
Table 1
3185 Harrison Boulevard, Ogden, Utah
7-Eleven Store No. 27074
Explanation of Abbreviations
DERR = Department of Environmental Response and Remediation
MBTEXN = methyl tertiary-butyl ether, benzene, toluene, ethylbenzene, total xylenes,
and naphthalene
mg/L = milligrams per liter
MTBE = methyl tertiary-butyl ether
RPD = relative percent difference
TPH-DRO = total petroleum hydrocarbons as diesel-range organics
TPH-GRO = total petroleum hydrocarbons as gasoline-range organics
UDEQ = Utah Department of Environmental Quality
-- = no data
<= analyte not detected above the specified laboratory reporting limit
bold = analyte detected above the specified laboratory reporting limit
bold = analytical result exceeds the specified UDEQ DERR Initial Screening Level
bold = analytical result exceeds the specified UDEQ DERR Initial Screening Level and Tier 1 Screening Level
* = For the original survey data, MW-6 was assigned an arbitrary TOC elevation of 100 feet, and the TOC elevations of the remaining wells
were calculated according to that datum. All wells were re-surveyed on March 9, 2023, and MW-1 was assigned an arbitrary TOC
elevation of 97.67 feet (which was the original calculated relative TOC elevation for MW-1).
#= Wells were abandoned on April 8, 2022 to accommodate UTA construction along Harrison Boulevard. Replacement wells were installed
on February 7 and 8, 2023.
~= The same analyte is found in the field blank.
1 = Laboratory method blank detected TPH-DRO for original analysis. Repeat analysis was completed outside of hold time. Repeat analysis
result was higher than original. Repeat analysis result is reported in table.
B = The same analyte is found in the associated blank.
J2 = Surrogate recovery limits have been exceeded; values are outside lower control limits.
J3 = The associated batch QC was outside the established quality control range for precision.
J4 = The associated batch QC was outside the established quality control range for accuracy.
J7 = Surrogate recovery cannot be used for control limit evaluation due to dilution.
Q = Sample was prepared and/or analyzed past holding time as defined in the method. Concentrations should beconsidered minimum values.
Z1 = The identification of the analyte is acceptable; the reported value is an estimate.
Notes
▪March 24, 2022 samples were collected into 40 mL vials that contained 5 mL of methanol. Reported concentrations include a 40/35 dilution
factor.
▪The first quarter 2023 groundwater monitoring and sampling event was conducted on March 9 and 10. All depth to water measurements were
collected on March 9.
▪The second quarter 2023 groundwater monitoring and sampling event was conducted on June 6 and 7. All depth to water measurements were
collected on June 6.
▪The third quarter 2023 groundwater monitoring and sampling event was conducted on September 13 and 14. All depth to water measurements were
collected on September 13.
▪The second quarter 2024 groundwater monitoring and sampling event was conducted on June 26 and 27. All depth to water measurements were
collected on June 26.
▪The fourth quarter 2024 groundwater monitoring and sampling event was conducted on December 11 and 12. All depth to water measurements were
collected on December 11.
fnl_dbs_27074_20241211-12.xlsx Water 3 of 3 Stantec Consulting Services Inc.
GRAPHS
GRAPH 1
MW-1 Select Concentration vs. Time Graphs
10
11
12
13
14
15
160.001
0.010
0.100
1.000
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 1A
7-Eleven Store No. 27074
MW-1 Benzene Concentration vs. Time
ISL TSL Benzene Depth to Groundwater
10
11
12
13
14
15
160.01
0.10
1.00
10.00
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 1B
7-Eleven Store No. 27074
MW-1 Ethylebenzene Concentration vs. Time
ISL TSL Ethylbenzene Depth to Groundwater
10
11
12
13
14
15
160.1
1.0
10.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Ja
n
-
2
3
Ma
y
-
2
3
Ju
l
-
2
3
Oc
t
-
2
3
Ja
n
-
2
4
Ap
r
-
2
4
Ju
l
-
2
4
Oc
t
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 1C
7-Eleven Store No. 27074
MW-1 TPH-GRO Concentration vs. Time
ISL TSL TPH-GRO Depth to Groundwater
10
11
12
13
14
15
160.1
1.0
10.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 1D
7-Eleven Store No. 27074
MW-1 TPH-DRO Concentration vs. Time
ISL TSL TPH-DRO Depth to Groundwater
GRAPH 2
MW-2/2R Select Concentration vs. Time Graphs
10
11
12
13
14
15
0.001
0.010
0.100
1.000
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 2A
7-Eleven Store No. 27074
MW-2/2R Benzene Concentration vs. Time
ISL TSL Benzene Depth to Groundwater
*Closed markers indicate MW-2R data.
10
11
12
13
14
15
0.1
1.0
10.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 2B
7-Eleven Store No. 27074
MW-2/2R Ethylebenzene Concentration vs. Time
ISL TSL Ethylbenzene Depth to Groundwater
*Closed markers indicate MW-2R data.
10
11
12
13
14
15
0.1
1.0
10.0
100.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Ja
n
-
2
3
Ma
y
-
2
3
Ju
l
-
2
3
Oc
t
-
2
3
Ja
n
-
2
4
Ap
r
-
2
4
Ju
l
-
2
4
Oc
t
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 2C
7-Eleven Store No. 27074
MW-2/2R TPH-GRO Concentration vs. Time
ISL TSL TPH-GRO Depth to Groundwater
*Closed markers indicate MW-2R data.
DUP-01 data used to plot 03/10/23 and 9/12/24 results.
10
11
12
13
14
15
0.1
1.0
10.0
100.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 2D
7-Eleven Store No. 27074
MW-2/2R TPH-DRO Concentration vs. Time
ISL TSL TPH-DRO Depth to Groundwater
*Closed markers indicate MW-2R data.
GRAPH 3
MW-3 Select Concentration vs. Time Graphs
12
13
14
15
16
17
0.0001
0.0010
0.0100
0.1000
1.0000
Ju
l
-
2
0
Oc
t
-
2
0
Ja
n
-
2
1
Ap
r
-
2
1
Ju
l
-
2
1
Oc
t
-
2
1
Ja
n
-
2
2
Ap
r
-
2
2
Ju
l
-
2
2
Oc
t
-
2
2
Ja
n
-
2
3
Ap
r
-
2
3
Ju
l
-
2
3
Oc
t
-
2
3
Ja
n
-
2
4
Ap
r
-
2
4
Ju
l
-
2
4
Oc
t
-
2
4
De
c
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 3A
7-Eleven Store No. 27074
MW-3 Benzene Concentration vs. Time
ISL TSL Benzene Depth to Groundwater
12
13
14
15
16
17
0.1
1.0
10.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Ja
n
-
2
3
Ma
y
-
2
3
Ju
l
-
2
3
Oc
t
-
2
3
Ja
n
-
2
4
Ap
r
-
2
4
Ju
l
-
2
4
Oc
t
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 3B
7-Eleven Store No. 27074
MW-3 TPH-GRO Concentration vs. Time
ISL TSL TPH-GRO Depth to Groundwater
12
13
14
15
16
17
0.1
1.0
10.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 3C
7-Eleven Store No. 27074
MW-3 TPH-DRO Concentration vs. Time
ISL TSL TPH-DRO Depth to Groundwater
GRAPH 4
MW-5/5R Select Concentration vs. Time Graphs
10
11
12
13
14
15
16
170.1
1.0
10.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Ja
n
-
2
3
Ma
y
-
2
3
Ju
l
-
2
3
Oc
t
-
2
3
Ja
n
-
2
4
Ap
r
-
2
4
Ju
l
-
2
4
Oc
t
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 4A
7-Eleven Store No. 27074
MW-5/5R TPH-GRO Concentration vs. Time
ISL TSL TPH-GRO Depth to Groundwater
*Closed markers indicate MW-5R data.
10
11
12
13
14
15
16
170.01
0.10
1.00
10.00
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Ja
n
-
2
3
Ma
y
-
2
3
Ju
l
-
2
3
Oc
t
-
2
3
Ja
n
-
2
4
Ap
r
-
2
4
Ju
l
-
2
4
Oc
t
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 4A
7-Eleven Store No. 27074
MW-5/5R TPH-DRO Concentration vs. Time
ISL TSL TPH-DRO Depth to Groundwater
*Closed markers indicate MW-5R data.
11
12
13
14
15
160.1
1.0
10.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 5A
7-Eleven Store No. 27074
MW-7 TPH-GRO Concentration vs. Time
ISL TSL TPH-GRO Depth to Groundwater
11
12
13
14
15
16
170.1
1.0
10.0
No
v
-
2
0
Fe
b
-
2
1
Ma
y
-
2
1
Au
g
-
2
1
No
v
-
2
1
Fe
b
-
2
2
Ma
y
-
2
2
Au
g
-
2
2
No
v
-
2
2
Fe
b
-
2
3
Ma
y
-
2
3
Au
g
-
2
3
No
v
-
2
3
Fe
b
-
2
4
Ma
y
-
2
4
Au
g
-
2
4
No
v
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
GRAPH 5B
7-Eleven Store No. 27074
MW-7 TPH-DRO Concentration vs. Time
ISL TSL TPH-DRO Depth to Groundwater
GRAPH 5
MW-7 Select Concentration vs. Time Graphs
11
12
13
14
15
160.1
1.0
10.0
100.0
1,000.0
Ma
r
-
2
3
Ju
n
-
2
3
Se
p
-
2
3
De
c
-
2
3
Ma
r
-
2
4
Ju
n
-
2
4
Se
p
-
2
4
De
c
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
ISL TSL TPH-DRO Depth to Groundwater
GRAPH 6
7-Eleven Store No. 27074
MW-8 TPH-DRO Concentration vs. Time
GRAPH 7
7-Eleven Store No. 27074
MW-9 TPH-DRO Concentration vs. Time
11
12
13
14
15
160.1
1.0
10.0
Ma
r
-
2
3
Ju
n
-
2
3
Se
p
-
2
3
De
c
-
2
3
Ma
r
-
2
4
Ju
n
-
2
4
Se
p
-
2
4
De
c
-
2
4
De
p
t
h
t
o
G
r
o
u
n
d
w
a
t
e
r
(
f
e
e
t
)
Co
n
c
e
n
t
r
a
t
i
o
n
(
m
g
/
L
)
DATE
ISL TSL TPH-DRO Depth to Groundwater
ATTACHMENT 1
Laboratory Report and Chain-of-Custody Documentation
ANALYTICAL REPORT
December 26, 2024
711 Stantec - Salt Lake City, UT
Sample Delivery Group:L1809483
Samples Received:12/13/2024
Project Number:203721870
Description:7-11 #27074 Ogden, UT
Site:27074
Report To:Anna Skinner
2890 E Cottonwood Pkwy
Suite 300
Salt Lake City, UT 84121
Entire Report Reviewed By:
December 26, 2024
[Preliminary Report]
Marty Edwards III
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 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
711 Stantec - Salt Lake City, UT 203721870 L1809483 12/26/24 18:05 1 of 22
December 26, 2024
Marty Edwards III
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
711 Stantec - Salt Lake City, UT 203721870 L1809483 12/26/24 18:11 1 of 22
TABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 3
Cn: Case Narrative 5
Sr: Sample Results 6
MW-1 L1809483-01 6
MW-2R L1809483-02 7
MW-3 L1809483-03 8
MW-5R L1809483-04 9
MW-7 L1809483-05 10
MW-8 L1809483-06 11
MW-9 L1809483-07 12
DUP-01 L1809483-08 13
TRIP BLANK L1809483-09 14
Qc: Quality Control Summary 15
Volatile Organic Compounds (GC) by Method 8015D/GRO 15
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 17
Semi-Volatile Organic Compounds (GC) by Method 8015D 19
Gl: Glossary of Terms 20
Al: Accreditations & Locations 21
Sc: Sample Chain of Custody 22
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
711 Stantec - Salt Lake City, UT 203721870 L1809483 12/26/24 18:05 2 of 22
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
711 Stantec - Salt Lake City, UT 203721870 L1809483 12/26/24 18:11 2 of 22
SAMPLE SUMMARY
Collected by Collected date/time Received date/time
MW-1 L1809483-01 GW Andrew Huffman 12/12/24 12:30 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC) by Method 8015D/GRO WG2422096 5 12/20/24 14:33 12/20/24 14:33 JBE Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2423378 50 12/22/24 02:52 12/22/24 02:52 JBE Mt. Juliet, TN
Semi-Volatile Organic Compounds (GC) by Method 8015D WG2421585 1 12/19/24 08:11 12/19/24 21:54 TJD Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-2R L1809483-02 GW Andrew Huffman 12/12/24 12:00 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC) by Method 8015D/GRO WG2422096 1 12/20/24 14:12 12/20/24 14:12 JBE Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2424149 5 12/25/24 04:26 12/25/24 04:26 DWR Mt. Juliet, TN
Semi-Volatile Organic Compounds (GC) by Method 8015D WG2421585 1 12/19/24 08:11 12/19/24 22:15 TJD Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-3 L1809483-03 GW Andrew Huffman 12/11/24 14:35 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC) by Method 8015D/GRO WG2421000 1 12/18/24 15:17 12/18/24 15:17 JAH Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2423378 1 12/21/24 23:08 12/21/24 23:08 JBE Mt. Juliet, TN
Semi-Volatile Organic Compounds (GC) by Method 8015D WG2421585 1 12/19/24 08:11 12/19/24 22:35 TJD Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-5R L1809483-04 GW Andrew Huffman 12/11/24 15:35 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC) by Method 8015D/GRO WG2421000 1 12/18/24 15:40 12/18/24 15:40 JAH Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2423378 1 12/21/24 23:29 12/21/24 23:29 JBE Mt. Juliet, TN
Semi-Volatile Organic Compounds (GC) by Method 8015D WG2421585 1 12/19/24 08:11 12/19/24 22:56 TJD Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-7 L1809483-05 GW Andrew Huffman 12/11/24 13:35 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC) by Method 8015D/GRO WG2421000 1 12/18/24 16:03 12/18/24 16:03 JAH Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2423378 1 12/21/24 23:49 12/21/24 23:49 JBE Mt. Juliet, TN
Semi-Volatile Organic Compounds (GC) by Method 8015D WG2421585 1 12/19/24 08:11 12/19/24 23:17 TJD Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-8 L1809483-06 GW Andrew Huffman 12/12/24 11:00 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC) by Method 8015D/GRO WG2421000 1 12/18/24 16:26 12/18/24 16:26 JAH Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2423378 1 12/22/24 00:10 12/22/24 00:10 JBE Mt. Juliet, TN
Semi-Volatile Organic Compounds (GC) by Method 8015D WG2421585 1 12/19/24 08:11 12/19/24 23:37 TJD Mt. Juliet, TN
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
MW-9 L1809483-07 GW Andrew Huffman 12/12/24 10:05 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC) by Method 8015D/GRO WG2421000 1 12/18/24 16:49 12/18/24 16:49 JAH Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2423378 1 12/22/24 00:30 12/22/24 00:30 JBE Mt. Juliet, TN
Semi-Volatile Organic Compounds (GC) by Method 8015D WG2421585 1 12/19/24 08:11 12/20/24 01:22 TJD Mt. Juliet, TN
Collected by Collected date/time Received date/time
DUP-01 L1809483-08 GW Andrew Huffman 12/12/24 00:00 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC) by Method 8015D/GRO WG2421000 1 12/18/24 17:12 12/18/24 17:12 JAH Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B WG2424149 25 12/25/24 04:47 12/25/24 04:47 DWR Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2423378 1 12/22/24 00:50 12/22/24 00:50 JBE Mt. Juliet, TN
Semi-Volatile Organic Compounds (GC) by Method 8015D WG2421585 1 12/19/24 08:11 12/20/24 01:42 TJD Mt. Juliet, TN
Collected by Collected date/time Received date/time
TRIP BLANK L1809483-09 GW Andrew Huffman 12/12/24 00:00 12/13/24 08:00
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 WG2423378 1 12/21/24 22:48 12/21/24 22:48 JBE Mt. Juliet, TN
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 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]
Marty Edwards III
Project Manager
Sample Delivery Group (SDG) Narrative
pH outside of method requirement.
Lab Sample ID Project Sample ID Method
L1809483-03 MW-3 8015D
L1809483-04 MW-5R 8015D
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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Marty Edwards III
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 01
L1809483
MW-1
Collected date/time: 12/12/24 12:30
Volatile Organic Compounds (GC) by Method 8015D/GRO
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) Low Fraction 2.74 0.500 5 12/20/2024 14:33 WG2422096
(S) a,a,a-Trifluorotoluene(FID)85.3 78.0-120 12/20/2024 14:33 WG2422096
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene 0.185 0.0500 50 12/22/2024 02:52 WG2423378
Toluene ND 0.0500 50 12/22/2024 02:52 WG2423378
Ethylbenzene 0.959 0.0500 50 12/22/2024 02:52 WG2423378
Xylenes, Total ND 0.150 50 12/22/2024 02:52 WG2423378
Methyl tert-butyl ether ND 0.00505 50 12/22/2024 02:52 WG2423378
Naphthalene 0.0516 Z1 0.0500 50 12/22/2024 02:52 WG2423378
(S) Toluene-d8 104 80.0-120 12/22/2024 02:52 WG2423378
(S) 4-Bromofluorobenzene 96.3 77.0-126 12/22/2024 02:52 WG2423378
(S) 1,2-Dichloroethane-d4 99.4 70.0-130 12/22/2024 02:52 WG2423378
Sample Narrative:
L1809483-01 WG2423378: MTBE and Naphthalene were reported to the MDL.
Semi-Volatile Organic Compounds (GC) by Method 8015D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) High Fraction 4.07 0.100 1 12/19/2024 21:54 WG2421585
(S) o-Terphenyl 113 52.0-156 12/19/2024 21:54 WG2421585
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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SAMPLE RESULTS - 02
L1809483
MW-2R
Collected date/time: 12/12/24 12:00
Volatile Organic Compounds (GC) by Method 8015D/GRO
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) Low Fraction 0.552 0.100 1 12/20/2024 14:12 WG2422096
(S) a,a,a-Trifluorotoluene(FID)85.8 78.0-120 12/20/2024 14:12 WG2422096
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene 0.00415 Z1 0.000471 5 12/25/2024 04:26 WG2424149
Toluene ND 0.00500 5 12/25/2024 04:26 WG2424149
Ethylbenzene 0.108 0.00500 5 12/25/2024 04:26 WG2424149
Xylenes, Total ND 0.0150 5 12/25/2024 04:26 WG2424149
Methyl tert-butyl ether ND 0.00500 5 12/25/2024 04:26 WG2424149
Naphthalene ND 0.0250 5 12/25/2024 04:26 WG2424149
(S) Toluene-d8 111 80.0-120 12/25/2024 04:26 WG2424149
(S) 4-Bromofluorobenzene 94.4 77.0-126 12/25/2024 04:26 WG2424149
(S) 1,2-Dichloroethane-d4 101 70.0-130 12/25/2024 04:26 WG2424149
Sample Narrative:
L1809483-02 WG2424149: Dilution due to matrix. Benzene was reported to the MDL.
Semi-Volatile Organic Compounds (GC) by Method 8015D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) High Fraction 1.29 0.100 1 12/19/2024 22:15 WG2421585
(S) o-Terphenyl 98.9 52.0-156 12/19/2024 22:15 WG2421585
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 03
L1809483
MW-3
Collected date/time: 12/11/24 14:35
Volatile Organic Compounds (GC) by Method 8015D/GRO
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) Low Fraction 0.349 0.100 1 12/18/2024 15:17 WG2421000
(S) a,a,a-Trifluorotoluene(FID)97.5 78.0-120 12/18/2024 15:17 WG2421000
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene ND 0.00100 1 12/21/2024 23:08 WG2423378
Toluene ND 0.00100 1 12/21/2024 23:08 WG2423378
Ethylbenzene ND 0.00100 1 12/21/2024 23:08 WG2423378
Xylenes, Total ND 0.00300 1 12/21/2024 23:08 WG2423378
Methyl tert-butyl ether ND 0.00100 1 12/21/2024 23:08 WG2423378
Naphthalene ND 0.00500 1 12/21/2024 23:08 WG2423378
(S) Toluene-d8 107 80.0-120 12/21/2024 23:08 WG2423378
(S) 4-Bromofluorobenzene 96.0 77.0-126 12/21/2024 23:08 WG2423378
(S) 1,2-Dichloroethane-d4 98.8 70.0-130 12/21/2024 23:08 WG2423378
Semi-Volatile Organic Compounds (GC) by Method 8015D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) High Fraction 0.790 0.100 1 12/19/2024 22:35 WG2421585
(S) o-Terphenyl 98.4 52.0-156 12/19/2024 22:35 WG2421585
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 04
L1809483
MW-5R
Collected date/time: 12/11/24 15:35
Volatile Organic Compounds (GC) by Method 8015D/GRO
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) Low Fraction ND 0.100 1 12/18/2024 15:40 WG2421000
(S) a,a,a-Trifluorotoluene(FID)98.8 78.0-120 12/18/2024 15:40 WG2421000
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene ND 0.00100 1 12/21/2024 23:29 WG2423378
Toluene ND 0.00100 1 12/21/2024 23:29 WG2423378
Ethylbenzene ND 0.00100 1 12/21/2024 23:29 WG2423378
Xylenes, Total ND 0.00300 1 12/21/2024 23:29 WG2423378
Methyl tert-butyl ether ND 0.00100 1 12/21/2024 23:29 WG2423378
Naphthalene ND 0.00500 1 12/21/2024 23:29 WG2423378
(S) Toluene-d8 108 80.0-120 12/21/2024 23:29 WG2423378
(S) 4-Bromofluorobenzene 101 77.0-126 12/21/2024 23:29 WG2423378
(S) 1,2-Dichloroethane-d4 100 70.0-130 12/21/2024 23:29 WG2423378
Semi-Volatile Organic Compounds (GC) by Method 8015D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) High Fraction 0.213 0.100 1 12/19/2024 22:56 WG2421585
(S) o-Terphenyl 98.9 52.0-156 12/19/2024 22:56 WG2421585
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 05
L1809483
MW-7
Collected date/time: 12/11/24 13:35
Volatile Organic Compounds (GC) by Method 8015D/GRO
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) Low Fraction 0.384 0.100 1 12/18/2024 16:03 WG2421000
(S) a,a,a-Trifluorotoluene(FID)98.3 78.0-120 12/18/2024 16:03 WG2421000
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene ND 0.00100 1 12/21/2024 23:49 WG2423378
Toluene ND 0.00100 1 12/21/2024 23:49 WG2423378
Ethylbenzene ND 0.00100 1 12/21/2024 23:49 WG2423378
Xylenes, Total ND 0.00300 1 12/21/2024 23:49 WG2423378
Methyl tert-butyl ether ND 0.00100 1 12/21/2024 23:49 WG2423378
Naphthalene ND 0.00500 1 12/21/2024 23:49 WG2423378
(S) Toluene-d8 105 80.0-120 12/21/2024 23:49 WG2423378
(S) 4-Bromofluorobenzene 93.4 77.0-126 12/21/2024 23:49 WG2423378
(S) 1,2-Dichloroethane-d4 97.9 70.0-130 12/21/2024 23:49 WG2423378
Semi-Volatile Organic Compounds (GC) by Method 8015D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) High Fraction 0.600 0.100 1 12/19/2024 23:17 WG2421585
(S) o-Terphenyl 108 52.0-156 12/19/2024 23:17 WG2421585
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 06
L1809483
MW-8
Collected date/time: 12/12/24 11:00
Volatile Organic Compounds (GC) by Method 8015D/GRO
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) Low Fraction ND 0.100 1 12/18/2024 16:26 WG2421000
(S) a,a,a-Trifluorotoluene(FID)98.7 78.0-120 12/18/2024 16:26 WG2421000
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene ND 0.00100 1 12/22/2024 00:10 WG2423378
Toluene ND 0.00100 1 12/22/2024 00:10 WG2423378
Ethylbenzene ND 0.00100 1 12/22/2024 00:10 WG2423378
Xylenes, Total ND 0.00300 1 12/22/2024 00:10 WG2423378
Methyl tert-butyl ether ND 0.00100 1 12/22/2024 00:10 WG2423378
Naphthalene ND 0.00500 1 12/22/2024 00:10 WG2423378
(S) Toluene-d8 109 80.0-120 12/22/2024 00:10 WG2423378
(S) 4-Bromofluorobenzene 96.1 77.0-126 12/22/2024 00:10 WG2423378
(S) 1,2-Dichloroethane-d4 105 70.0-130 12/22/2024 00:10 WG2423378
Semi-Volatile Organic Compounds (GC) by Method 8015D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) High Fraction 0.169 0.100 1 12/19/2024 23:37 WG2421585
(S) o-Terphenyl 94.7 52.0-156 12/19/2024 23:37 WG2421585
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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711 Stantec - Salt Lake City, UT 203721870 L1809483 12/26/24 18:11 11 of 22
SAMPLE RESULTS - 07
L1809483
MW-9
Collected date/time: 12/12/24 10:05
Volatile Organic Compounds (GC) by Method 8015D/GRO
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) Low Fraction ND 0.100 1 12/18/2024 16:49 WG2421000
(S) a,a,a-Trifluorotoluene(FID)98.4 78.0-120 12/18/2024 16:49 WG2421000
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene ND 0.00100 1 12/22/2024 00:30 WG2423378
Toluene ND 0.00100 1 12/22/2024 00:30 WG2423378
Ethylbenzene ND 0.00100 1 12/22/2024 00:30 WG2423378
Xylenes, Total ND 0.00300 1 12/22/2024 00:30 WG2423378
Methyl tert-butyl ether ND 0.00100 1 12/22/2024 00:30 WG2423378
Naphthalene ND 0.00500 1 12/22/2024 00:30 WG2423378
(S) Toluene-d8 102 80.0-120 12/22/2024 00:30 WG2423378
(S) 4-Bromofluorobenzene 101 77.0-126 12/22/2024 00:30 WG2423378
(S) 1,2-Dichloroethane-d4 99.1 70.0-130 12/22/2024 00:30 WG2423378
Semi-Volatile Organic Compounds (GC) by Method 8015D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) High Fraction 0.313 0.100 1 12/20/2024 01:22 WG2421585
(S) o-Terphenyl 86.3 52.0-156 12/20/2024 01:22 WG2421585
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
711 Stantec - Salt Lake City, UT 203721870 L1809483 12/26/24 18:11 12 of 22
SAMPLE RESULTS - 08
L1809483
DUP-01
Collected date/time: 12/12/24 00:00
Volatile Organic Compounds (GC) by Method 8015D/GRO
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) Low Fraction 4.24 0.100 1 12/18/2024 17:12 WG2421000
(S) a,a,a-Trifluorotoluene(FID)102 78.0-120 12/18/2024 17:12 WG2421000
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene 0.158 0.00100 1 12/22/2024 00:50 WG2423378
Toluene 0.00140 0.00100 1 12/22/2024 00:50 WG2423378
Ethylbenzene 1.01 0.0250 25 12/25/2024 04:47 WG2424149
Xylenes, Total 0.0163 0.00300 1 12/22/2024 00:50 WG2423378
Methyl tert-butyl ether ND 0.00100 1 12/22/2024 00:50 WG2423378
Naphthalene 0.0456 0.00500 1 12/22/2024 00:50 WG2423378
(S) Toluene-d8 107 80.0-120 12/22/2024 00:50 WG2423378
(S) Toluene-d8 112 80.0-120 12/25/2024 04:47 WG2424149
(S) 4-Bromofluorobenzene 105 77.0-126 12/22/2024 00:50 WG2423378
(S) 4-Bromofluorobenzene 93.0 77.0-126 12/25/2024 04:47 WG2424149
(S) 1,2-Dichloroethane-d4 96.9 70.0-130 12/22/2024 00:50 WG2423378
(S) 1,2-Dichloroethane-d4 99.2 70.0-130 12/25/2024 04:47 WG2424149
Semi-Volatile Organic Compounds (GC) by Method 8015D
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
TPH (GC/FID) High Fraction 4.40 0.100 1 12/20/2024 01:42 WG2421585
(S) o-Terphenyl 114 52.0-156 12/20/2024 01:42 WG2421585
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
711 Stantec - Salt Lake City, UT 203721870 L1809483 12/26/24 18:11 13 of 22
SAMPLE RESULTS - 09
L1809483
TRIP BLANK
Collected date/time: 12/12/24 00:00
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1
Result Qualifier RDL Dilution Analysis Batch
Analyte mg/l mg/l date / time
Benzene ND 0.00100 1 12/21/2024 22:48 WG2423378
Toluene ND 0.00100 1 12/21/2024 22:48 WG2423378
Ethylbenzene ND 0.00100 1 12/21/2024 22:48 WG2423378
Xylenes, Total ND 0.00300 1 12/21/2024 22:48 WG2423378
Methyl tert-butyl ether ND 0.00100 1 12/21/2024 22:48 WG2423378
Naphthalene ND 0.00500 1 12/21/2024 22:48 WG2423378
(S) Toluene-d8 108 80.0-120 12/21/2024 22:48 WG2423378
(S) 4-Bromofluorobenzene 102 77.0-126 12/21/2024 22:48 WG2423378
(S) 1,2-Dichloroethane-d4 102 70.0-130 12/21/2024 22:48 WG2423378
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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QUALITY CONTROL SUMMARYWG2421000
Volatile Organic Compounds (GC) by Method 8015D/GRO L1809483-03,04,05,06,07,08
Method Blank (MB)
(MB) R4159879-3 12/18/24 12:37
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
TPH (GC/FID) Low Fraction U 0.0314 0.100
(S)
a,a,a-Trifluorotoluene(FID)99.3 78.0-120
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R4159879-1 12/18/24 11:29 • (LCSD) R4159879-2 12/18/24 11:52
Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte mg/l mg/l mg/l %%%%%
TPH (GC/FID) Low Fraction 5.00 5.22 5.56 104 111 72.0-127 6.31 20
(S)
a,a,a-Trifluorotoluene(FID) 105 106 78.0-120
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2422096
Volatile Organic Compounds (GC) by Method 8015D/GRO L1809483-01,02
Method Blank (MB)
(MB) R4160990-2 12/20/24 12:42
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
TPH (GC/FID) Low Fraction U 0.0314 0.100
(S)
a,a,a-Trifluorotoluene(FID)86.4 78.0-120
Laboratory Control Sample (LCS)
(LCS) R4160990-1 12/20/24 11:59
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte mg/l mg/l %%
TPH (GC/FID) Low Fraction 5.00 5.21 104 72.0-127
(S)
a,a,a-Trifluorotoluene(FID) 93.0 78.0-120
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2423378
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 L1809483-01,03,04,05,06,07,08,09
Method Blank (MB)
(MB) R4161252-3 12/21/24 22:28
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
Benzene U 0.0000941 0.00100
Toluene U 0.000278 0.00100
Ethylbenzene U 0.000137 0.00100
Xylenes, Total U 0.000174 0.00300
Methyl tert-butyl ether U 0.000101 0.00100
Naphthalene U 0.00100 0.00500
(S) Toluene-d8 112 80.0-120
(S) 4-Bromofluorobenzene 101 77.0-126
(S) 1,2-Dichloroethane-d4 103 70.0-130
Laboratory Control Sample (LCS)
(LCS) R4161252-1 12/21/24 21:27
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte mg/l mg/l %%
Benzene 0.00500 0.00558 112 70.0-123
Toluene 0.00500 0.00494 98.8 79.0-120
Ethylbenzene 0.00500 0.00523 105 79.0-123
Xylenes, Total 0.0150 0.0149 99.3 79.0-123
Methyl tert-butyl ether 0.00500 0.00560 112 68.0-125
Naphthalene 0.00500 0.00336 67.2 54.0-135
(S) Toluene-d8 98.7 80.0-120
(S) 4-Bromofluorobenzene 89.1 77.0-126
(S) 1,2-Dichloroethane-d4 100 70.0-130
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2424149
Volatile Organic Compounds (GC/MS) by Method 8260B/8260B/OA1 L1809483-02,08
Method Blank (MB)
(MB) R4162028-5 12/24/24 23:32
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
Benzene U 0.0000941 0.00100
Toluene U 0.000278 0.00100
Ethylbenzene U 0.000137 0.00100
Xylenes, Total U 0.000174 0.00300
Methyl tert-butyl ether U 0.000101 0.00100
Naphthalene U 0.00100 0.00500
(S) Toluene-d8 118 80.0-120
(S) 4-Bromofluorobenzene 97.0 77.0-126
(S) 1,2-Dichloroethane-d4 98.1 70.0-130
Laboratory Control Sample (LCS)
(LCS) R4162028-1 12/24/24 21:47
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte mg/l mg/l %%
Benzene 0.00500 0.00496 99.2 70.0-123
Toluene 0.00500 0.00527 105 79.0-120
Ethylbenzene 0.00500 0.00514 103 79.0-123
Xylenes, Total 0.0150 0.0159 106 79.0-123
Methyl tert-butyl ether 0.00500 0.00499 99.8 68.0-125
Naphthalene 0.00500 0.00497 99.4 54.0-135
(S) Toluene-d8 110 80.0-120
(S) 4-Bromofluorobenzene 93.4 77.0-126
(S) 1,2-Dichloroethane-d4 99.8 70.0-130
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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QUALITY CONTROL SUMMARYWG2421585
Semi-Volatile Organic Compounds (GC) by Method 8015D L1809483-01,02,03,04,05,06,07,08
Method Blank (MB)
(MB) R4160096-1 12/19/24 16:43
MB Result MB Qualifier MB MDL MB RDL
Analyte mg/l mg/l mg/l
TPH (GC/FID) High Fraction U 0.0605 0.100
(S) o-Terphenyl 96.5 52.0-156
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R4160096-2 12/19/24 17:04 • (LCSD) R4160096-3 12/19/24 17:25
Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte mg/l mg/l mg/l %%%%%
TPH (GC/FID) High Fraction 1.50 1.57 1.64 105 109 50.0-150 4.36 20
(S) o-Terphenyl 106 94.5 52.0-156
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 Sc
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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
MDL Method Detection Limit.
ND Not detected at the Reporting Limit (or MDL where applicable).
RDL Reported Detection Limit.
Rec.Recovery.
RPD Relative Percent Difference.
SDG Sample Delivery Group.
(S)
Surrogate (Surrogate Standard) - Analytes added to every blank, sample, Laboratory Control Sample/Duplicate and
Matrix Spike/Duplicate; used to evaluate analytical efficiency by measuring recovery. Surrogates are not expected to be
detected in all environmental media.
U Not detected at the Reporting Limit (or MDL where applicable).
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.
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
Z1 The identification of the analyte is acceptable; the reported value is an estimate.
1 Cp
2 Tc
3 Ss
4 Cn
5 Sr
6 Qc
7 Gl
8 Al
9 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
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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 Sr
6 Qc
7 Gl
8 Al
9 Sc
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