HomeMy WebLinkAboutAS-3241_28414_CA_MRP_20220124_ALLJanuary 24, 2022
Mr. Dan Murphy
North Carolina Department of Environmental Quality
Division of Waste Management, UST Section
Asheville Regional Office
2090 U.S. Highway 70
Swannanoa, North Carolina 28778
Subject:Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
502 Wilkseboro Boulevard SE
Lenoir, Caldwell County,North Carolina
Incident No: 28414
Mid-Atlantic Project No.:R1760.25
Dear Mr. Murphy:
Speedway LLC is pleased to present this report of environmental services for the
above-referenced facility. This report documents the results of the groundwater
monitoring and surface water sampling activities conducted at the site on December 20,
2021. If you have any questions, please feel free to contact me at (919) 516-8069 or
Cameron Moore with Mid-Atlantic Associates, Inc. at (980) 585-1271.
Sincerely,
SPEEDWAY LLC
Charles A. Chiara
Environmental Representative
Located at:
502 Wilkseboro Boulevard SE
Lenoir,Caldwell County,North Carolina
Prepared for (Users):
Speedway LLC
500 Speedway Drive
Enon,Ohio 45323
919-516-8069
Report Date: January 24, 2022
MAA Project: R1760.25
Groundwater
Monitoring Report
Speedway 7972
(Former WilcoHess
353)
Facility ID#:0-033119
502 Wilkseboro
Boulevard SE
Lenoir,North Carolina
Incident No.:28414
Prepared By:
Mid-Atlantic Associates, Inc.
409 Rogers View Court,
Raleigh,North Carolina 27610
(919) 250-9918
GROUNDWATER MONITORING REPORT
A. SITE INFORMATION
1. Site Identification
Date of Report:January 24, 2022
Facility ID:0-033119 UST Incident No. (if known):28414
Site Risk:Intermediate Site Rank:I-184-D Land Use Classification:Commercial/Industrial
Site Name:Speedway 7972 (Former WilcoHess 353)
Site Location:502 Wilkseboro Boulevard SE,Lenoir,North Carolina
Nearest City/Town:Lenoir County:Caldwell
Latitude:35.916295 N Longitude:-81.516153 W
Description of Geographical Data
Point:
Site Property
Location Method:Google Earth
2. Information about Contacts Associated with the Leaking UST System
UST Owner:Speedway LLC
Address:500 Speedway Drive, Enon, Ohio 45323 Phone:(919) 516-8069
UST Operator:Same as UST Owner
Address:Phone:
Property Owner:Same as UST Owner
Address:Phone:
Property Occupant:Same as UST Owner
Address:Phone:
Consultant/Contractor:Mid-Atlantic Associates, Inc.
Address:409 Rogers View Ct., Raleigh, NC 27610 Phone:(919) 250-9918
3. Release Information
Date Discovered:July 18, 2006
Estimated Quantity of Release:Unknown
Cause of Release:Unknown, gasoline free product found in tank pit observation wells
Source of Release (Piping/UST):Gasoline UST system
Sizes and contents of UST system(s) from which release occurred:Three 12,000-gallon gasoline USTs (source is unclear)
I,Cameron D. Moore, PG ,a Licensed Geologist for Mid-Atlantic Associates, Inc., do certify that the information contained
in this report is correct and accurate to the best of my knowledge. Mid-Atlantic Associates, Inc. is licensed to geology and
engineering in North Carolina. The certification numbers of the corporation are:C-186 and F-0967.
(Please affix seal and signature)
TABLE OF CONTENTS
1.0 BACKGROUND INFORMATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
2.0 SITE HISTORY AND SOURCE CHARACTERIZATION . . . . . . . . . . . . . . . . . . . . 2
2.1 UST Information . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
2.2 UST System Owner/Operator . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
2.3 Information on Source of Release . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
2.4 Regional Geology and Hydrogeology . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3
2.5 Site Geology and Hydrogeology . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3
3.0 POTENTIAL RECEPTORS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3
4.0 FIELD ACTIVITIES . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
4.1 Liquid Level Measurements . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
4.2 Monitoring Well Sample Collection . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
4.3 Surface Water Sample Collection . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
5.0 DISCUSSION OF SAMPLING RESULTS . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5
5.1 Summary of Analytical Results . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5
5.2 Description of Current Plume Size and Location . . . . . . . . . . . . . . . . . . . . . 5
5.3 Additional Monitoring Information . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6
6.0 FUTURE SITE REMEDIATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7
7.0 SUMMARY, CONCLUSIONS, AND RECOMMENDATIONS . . . . . . . . . . . . . . . . 7
8.0 STATEMENTS AND CERTIFICATION . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8
APPENDICES
Drawings
Tables
Appendix A Selected Historical Site Information
Appendix B Mid-Atlantic Field Procedures
Appendix C Laboratory Analytical Reports and Chain-of-Custody Records for
Groundwater & Surface Water Samples
1.0 BACKGROUND INFORMATION
The subject site is the Speedway 7972 (former WilcoHess 353) located at 502
Wilkesboro Boulevard SE in Lenoir, North Carolina (Drawing 1.1). On October 1, 2014,
Speedway LLC acquired the site from Hess Corporation, who had previously acquired
the site from WilcoHess LLC. The site is currently in use as a convenience store and retail
petroleum dispensing facility. The facility operates three 12,000-gallon gasoline USTs,
one 12,000-gallon diesel UST, and one 10,000-gallon kerosene UST. The layout of the
facility is shown on Drawing 1.2.
Gasoline free product was historically present on the water table in monitoring wells
MW-1 and MW-8.Free product, which had not been detected in MW-1 since August
2011, was present in the well during Mid-Atlantic's June 8, 2021 groundwater monitoring
event. Prior to the start of a Mobile Multi Phase Extraction (MMPE) event on MW-1 on
November 15, 2021, free product was also detected in MW-8 for the first time since
August 2012. The site is currently classified as intermediate risk due to the presence
of a downgradient surface water body (UT to Lower Creek) located within 500 feet
of the source area of the release. The UT to Lower Creek is located approximately
125 feet south and hydraulically downgradient of the source area of the release, and
petroleum-related constituents have historically been detected in surface water samples
collected from this drainage feature at concentrations exceeding the North Carolina
Surface Water Quality Standards (NCSWQS). The approximate surface water sampling
locations are identified on Drawing 1.2. Selected historical site assessment data is
included in Appendix A.
A Trust Fund Pre-Approval Task Authorization (TA #25) was obtained from NCDEQ on
November 2,2021 and covered the sampling and laboratory analysis of six groundwater
monitoring wells and three surface water points.This report documents the results of
the groundwater monitoring and surface water sampling activities conducted at the site
on December 20, 2021. The opinions included herein are based on our experience and
information obtained during the study. This report is based on limited observations made
on the dates noted using procedures described herein. If additional information becomes
available, we request the opportunity to review the information, reassess the potential
environmental concerns, and modify our conclusions, if appropriate.
2.0 SITE HISTORY AND SOURCE CHARACTERIZATION
2.1 UST Information
According to the UST Section’s Registration database, the site’s Facility I.D. number is
0-033119. The following table summarizes the UST system information.
Tank No.Const.
Type Install Date Size
(Gallons)Status Last
Contents
Previous
Contents (If
Any)
1 Steel 11/1/1989 12,000 In Use Gasoline None
2 Steel 11/1/1989 12,000 In Use Gasoline None
3 Steel 11/1/1989 12,000 In Use Gasoline None
4 Steel 11/1/1989 12,000 In Use Diesel None
5 Steel 11/1/1989 10,000 In Use Kerosene None
2.2 UST System Owner/Operator
The UST system is owned and operated by Speedway LLC.
2.3 Information on Source of Release
It appears that a release originally occurred from the gasoline tanks based on impacted
soil and the historical presence of free product near the gasoline USTs. The causes and
dates of the original release(s) are unknown. Subsequently, Mid-Atlantic visited the site
on June 8, 2021 to perform semi-annual groundwater and surface water sampling and
discovered approximately four feet of free product in MW-1. Testing of the UST system
was subsequently conducted by Crompco, LLC on June 10, 2021 and the regular
unleaded gasoline line as well as the premium unleaded gasoline spill bucket did not
pass the tests. The line failure occurred across the manifold in the former midgrade
unleaded piping run.Tideland Construction capped the line at the dispenser and former
midgrade unleaded STP.Crompco re-tested the regular unleaded line after repairs
and obtained passing results on June 14, 2021.Although the spill bucket failed the
hydrostatic testing, it is not believed to be a significant contributor to the free product
found in well MW-1.
An MMPE event was scheduled for December 6 - 10, 2021 to extract free product
from MW-1. Significant free product (3.79 ft) was detected in MW-1 immediately prior
to the beginning of the MMPE. In addition MW-8, which has not had measurable free
product since August 2012,was found to contain approximately 3.48 ft immediately prior
to the beginning of the MMPE. The presence of free product is likely related to the
above described petroleum release that occurred from an abandoned, capped product
Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
Lenoir, North Carolina
January 24, 2022
Page 2
line that was still connected to an active dispenser. That line was repaired/disconnected
and subsequent soil sampling was performed, as outlined in Mid-Atlantic's report dated
September 20, 2021.
A selection of downgradient, off site wells (MW-11, MW-15, and MW-16) were gauged
immediately prior to the MMPE on December 6, 2021 to confirm free product was not
migrating off site. Free product was not present in the aforementioned wells. At the
conclusion of the MMPE event, the remaining down/cross gradient wells (MW-2, MW-13,
and MW-14) were gauged and free product was not found.
2.4 Regional Geology and Hydrogeology
According to the map titled Geology of North Carolina (1985), prepared by the North
Carolina Geological Survey Section of the NCDEQ, the subject site is located in the
intrusive rocks of the Inner Piedmont physiographic province. The site appears to be
located on top of metamorphic rocks described as “Migmatitic Granitic Gneiss - foliated
to massive, granitic to quartz dioritic; biotite gneiss and amphibolite common.”
Groundwater in the North Carolina Piedmont region is typically found within the pore
spaces of the saprolite and alluvium deposits and within the fractures of the underlying
bedrock. In general, larger quantities of groundwater are available in valleys and
low‑lying areas where saprolite thickness is usually greater.
2.5 Site Geology and Hydrogeology
Refer to the historical documents in Appendix A for a summary of the geological and
hydrogeological parameters encountered during performance of the site activities as well
as the soil boring logs and well construction logs for the well system.
Measurements taken during historical site activities indicate the following conditions:
•Groundwater flow across the site is generally toward the south-southwest;
•The horizontal seepage velocity for shallow groundwater at the site is estimated
at approximately 98 feet/year;
•The vertical hydraulic gradient is approximately 0.046 foot/foot downward; and
•The hydraulic conductivity was estimated to be 0.18 feet/day.
3.0 POTENTIAL RECEPTORS
Receptor information for the site was previously documented in Mid-Atlantic’s Phase I
Limited Site Assessment Report dated November 13, 2006.A receptor survey update
was not conducted during this monitoring event. Please refer to previous reports for
detailed receptor information. As indicated, the site is currently classified as
Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
Lenoir, North Carolina
January 24, 2022
Page 3
“intermediate” risk due to the presence of free product on the water table and the
existence of a surface water body (UT to Lower Creek)located approximately 125 feet
south and hydraulically downgradient of the release area (Drawing 1.2).
According to Classifications and Water Quality Standards Assigned to the Waters of the
Yadkin-Pee Dee River Basin, Lower Creek is classified as a Class C Water. A Class C
Water is defined as a freshwater body that must be protected for secondary recreation,
fishing, aquatic life including propagation and survival, and wildlife.
4.0 FIELD ACTIVITIES
4.1 Liquid Level Measurements
Mid-Atlantic personnel collected groundwater level measurements from selected site
monitoring wells MW-1, MW-3, MW-8, MW-11, MW-15, and MW-16 on December 20,
2021 using an oil/water interface probe. During well gauging, free product was
encountered in MW-1 (0.14 ft) and MW-8 (0.04 ft). Monitoring well construction details
are provided in Table 4.1. Groundwater level measurements were collected using the
procedures outlined in Appendix B. The results of these activities, along with historical
measurements, are summarized in Table 4.2.
4.2 Monitoring Well Sample Collection
Mid-Atlantic personnel collected groundwater samples from four of six selected site
monitoring wells (MW-3, MW-11, MW-15, and MW-16) on December 20, 2021. Free
product was present in MW-1 and MW-8 and samples were not collected from these
wells. The sampling event was conducted to monitor plume concentrations in the vicinity
of the source area of the release (MW-1, MW-3 and MW-8) and immediately upgradient
of the receiving UT to Lower Creek (MW-11, MW-15 and MW-16). Groundwater samples
were collected using the procedures outlined in Appendix B. Samples were shipped to
Pace Analytical in Mt. Juliet, Tennessee and analyzed by the methods shown on the
chain-of-custody record provided in Appendix C.
4.3 Surface Water Sample Collection
On December 20, 2021,Mid-Atlantic personnel collected three surface water samples
from the UT to Lower Creek, located to the south and downgradient of the source
area of the release. The approximate sample locations (Stream #1, Stream #2, and
Stream #3) are shown on Drawing 1.2.Surface water samples were collected using
the procedures outlined in Appendix B. Samples were shipped to Pace Analytical in Mt.
Juliet, Tennessee and analyzed by the methods shown on the chain-of-custody record in
Appendix C.
Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
Lenoir, North Carolina
January 24, 2022
Page 4
5.0 DISCUSSION OF SAMPLING RESULTS
5.1 Summary of Analytical Results
Groundwater
The laboratory analytical report and chain-of-custody record for groundwater samples
collected on December 20, 2021 are provided in Appendix C and summarized in Table
5.1, which also includes a summary of historical groundwater sampling data for selected
target compounds.Free product was detected in MW-1 and MW-8 during gauging
activities and samples were not collected from these wells. The groundwater sample
collected from monitoring well MW-3 exhibited benzene concentrations above the
NCGQS and the sample from MW-16 was found to contain naphthalene above the
NCGQS (note: the naphthalene concentration was a "J" value, or estimated value).No
other samples collected during the monitoring event exceeded the NCGQS.
Exceedances of the NCSWQS were not measured in groundwater samples collected
from the wells.
Surface Water
The laboratory analytical reports and chain-of-custody records for surface water samples
collected on December 20, 2021 are provided in Appendix C and summarized in Table
5.2, which also includes a summary of historical surface water sampling data for selected
target compounds. As summarized, target compounds were not detected in surface
water samples Stream #1, Stream #2, or Stream #3 at concentrations in excess of their
applicable NCSWQS or EPA NWQC for the December 20, 2021 sampling event.
5.2 Description of Current Plume Size and Location
Until this recent groundwater sampling event, free product had not been detected in
MW-8 since August 2012. During the previous groundwater monitoring event in June
2021, free product was detected in MW-1 for the first time since August
2011.Dissolved-phase groundwater contaminants appear to have been
migrating hydraulically downgradient of the source area of the release, in the direction of
the UT to Lower Creek.The dissolved-phase groundwater contaminant plume appears
to be defined by the current monitoring well network to the extent of ten times the
NCSWQS, as concentrations did not exceed ten times the NCSWQS for samples
collected from monitoring wells MW-11, MW-15 or MW-16, located immediately
upgradient of the UT to Lower Creek.
Benzene and toluene isoconcentration maps for the December 20, 2021 sampling event
are provided as Drawings 5.1 and 5.2, respectively. When compared with the results
of previous sampling events, the groundwater contaminant concentrations appear to be
generally consistent with more recent sampling events, with the exception of free product
Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
Lenoir, North Carolina
January 24, 2022
Page 5
in MW-1 and MW-8. The presence of free product is likely related to the above petroleum
release described in Section 2.3 that occurred from an abandoned, capped product line
that was still connected to an active dispenser. That line was repaired/disconnected
and subsequent soil sampling was performed, as outlined in Mid-Atlantic's report dated
September 20, 2021. Benzene concentrations decreased in MW-16 to below the NCGQS
during this monitoring event. An increase in benzene concentrations in MW-3 to the
southeast of the free product plume may indicate that dissolved phase groundwater
contaminants are beginning to migrate in this direction.
For surface water samples collected from the UT to Lower Creek, target compounds
have not been detected in excess of the NCSWQS since September 2014. Based on the
current available data, additional monitoring events appear to be warranted to continue
to evaluate contaminant trends in the groundwater and the downgradient UT to Lower
Creek.
5.3 Additional Monitoring Information
•Elevation Comparison of the Water Table to the UT to Lower Creek
The elevations of the shallow water table for three monitoring wells (MW-2, MW-11,
and MW-12) in the vicinity of the UT to Lower Creek were previously compared to
the elevations of two surveyed points in the drainage feature. These activities were
documented in Mid-Atlantic’s Groundwater Monitoring and Free Product Recovery
Report dated June 15, 2012 and the results of water elevation comparisons since that
time are summarized in Table 5.3. As indicated, it appears the bottom of the ditch is
lower in elevation than the water table, suggesting that groundwater is discharging into
the drainage feature.
•Proximity of Plume to Nearest Receptor
The nearest surface water body is the UT to Lower Creek, located approximately 125
feet to the south and hydraulically downgradient of the source area of the release. Based
on relative elevations of the water table in this area to the bottom of the UT, groundwater
appears to be discharging to this drainage feature (Table 5.3). Monitoring wells MW-11,
MW-15 and MW-16 are located immediately upgradient of the UT to Lower Creek
and thus provide the best data for use in groundwater to surface water comparisons.
Therefore, based on the results of the historical sampling events, the dissolved-phase
groundwater contaminant plume appears to be migrating off-site and discharging to the
UT to Lower Creek.
•Groundwater Flow Direction
Groundwater flow direction in the surficial aquifer was determined by development of a
water table contour map (Drawing 5.3) based upon water table elevation data obtained
from select site monitoring wells on December 20, 2021. Interpretation of the water
Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
Lenoir, North Carolina
January 24, 2022
Page 6
level data for the current sampling event suggests that the groundwater flow direction is
primarily towards the southwest, with a hydraulic gradient (measured from MW-8 toward
MW-15) of approximately 0.066 ft/ft. The hydraulic gradient was calculated using the
procedure discussed in Appendix B.
6.0 FUTURE SITE REMEDIATION
The site is currently ranked intermediate risk due to the presence of free product on
the water table and the existence of a surface water body within 500 feet of the source
area of the release. The UT to Lower Creek is located approximately 125 feet south
and hydraulically downgradient of the release, and petroleum-related constituents have
historically been detected in the surface water samples collected from this drainage
feature (note that these constituents have not been detected in concentrations exceeding
the NCSWQS since September 2014).
During semi-annual groundwater sampling on June 8, 2021, free product was discovered
in MW-1 for the first time since August 2011. Immediately prior to an MMPE event that
began on December 6, 2021, free product was measured for the first time in MW-8 since
August 2012. The presence of free product is likely related to a June 2021 petroleum
release that occurred from an abandoned, capped product line that was still connected to
an active dispenser. That line was repaired/disconnected and subsequent soil sampling
was performed, as outlined in Mid-Atlantic's report dated September 20, 2021. Wells
located off site and down/cross-gradient of the plume were gauged before and after the
MMPE event with no free product detected. Additionally, MW-11, MW-15, and MW-16
located downgradient of the plume were sampled during this reporting period and the
results for each well were below the NCGQS.
The plume appears to be relatively stable and the contaminants do not appear to
be causing surface water standard exceedances in the downgradient receptor. Future
site remediation should involve continued semi-annual surface water and groundwater
sampling, as well as periodic gauging of MW-1 and MW-8 to monitor for the return of free
product. Significant return of free product in these wells may warrant additional MMPE
events.
7.0 SUMMARY, CONCLUSIONS, AND RECOMMENDATIONS
The December 20, 2021 groundwater/surface water monitoring activities are summarized
as follows:
•Groundwater samples were collected from four of six selected site monitoring
wells on December 20, 2021 to monitor plume concentrations in the vicinity of the
source area of the release;
•Free product was present on the water table in wells MW-1 and
MW-8 on December 20, 2021. These wells were not sampled;and,
Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
Lenoir, North Carolina
January 24, 2022
Page 7
•A total of three surface water samples were collected from the downgradient UT
to Lower Creek, located approximately 125 feet south of the source area of the
release.
Based on the results of the sampling event, Mid-Atlantic concludes the following:
•An increase in benzene concentrations in MW-3 to the southeast of the free
product plume may be an indication that dissolved phase groundwater
contaminants are migrating in this direction;
•Surface water samples collected from the UT to Lower Creek did not exhibit
target compound concentrations in excess of the NCSWQS for the current
monitoring event. Additionally, target compounds for surface water samples
collected from the UT to Lower Creek have not been detected at concentrations
exceeding the NCSWQS since September 2014;
•When compared with the results of previous sampling events, the groundwater
contaminant concentrations appear to be generally consistent with more recent
sampling events, with the exception of the presence of free product in MW-1 and
MW-8. The presence of free product is likely related to a June 2021 petroleum
release that occurred from an abandoned, capped product line that was still
connected to an active dispenser and,
•The dissolved-phase groundwater contaminant plume is currently defined by the
existing monitoring well network to the extent of ten times the NCSWQS.
Based on these conclusions, Mid-Atlantic recommends the following:
•Continued free product gauging of the site monitoring wells, with the next
measurement in February or March of 2022;
•Continued free product recovery using MMPE to address free product on the
water table in the vicinity of monitoring wells MW-1 and MW-8;
•Continued semi-annual groundwater sampling with the inclusion of wells
MW-2,MW-6 and MW-7 to gain additional information regarding the extent of the
contaminant plume;
•Continued surface water sampling to monitor the potential for impact to the
downgradient surface water receptor;and,
•Submittal of this report to the NCDEQ, Asheville Regional Office, UST Section.
8.0 STATEMENTS AND CERTIFICATION
The following statements must be included at the closing of the document text, and must
display the seal and signature of the certifying P.E. or L.G. in addition to the name and
certification number of the company or corporation [See 15A NCAC 2L .0103(e).]
NO.DESCRIPTION YES NO
1 Enter the date the monitoring report was due.Not Established.Will
this report be submitted after the established due date?
Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
Lenoir, North Carolina
January 24, 2022
Page 8
NO.DESCRIPTION YES NO
2 Was any required information from the above template missing from this
report?
If the answer to question #1 or # 2 is “YES”, please provide additional information in this cell
to explain what was missing and why.
Pertinent available information regarding site groundwater conditions is provided throughout
the report and selected historical assessment information is provided in Appendix A.
3 If applicable, will any of the proposed attenuation milestones under the
schedule approved in the Corrective Action Plan not be met? (within a
reasonable margin of error)
Not applicable (N/A).No Corrective Action Plan is in place.
If the answer to question #3 is “NO”, skip to the certification under #6 below.
If the answer to question #3 is “YES”, please generally describe in this cell the possible
reason(s) and outline proposed remedies. (This should be described in more detail in the
report text above.)
Natural attenuation is not currently part of the remedial strategy at this site, although it may
be in the future. Remedial efforts to date have focused on removing free product from the
water table.
4 Does any known or suspected source zone soil contamination or free
product remain outside of the assessed area that could be inhibiting
natural attenuation?
5 Has there been an unexpected increase in contaminant mass sufficient
to suggest a potential new release from a separate onsite or offsite
source?
If the answer to either question #4 or #5 is “YES”, generally describe in this cell any actions
recommended to further assess or clean up this known or suspected source.
Free product was measured for the first time since August 2012 in MW-8. These data are
likely related to a July 2021 petroleum release that occurred from an abandoned, capped
product line that was still connected to an active dispenser. That line was repaired/
disconnected and subsequent soil sampling was performed, as outlined in Mid-Atlantic's
report dated September 20, 2021.
6 Certification:
I,Cameron D. Moore, PG, a Licensed Geologist for Mid-Atlantic Associates, Inc., do
certify that the information contained in this report is correct and accurate to the best of my
knowledge.
Mid-Atlantic Associates, Inc.is licensed to practice geology/engineering in North Carolina.
The certification numbers of the company or corporation are C-186 & F-0967.
Groundwater Monitoring Report
Speedway 7972 (Former WilcoHess 353)
Lenoir, North Carolina
January 24, 2022
Page 9
DRAWINGS
DRAWN
BY:
DATE:
ENG.
CHECK:
JOB NO:DRAFT
CHECK:
GIS NO:
SITE LOCATION
´
1:24,000SCALE:
§¨¦I- 40
Boone
Newton
Lenoir
HickoryMorganton
Cornelius
Wilkes
Burke
Caldwell
Catawba
Avery
Iredell
Watauga
Ashe
Lincoln
McDowell
Carter
Alexander
Rutherford
Johnson
0 2,000 4,0001,000 Feet
REFERENCES:
1. USGS TOPOGRAPHIC QUADRANGLE:
LENOIR, NC - 2016
2. INSET MAP DATA DOWNLOADED FROM DATA.GOV
AREA SHOWN WITHIN
NORTH CAROLINA
TOPOGRAPHIC SITE MAP
SPEEDWAY 7972
(FORMER WILCOHESS 353)
502 WILKESBORO BLVD SE
LENOIR, NORTH CAROLINA APPROVAL:
JANUARY 2022
05G-R1760.23-01
DWG NO: 1.1
CONTOUR INTERVAL = 40 FEET
RSM
000R1760.25 GMH
GMH
TABLES
MW-1 2 9/20/2006 20 5 - 20
MW-2 2 5/31/2011 15 5 - 15
MW-3 2 6/1/2011 18 8 - 18
MW-4 2 5/31/2011 16.5 6.5 - 16.5
MW-5 2 5/31/2011 17 7 - 17
MW-6 2 5/31/2011 18 8 - 18
MW-7 2 6/1/2011 17 7 - 17
MW-8 2 6/1/2011 16 6 - 16
MW-9D 2 6/2/2011 80 40 - 80
MW-10 2 8/30/2011 21 11 - 21
MW-11 2 8/29/2011 16 6 - 16
MW-12 2 8/29/2011 17 7 - 17
MW-13 2 8/30/2011 16 6 - 16
MW-14 2 8/30/2011 16 6 - 16
MW-15 2 8/3/2016 17 7 - 17
MW-16 2 8/3/2016 16 6 - 16
NOTES:
DWM INCIDENT NO.: 28414
TABLE 4.1
MONITORING WELL CONSTRUCTION INFORMATIONSPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC JOB NO. 000R1760.25
WELL NUMBER DIAMETER
(INCHES)
CONSTRUCTION
DATE
CASING DEPTH
(FEET BLS)INTERVAL (FEET
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP
THICKNESS (ft)DTW (ft), BTOC CORRECTED
DTW (ft)SWLE (ft)
MW-1 09/21/06 102.18 ----11.05 --91.13
MW-1 06/02/11 102.18 ----11.01 --91.17
MW-1 08/29/11 102.18 11.54 0.56 12.10 11.69 90.49
MW-1 04/27/12 102.18 ----10.74 --91.44
MW-1 08/16/12 102.18 ----11.34 --90.84
MW-1 02/13/13 102.18 ----10.81 --91.37
MW-1 09/05/13 102.18 ----10.79 --91.39
MW-1 05/01/14 102.18 ----10.46 --91.72
MW-1 09/23/14 102.18 ----11.30 --90.88
MW-1 10/28/15 102.18 ----10.70 --91.48
MW-1 08/03/16 102.18 ----11.38 --90.80
MW-1 12/21/17 102.18 ----11.10 --91.08
MW-1 06/27/18 102.18 NM NM NM NM NM
MW-1 03/25/19 102.18 ----10.49 --91.69
MW-1 11/21/19 102.18 ----11.37 --90.81
MW-1 06/18/20 102.18 ----9.90 --92.28
MW-1 11/18/20 102.18 ----9.31 --92.87
MW-1 06/08/21 102.18 11.85 4.00 15.85 12.93 89.25
MW-1 07/15/21 102.18 10.00 3.38 13.38 10.91 91.27
MW-1 12/20/21 102.18 11.51 0.14 11.65 11.55 90.63
MW-2
MW-2 06/02/11 98.52 ----7.90 --90.62
MW-2 08/29/11 98.52 ----8.45 --90.07
MW-2 04/27/12 98.52 ----7.27 --91.25
MW-2 08/16/12 98.52 ----8.39 --90.13
MW-2 02/13/13 98.52 ----8.09 --90.43
MW-2 09/05/13 98.52 ----8.32 --90.20
MW-2 05/01/14 98.52 ----8.14 --90.38
MW-2 09/23/14 98.52 ----8.51 --90.01
MW-2 10/28/15 98.52 ----8.06 --90.46
MW-2 08/03/16 98.52 NM NM NM NM NM
MW-2 12/21/17 98.52 NM NM NM NM NM
MW-2 06/27/18 98.52 NM NM NM NM NM
MW-2 03/25/19 98.52 NM NM NM NM NM
MW-2 11/21/19 98.52 NM NM NM NM NM
MW-2 06/18/20 98.52 NM NM NM NM NM
MW-2 11/18/20 98.52 NM NM NM NM NM
MW-2 06/08/21 98.52 NM NM NM NM NM
MW-2 07/15/21 98.52 NM NM NM NM NM
MW-2 12/20/21 98.52 NM NM NM NM NM
MW-3
MW-3 06/02/11 102.71 ----12.87 --89.84
MW-3 08/29/11 102.71 ----13.50 --89.21
MW-3 04/27/12 102.71 ----12.23 --90.48
MW-3 08/16/12 102.71 ----12.30 --90.41
MW-3 02/13/13 102.71 ----12.09 --90.62
MW-3 09/05/13 102.71 ----12.91 --89.80
MW-3 05/01/14 102.71 ----12.28 --90.43
MW-3 09/23/14 102.71 ----13.19 --89.52
MW-3 10/28/15 102.71 ----11.26 --91.45
MW-3 08/03/16 102.71 ----12.85 --89.86
MW-3 12/21/17 102.71 ----11.86 --90.85
MW-3 06/27/18 102.71 NM NM NM NM NM
MW-3 03/25/19 102.71 ----12.70 --90.01
MW-3 11/21/19 102.71 ----13.15 --89.56
MW-3 06/18/20 102.71 ----11.38 --91.33
MW-3 11/18/20 102.71 ----12.01 90.70
MW-3 06/08/21 102.71 ----13.19 --89.52
MW-3 07/15/21 102.71 NM NM NM NM NM
MW-3 12/20/21 102.71 ----13.22 --89.49
TABLE 4.2HISTORICAL LIQUID LEVEL MEASUREMENTSSPEEDWAY 7972 (FORMER WILCOHESS 353)LENOIR, NORTH CAROLINA
MID-ATLANTIC JOB NO. 000R1760.25DWM INCIDENT NO.: 28414
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP THICKNESS (ft)DTW (ft), BTOC CORRECTED DTW (ft)SWLE (ft)
MW-4
MW-4 06/02/11 103.37 ----11.76 --91.61
MW-4 08/29/11 103.37 ----12.47 --90.90
MW-4 04/27/12 103.37 ----11.41 --91.96
MW-4 08/16/12 103.37 ----12.28 --91.09
MW-4 02/13/13 103.37 ----11.37 --92.00
MW-4 09/05/13 103.37 ----11.60 --91.77
MW-4 05/01/14 103.37 ----11.22 --92.15
MW-4 09/23/14 103.37 ----12.06 --91.31
MW-4 10/28/15 103.37 ----11.92 --91.45
MW-4 08/03/16 103.37 NM NM NM NM NM
MW-4 12/21/17 103.37 NM NM NM NM NM
MW-4 06/27/18 103.37 NM NM NM NM NM
MW-4 03/25/19 103.37 NM NM NM NM NM
MW-4 11/21/19 103.37 NM NM NM NM NM
MW-4 06/18/20 103.37 NM NM NM NM NM
MW-4 11/18/20 103.37 NM NM NM NM NM
MW-4 06/08/21 103.37 NM NM NM NM NM
MW-4 07/15/21 103.37 NM NM NM NM NM
MW-4 12/20/21 103.37 NM NM NM NM NM
MW-5
MW-5 06/02/11 103.23 ----10.23 --93.00
MW-5 08/29/11 103.23 ----10.80 --92.43
MW-5 04/27/12 103.23 ----10.14 --93.09
MW-5 08/16/12 103.23 ----10.69 --92.54
MW-5 02/13/13 103.23 ----10.12 --93.11
MW-5 09/05/13 103.23 ----10.09 --93.14
MW-5 05/01/14 103.23 ----10.01 --93.22
MW-5 09/23/14 103.23 ----10.43 --92.80
MW-5 10/28/15 103.23 ----10.53 --92.70
MW-5 08/03/16 103.23 NM NM NM NM NM
MW-5 12/21/17 103.23 NM NM NM NM NM
MW-5 06/27/18 103.23 NM NM NM NM NM
MW-5 03/25/19 103.23 NM NM NM NM NM
MW-5 11/21/19 103.23 NM NM NM NM NM
MW-5 06/18/20 103.23 NM NM NM NM NM
MW-5 11/18/20 103.23 NM NM NM NM NM
MW-5 06/08/21 103.23 NM NM NM NM NM
MW-5 07/15/21 103.23 NM NM NM NM NM
MW-5 12/20/21 103.23 NM NM NM NM NM
MW-6
MW-6 06/02/11 103.85 ----10.74 --93.11
MW-6 08/29/11 103.85 ----11.34 --92.51
MW-6 04/27/12 103.85 ----10.69 --93.16
MW-6 08/16/12 103.85 ----11.19 --92.66
MW-6 02/13/13 103.85 ----10.66 --93.19
MW-6 09/05/13 103.85 ----10.59 --93.26
MW-6 05/01/14 103.85 ----10.48 --93.37
MW-6 09/23/14 103.85 ----10.96 --92.89
MW-6 10/28/15 103.85 ----11.04 --92.81
MW-6 08/03/16 103.85 NM NM NM NM NM
MW-6 12/21/17 103.85 NM NM NM NM NM
MW-6 06/27/18 103.85 NM NM NM NM NM
MW-6 03/25/19 103.85 NM NM NM NM NM
MW-6 11/21/19 103.85 NM NM NM NM NM
MW-6 06/18/20 103.85 NM NM NM NM NM
MW-6 11/18/20 103.85 NM NM NM NM NM
MW-6 06/08/21 103.85 NM NM NM NM NM
MW-6 07/15/21 103.85 NM NM NM NM NM
MW-6 12/20/21 103.85 NM NM NM NM NM
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP THICKNESS (ft)DTW (ft), BTOC CORRECTED DTW (ft)SWLE (ft)
MW-7
MW-7 06/02/11 101.70 ----9.24 --92.46
MW-7 08/29/11 101.70 ----9.64 --92.06
MW-7 04/27/12 101.70 ----9.18 --92.52
MW-7 08/16/12 101.70 ----9.46 --92.24
MW-7 02/13/13 101.70 ----9.13 --92.57
MW-7 09/05/13 101.70 ----9.02 --92.68
MW-7 05/01/14 101.70 ----8.98 --92.72
MW-7 09/23/14 101.70 ----9.39 --92.31
MW-7 10/28/15 101.70 ----9.18 --92.52
MW-7 08/03/16 101.70 NM NM NM NM NM
MW-7 12/21/17 101.70 NM NM NM NM NM
MW-7 06/27/18 101.70 NM NM NM NM NM
MW-7 03/25/19 101.70 NM NM NM NM NM
MW-7 11/21/19 101.70 NM NM NM NM NM
MW-7 06/18/20 101.70 NM NM NM NM NM
MW-7 11/18/20 101.70 NM NM NM NM NM
MW-7 06/08/21 101.70 NM NM NM NM NM
MW-7 07/15/21 101.70 NM NM NM NM NM
MW-7 12/20/21 101.70 NM NM NM NM NM
MW-8
MW-8 06/02/11 102.29 ----10.92 --91.37
MW-8 08/29/11 102.29 11.74 0.26 12.00 11.81 90.48
MW-8 04/27/12 102.29 ----11.14 --91.15
MW-8 08/16/12 102.29 11.51 0.04 11.55 11.52 90.74
MW-8 02/13/13 102.29 ----11.10 --91.19
MW-8 09/05/13 102.29 ----11.26 --91.03
MW-8 05/01/14 102.29 ----10.09 --92.20
MW-8 09/23/14 102.29 ----11.59 --90.70
MW-8 10/28/15 102.29 ----10.89 --91.40
MW-8 08/03/16 102.29 ----11.61 --90.68
MW-8 12/21/17 102.29 ----11.29 --91.00
MW-8 06/27/18 102.29 NM NM NM NM NM
MW-8 11/21/19 102.29 ----11.66 --90.63
MW-8 06/18/20 102.29 ----10.73 --91.56
MW-8 11/18/20 102.29 ----10.74 --91.55
MW-8 06/08/21 102.29 ----11.64 --90.65
MW-8 07/15/21 102.29 NM NM NM NM NM
MW-8 12/20/21 102.29 11.92 0.04 11.96 11.93 90.36
MW-9D
MW-9D 06/02/11 102.64 ----78.29 --24.35
MW-9D 08/29/11 102.64 ----14.40 --88.24
MW-9D 04/27/12 102.64 ----10.75 --91.89
MW-9D 08/16/12 102.64 ----11.03 --91.61
MW-9D 02/14/13 102.64 ----10.32 --92.32
MW-9D 09/05/13 102.64 ----9.96 --92.68
MW-9D 05/01/14 102.64 ----10.26 --92.38
MW-9D 09/23/14 102.64 ----11.16 --91.48
MW-9D 10/28/15 102.64 ----10.80 --91.84
MW-9D 08/03/16 102.64 NM NM NM NM NM
MW-9D 12/21/17 102.64 NM NM NM NM NM
MW-9D 06/27/18 102.64 NM NM NM NM NM
MW-9D 03/25/19 102.64 NM NM NM NM NM
MW-9D 11/21/19 102.64 NM NM NM NM NM
MW-9D 06/18/20 102.64 NM NM NM NM NM
MW-9D 11/18/20 102.64 NM NM NM NM NM
MW-9D 06/08/21 102.64 NM NM NM NM NM
MW-9D 07/15/21 102.64 NM NM NM NM NM
Well did not exist
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP
THICKNESS (ft)DTW (ft), BTOC CORRECTED
DTW (ft)SWLE (ft)
MW-10
MW-10 08/29/11 98.02 ----15.53 --82.49
MW-10 04/27/12 98.02 ----13.25 --84.77
MW-10 08/16/12 98.02 ----13.77 --84.25
MW-10 02/13/13 98.02 ----13.38 --84.64
MW-10 09/05/13 98.02 ----13.90 --84.12
MW-10 05/01/14 98.02 ----13.11 --84.91
MW-10 09/23/14 98.02 ----14.46 --83.56
MW-10 10/28/15 98.02 ----11.83 --86.19
MW-10 08/03/16 98.02 NM NM NM NM NM
MW-10 12/21/17 98.02 NM NM NM NM NM
MW-10 06/27/18 98.02 NM NM NM NM NM
MW-10 11/21/19 98.02 NM NM NM NM NM
MW-10 06/18/20 98.02 NM NM NM NM NM
MW-10 11/18/20 98.02 NM NM NM NM NM
MW-10 06/08/21 98.02 NM NM NM NM NM
MW-10 07/15/21 98.02 NM NM NM NM NM
MW-10 12/20/21 98.02 NM NM NM NM NM
MW-11
MW-11 08/29/11 93.21 ----9.84 --83.37
MW-11 04/27/12 93.21 ----9.29 --83.92
MW-11 08/16/12 93.21 ----9.52 --83.69
MW-11 02/13/13 93.21 ----9.39 --83.82
MW-11 09/05/13 93.21 ----9.62 --83.59
MW-11 05/01/14 93.21 ----9.42 --83.79
MW-11 09/23/14 93.21 ----9.72 --83.49
MW-11 10/28/15 93.21 ----8.95 --84.26
MW-11 08/03/16 93.21 ----9.62 --83.59
MW-11 12/21/17 93.21 ----9.20 --84.01
MW-11 06/27/18 93.21 ----9.20 --84.01
MW-11 03/25/19 93.21 ----9.43 --83.78
MW-11 11/21/19 93.21 ----9.66 --83.55
MW-11 06/18/20 93.21 ----9.17 --84.04
MW-11 11/18/20 93.21 ----9.24 --83.97
MW-11 06/08/21 93.21 ----9.74 --83.47
MW-11 07/15/21 93.21 NM NM NM NM NM
MW-11 12/20/21 93.21 ----9.79 --83.42
MW-12
MW-12 08/29/11 94.31 ----10.17 --84.14
MW-12 04/27/12 94.31 ----9.74 --84.57
MW-12 08/16/12 94.31 ----10.12 --84.19
MW-12 02/13/13 94.31 ----9.88 --84.43
MW-12 09/05/13 94.31 ----10.14 --84.17
MW-12 05/01/14 94.31 ----9.94 --84.37
MW-12 09/23/14 94.31 ----10.28 --84.03
MW-12 10/28/15 94.31 ----9.69 --84.62
MW-12 08/03/16 94.31 NM NM NM NM NM
MW-12 12/21/17 94.31 NM NM NM NM NM
MW-12 06/27/18 94.31 NM NM NM NM NM
MW-12 03/25/19 94.31 NM NM NM NM NM
MW-12 11/21/19 94.31 NM NM NM NM NM
MW-12 06/18/20 94.31 NM NM NM NM NM
MW-12 11/18/20 94.31 NM NM NM NM NM
MW-12 06/08/21 94.31 NM NM NM NM NM
MW-12 07/15/21 94.31 NM NM NM NM NM
MW-12 12/20/21 94.31 NM NM NM NM NM
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP THICKNESS (ft)DTW (ft), BTOC CORRECTED DTW (ft)SWLE (ft)
MW-13
MW-13 08/29/11 95.18 ----9.88 --85.30
MW-13 04/27/12 95.18 ----10.02 --85.16
MW-13 08/16/12 95.18 ----10.08 --85.10
MW-13 02/14/13 95.18 ----10.04 --85.14
MW-13 09/05/13 95.18 ----10.68 --84.50
MW-13 05/01/14 95.18 ----10.58 --84.60
MW-13 09/23/14 95.18 ----10.69 --84.49
MW-13 10/28/15 95.18 ----10.69 --84.49
MW-13 08/03/16 95.18 NM NM NM NM NM
MW-13 12/21/17 95.18 NM NM NM NM NM
MW-13 06/27/18 95.18 NM NM NM NM NM
MW-13 03/25/19 95.18 NM NM NM NM NM
MW-13 11/21/19 95.18 NM NM NM NM NM
MW-13 06/18/20 95.18 NM NM NM NM NM
MW-13 11/18/20 95.18 NM NM NM NM NM
MW-13 06/08/21 95.18 NM NM NM NM NM
MW-13 07/15/21 95.18 NM NM NM NM NM
MW-13 12/20/21 95.18 NM NM NM NM NM
MW-14
MW-14 08/29/11 95.92 ----8.90 --87.02
MW-14 04/27/12 95.92 ----8.46 --87.46
MW-14 08/16/12 95.92 ----8.83 --87.09
MW-14 02/14/13 95.92 ----8.29 --87.63
MW-14 09/05/13 95.92 ----8.38 --87.54
MW-14 05/01/14 95.92 ----8.18 --87.74
MW-14 09/23/14 95.92 ----8.41 --87.51
MW-14 10/28/15 95.92 ----8.33 --87.59
MW-14 08/03/16 95.92 NM NM NM NM NM
MW-14 12/21/17 95.92 NM NM NM NM NM
MW-14 06/27/18 95.92 NM NM NM NM NM
MW-14 03/25/19 95.92 NM NM NM NM NM
MW-14 11/21/19 95.92 NM NM NM NM NM
MW-14 06/18/20 95.92 NM NM NM NM NM
MW-14 11/18/20 95.92 NM NM NM NM NM
MW-14 06/08/21 95.92 NM NM NM NM NM
MW-14 07/15/21 95.92 NM NM NM NM NM
MW-14 12/20/21 95.92 NM NM NM NM NM
MW-15
MW-15 08/03/16 92.12 ----8.35 --83.77
MW-15 12/21/17 92.12 ----8.04 --84.08
MW-15 06/27/18 92.12 ----8.02 --84.10
MW-15 03/25/19 92.12 ----8.15 --83.97
MW-15 11/21/19 92.12 ----8.39 --83.73
MW-15 06/18/20 92.12 ----7.97 --84.15
MW-15 11/18/20 92.12 ----8.02 --84.10
MW-15 06/08/21 92.12 ----8.46 --83.66
MW-15 07/15/21 92.12 NM NM NM NM NM
MW-15 12/20/21 92.12 ----8.50 --83.62
MW-16
MW-16 08/03/16 92.02 ----7.64 --84.38
MW-16 12/21/17 92.02 ----8.01 --84.01
MW-16 06/27/18 92.02 ----7.99 --84.03
MW-16 03/25/19 92.02 ----8.17 --83.85
MW-16 11/21/19 92.02 ----8.38 --83.64
MW-16 06/18/20 92.02 ----7.97 --84.05
MW-16 11/18/20 92.02 ----8.02 --84.00
MW-16 06/08/21 92.02 ----8.42 --83.60
MW-16 07/15/21 92.02 NM NM NM NM NM
MW-16 12/20/21 92.02 ----8.49 --83.53
Well did not exist
5,000 84,500 260,000 85,500 70,000 20,0005109701104,500 NE 15,000 120 14,000 NE NE 25016006005007020640070020015
MW-1 09/21/06 10,100 910 12,800 4,860 NA 2,070 NA 35,000 8,700 2,000 NA
MW-1 06/02/11 1,540 2,480 9,710 11,610 ND 676 26,000 33,300 11,800 0.8 J
MW-1 08/29/11 FP FP FP FP FP FP FP FP FP FP FP
MW-1 04/27/12 794 1,900 7,300 10,700 ND
MW-1 08/16/12 536 1,510 2,580 5,550 133 NDa NA NA NA NA NA
MW-1 02/13/13 400 2,400 2,700 9,600 ND 74 J 650 NA NA NA NAMW-1 09/05/13 110 1,100 750 4,100 ND ND 480 J NA NA NA NAMW-1 05/02/14 110 1,100 590 3,700 ND ND NA NA NA NA NA
MW-1 09/23/14 46 880 310 2,750 ND ND 270 NA NA NA NA
MW-1 10/28/15 22.2 670 107 2,043 ND ND 329 NA NA NA NA
MW-1 08/03/16 51.4 633 107 1,877 7.07 J ND 252 NA NA NA NA
MW-1 12/21/17 54.8 592 47.5 J 1,670 ND ND 204 J NA NA NA NA
MW-1 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-1 03/25/19 182 V3 503 ND ND 40.7 V3 23.9 V3 114 NA NA NA NA
MW-1 11/21/19 370 570 1.39 42.20 34.4 7.48 17.7 NA NA NA NA
MW-1 06/18/20 200 371 23.8 J 274 17.8 J ND 26.6 J NA NA NA NA
MW-1 11/18/20 375 381 664 1,203 74.7 9.52 J 143 NA NA NA NA
MW-1 06/08/21 FP FP FP FP FP FP FP FP FP FP FP
MW-1 07/15/21 FP FP FP FP FP FP FP FP FP FP FPMW-1 12/20/21 FP FP FP FP FP FP FP FP FP FP FP
MW-2 06/02/11 3,200 1,150 6,080 3,960 ND 240 17,200 12,400 NDa 0.7 J
MW-2 08/29/11 1,450 822 820 1,006 74 J 125 J NA NA NA NA NA
MW-2 04/27/12 1,400 1,730 1,340 3,322 ND
MW-2 08/16/12 131 141 ND ND ND 22.8 NA NA NA NA NA
MW-2 02/13/13 78 37 3.0 2.2 J 0.46 J 14 12 NA NA NA NA
MW-2 09/05/13 3.9 1.0 ND ND ND 4.5J ND NA NA NA NA
MW-2 05/02/14 2.0 4.9 ND ND ND 12 NA NA NA NA NA
MW-2 09/23/14 0.16 J 0.37 J ND ND ND 6.4 ND NA NA NA NA
MW-2 10/28/15 ND 1.15 ND 4.48 J ND 3.62 ND NA NA NA NA
MW-2 08/03/16 NS NS NS NS NS NS NS NS NS NS NSMW-2 12/21/17 NS NS NS NS NS NS NS NS NS NS NSMW-2 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-2 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-2 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-2 06/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-2 11/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-2 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-2 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-2 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
MW-3 06/02/11 50.9 25.9 103 122.5 ND ND 8.34 154 ND 191 1.3 J
MW-3 08/29/11 155 68.6 129 376.2 23.4 ND NA NA NA NA NAMW-3 04/27/12 ND ND ND ND ND ND NA NA NA NA NAMW-3 08/16/12 2.56 ND 0.840 J 3.92 J ND ND NA NA NA NA NA
MW-3 02/13/13 ND ND ND ND ND ND ND NA NA NA NA
MW-3 09/05/13 1.1 1.2 1.8 2.5 J ND ND ND NA NA NA NA
MW-3 05/01/14 ND ND ND ND ND ND NA NA NA NA NA
MW-3 09/23/14 4.4 5.4 2.6 9.8 ND ND 1.4 NA NA NA NA
MW-3 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-3 08/03/16 9.12 8.50 4.37 J 21.5 ND ND 7.42 NA NA NA NA
MW-3 12/21/17 ND ND ND ND ND ND ND NA NA NA NA
MW-3 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-3 03/25/19 ND ND ND ND ND ND 1.76 J NA NA NA NA
MW-3 11/21/19 ND ND ND ND ND ND ND NA NA NA NA
MW-3 06/18/20 ND ND ND ND ND ND ND NA NA NA NAMW-3 11/18/20 ND ND ND ND ND ND ND NA NA NA NAMW-3 06/08/21 4.29 1.70 1.55 5.14 5.28 0.844 J 3.13 NA NA NA NA
MW-3 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-3 12/20/21 37.2 3.20 1.11 1.11 55.4 8.02 2.45 J NA NA NA NA
MW-4 06/02/11 ND ND ND ND 0.41 6.95 ND ND ND ND 0.8J
MW-4 08/29/11 ND ND ND ND ND 3.11 NA NA NA NA NA
MW-4 04/27/12 ND ND ND ND ND 1.56 J NA NA NA NA NA
MW-4 08/16/12 ND ND ND ND ND 2.54 NA NA NA NA NA
MW-4 02/13/13 ND ND ND ND ND 1.1 J ND NA NA NA NA
MW-4 09/05/13 ND ND ND ND ND 3.6 J ND NA NA NA NA
MW-4 05/01/14 ND ND ND ND ND 1.5*NA NA NA NA NA
MW-4 09/23/14 ND ND ND ND 0.26 J 1.8 NA NA NA NA NAMW-4 10/28/15 ND ND ND ND ND 0.927 J ND NA NA NA NAMW-4 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-4 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-4 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-4 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-4 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-4 6/18/2020 NS NS NS NS NS NS NS NS NS NS NS
MW-4 11/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-4 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-4 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-4 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
C9-C12 Aliphatics (ug/l)
Benzene (ug/l)Ethylbenzene (ug/l)
C9-C10 Aromatics (ug/l)
Lead (ug/l)Diisopropyl ether (DIPE) (ug/l)MTBE (ug/l)Naphthalene (ug/l)
C5-C8 Aliphatics (ug/l)
Toluene (ug/l)
Total Xylenes (ug/l) Well Number Sample Date
Page 1 of 4
5,000 84,500 260,000 85,500 70,000 20,0005109701104,500 NE 15,000 120 14,000 NE NE 25016006005007020640070020015
C9-C12 Aliphatics (ug/l)
Benzene (ug/l)Ethylbenzene (ug/l)
C9-C10 Aromatics (ug/l)
Lead (ug/l)Diisopropyl ether (DIPE) (ug/l)MTBE (ug/l)Naphthalene (ug/l)
C5-C8 Aliphatics (ug/l)
Toluene (ug/l)
Total Xylenes (ug/l) Well Number Sample Date
MW-5 06/02/11 ND ND ND ND ND 1.62 ND ND ND ND 0.7 J
MW-5 08/29/11 ND ND ND ND ND 1.48 J NA NA NA NA NA
MW-5 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-5 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-5 02/13/13 ND ND ND ND ND 0.77 J ND NA NA NA NAMW-5 09/05/13 ND ND ND ND ND 0.76 J ND NA NA NA NAMW-5 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-5 09/23/14 ND ND ND ND ND 1.0 NA NA NA NA NA
MW-5 10/28/15 ND ND ND ND ND 0.659 J ND NA NA NA NA
MW-5 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-5 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-5 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-5 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-5 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-5 06/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-5 11/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-5 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-5 07/15/21 NS NS NS NS NS NS NS NS NS NS NSMW-5 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
MW-6 06/02/11 ND ND ND ND ND 3.76 ND ND ND ND 1.2 J
MW-6 08/29/11 ND ND ND ND ND 2.58 NA NA NA NA NA
MW-6 04/27/12 ND ND ND ND ND 2.00 NA NA NA NA NA
MW-6 08/16/12 ND ND ND ND ND 2.68 NA NA NA NA NA
MW-6 02/13/13 ND ND ND ND ND 3.2 J ND NA NA NA NA
MW-6 09/05/13 ND ND ND ND ND 3.3 J ND NA NA NA NA
MW-6 05/01/14 ND ND ND ND 0.49 J 6.1*NA NA NA NA NA
MW-6 09/23/14 ND ND ND ND 0.52 4.2 NA NA NA NA NA
MW-6 10/28/15 ND ND ND ND 0.640 J 3.41 ND NA NA NA NA
MW-6 08/03/16 NS NS NS NS NS NS NS NS NS NS NSMW-6 12/21/17 NS NS NS NS NS NS NS NS NS NS NSMW-6 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-6 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-6 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-6 06/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-6 11/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-6 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-6 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-6 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
MW-7 06/02/11 ND ND ND ND ND 0.9 ND ND ND ND 24.1
MW-7 08/29/11 ND ND ND ND ND ND NA NA NA NA NAMW-7 04/27/12 ND ND ND ND ND ND NA NA NA NA NAMW-7 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-7 02/13/13 ND ND ND ND ND 0.81 J ND NA NA NA NA
MW-7 09/05/13 ND ND ND ND ND 0.55 J ND NA NA NA NA
MW-7 05/01/14 ND ND ND ND ND ND NA NA NA NA NA
MW-7 09/23/14 ND ND ND ND ND 0.80 NA NA NA NA NA
MW-7 10/28/15 ND ND ND ND ND 0.980 J ND NA NA NA NA
MW-7 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-7 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-7 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-7 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-7 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-7 06/18/20 NS NS NS NS NS NS NS NS NS NS NSMW-7 11/18/20 NS NS NS NS NS NS NS NS NS NS NSMW-7 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-7 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-7 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
MW-8 06/02/11 2,300 1,600 12,500 11,220 NDa NDa 600 22,600 27,900 NDa 1.1 J
MW-8 08/29/11 FP FP FP FP FP FP FP FP FP FP FP
MW-8 04/27/12 805 1,340 5,280 10,240 ND
MW-8 08/16/12 FP FP FP FP FP FP FP FP FP FP FP
MW-8 02/13/13 700 1,800 3,500 12,000 ND ND 880 NA NA NA NA
MW-8 09/05/13 730 1,300 6,900 11,000 ND ND 900 NA NA NA NA
MW-8 05/02/14 480 1,100 3,800 8,800 ND ND NA NA NA NA NA
MW-8 09/23/14 300 1,400 3,800 7,600 ND ND 710 NA NA NA NAMW-8 10/28/15 140 1,740 3,580 8,970 ND ND 875 NA NA NA NAMW-8 08/03/16 655 942 2,300 4,920 39.1 J ND 670 NA NA NA NA
MW-8 12/21/17 180 1,100 2,000 5,480 ND ND 556 NA NA NA NA
MW-8 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-8 03/25/19 418 668 1,090 2,487 46.9 7.75 386 NA NA NA NA
MW-8 11/21/19 392 585 668 2,401 107 ND 193 J NA NA NA NA
MW-8 06/18/20 696 445 451 1,762 127 19.9 J 197 J NA NA NA NA
MW-8 11/18/20 535 376 281 1,462 249 35.3 J 236 J NA NA NA NA
MW-8 06/08/21 1250 585 440 2,287 791 101 255 NA NA NA NA
MW-8 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-8 12/20/21 FP FP FP FP FP FP FP FP FP FP FP
Page 2 of 4
5,000 84,500 260,000 85,500 70,000 20,0005109701104,500 NE 15,000 120 14,000 NE NE 25016006005007020640070020015
C9-C12 Aliphatics (ug/l)
Benzene (ug/l)Ethylbenzene (ug/l)
C9-C10 Aromatics (ug/l)
Lead (ug/l)Diisopropyl ether (DIPE) (ug/l)MTBE (ug/l)Naphthalene (ug/l)
C5-C8 Aliphatics (ug/l)
Toluene (ug/l)
Total Xylenes (ug/l) Well Number Sample Date
MW-9d 06/02/11 ND ND 0.64 ND ND ND ND ND ND ND 7.6
MW-9d 08/29/11 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 02/14/13 ND ND ND ND ND ND ND NA NA NA NAMW-9d 09/05/13 ND ND ND ND ND ND ND NA NA NA NAMW-9d 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-9d 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 06/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 11/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 07/15/21 NS NS NS NS NS NS NS NS NS NS NSMW-9d 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
MW-10
MW-10 08/30/11 ND ND ND ND ND ND ND ND ND ND 17.2
MW-10 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-10 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-10 02/13/13 ND ND ND ND ND ND ND NA NA NA NA
MW-10 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-10 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-10 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-10 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-10 08/03/16 NS NS NS NS NS NS NS NS NS NS NSMW-10 12/21/17 NS NS NS NS NS NS NS NS NS NS NSMW-10 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-10 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-10 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-10 06/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-10 11/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-10 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-10 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-10 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
MW-11
MW-11 08/30/11 303 ND ND ND ND 335 ND 853 ND ND 4.0 JMW-11 04/27/12 ND ND ND ND 6.27 17.2 NA NA NA NA NAMW-11 08/16/12 71.7 ND ND ND 7.70 75.6 NA NA NA NA NA
MW-11 02/13/13 ND ND ND ND 10 8.9 ND NA NA NA NA
MW-11 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-11 05/02/14 ND ND ND ND 1.3 ND NA NA NA NA NA
MW-11 09/23/14 ND ND ND ND 0.61 0.97 NA NA NA NA NA
MW-11 10/28/15 20.3 ND ND ND 0.719 J 4.27 ND NA NA NA NA
MW-11 08/03/16 ND ND ND ND 0.398 J 0.486 J ND NA NA NA NA
MW-11 12/21/17 ND ND ND ND 3.34 0.824 J ND NA NA NA NA
MW-11 06/27/18 ND ND ND ND 0.511 J ND ND NA NA NA NA
MW-11 03/25/19 ND ND ND ND ND ND ND NA NA NA NA
MW-11 11/21/19 ND ND ND ND 14.2 1.19 ND NA NA NA NA
MW-11 06/18/20 ND ND ND ND ND ND ND NA NA NA NAMW-11 11/18/20 ND ND ND ND ND ND ND NA NA NA NAMW-11 06/08/21 ND ND ND ND 6.52 0.570 J ND NA NA NA NA
MW-11 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-11 12/20/21 ND ND ND ND 36.1 3.69 ND NA NA NA NA
MW-12
MW-12 08/30/11 ND ND ND ND ND ND ND ND ND ND 0.9J
MW-12 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-12 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-12 02/13/13 ND ND ND ND ND ND ND NA NA NA NA
MW-12 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-12 05/02/14 ND ND ND ND ND ND NA NA NA NA NAMW-12 09/23/14 ND ND ND ND ND ND NA NA NA NA NAMW-12 10/28/15 ND ND ND ND ND ND ND NA NA NA NAMW-12 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-12 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-12 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-12 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-12 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-12 06/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-12 11/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-12 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-12 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-12 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
Page 3 of 4
5,000 84,500 260,000 85,500 70,000 20,000
510 970 110 4,500 NE 15,000 120 14,000 NE NE 25016006005007020640070020015
C9-C12 Aliphatics (ug/l)
Benzene (ug/l)Ethylbenzene (ug/l)
C9-C10 Aromatics (ug/l)
Lead (ug/l)Diisopropyl ether (DIPE) (ug/l)MTBE (ug/l)Naphthalene (ug/l)
C5-C8 Aliphatics (ug/l)
Toluene (ug/l)
Total Xylenes (ug/l) Well Number Sample Date
MW-13
MW-13 08/30/11 ND ND ND ND ND ND ND ND ND ND 8.5
MW-13 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-13 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-13 02/14/13 ND ND ND ND ND ND ND NA NA NA NA
MW-13 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-13 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-13 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-13 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-13 08/03/16 NS NS NS NS NS NS NS NS NS NS NSMW-13 12/21/17 NS NS NS NS NS NS NS NS NS NS NSMW-13 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-13 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-13 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-13 06/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-13 11/18/20 NS NS NS NS NS NS NS NS NS NS NS
MW-13 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-13 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-13 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
MW-14
MW-14 08/30/11 ND ND ND ND ND ND ND ND ND ND 9.1MW-14 04/27/12 ND ND ND ND ND ND NA NA NA NA NAMW-14 08/16/12 ND ND ND ND ND ND NA NA NA NA NAMW-14 02/14/13 ND ND ND ND ND ND ND NA NA NA NA
MW-14 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-14 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-14 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-14 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-14 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-14 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-14 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-14 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-14 11/21/19 NS NS NS NS NS NS NS NS NS NS NS
MW-14 06/18/20 NS NS NS NS NS NS NS NS NS NS NSMW-14 11/18/20 NS NS NS NS NS NS NS NS NS NS NSMW-14 06/08/21 NS NS NS NS NS NS NS NS NS NS NS
MW-14 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-14 12/20/21 NS NS NS NS NS NS NS NS NS NS NS
MW-15MW-15 08/04/16 2.05 14.7 5.09 37.4 2.75 113 4.96 J 636 492 241 8.72 B
MW-15 12/21/17 0.985 J 7.20 0.809 J 5.691 J 2.05 45.2 1.64 J NA NA NA NA
MW-15 06/27/18 3.64 3.70 ND 4.88 2.10 40.9 1.30 J NA NA NA NA
MW-15 03/25/19 128 20.0 6.67 12.29 1.55 23.8 3.48 J NA NA NA NA
MW-15 11/21/19 ND 0.757 J ND ND 7.47 32.4 ND NA NA NA NA
MW-15 06/18/20 62.8 10.6 1.12 7.32 4.00 16.1 1.23 J NA NA NA NA
MW-15 11/18/20 1.86 3.95 ND 1.07 J 2.42 12.7 1.25 J NA NA NA NA
MW-15 06/08/21 72.1 5.57 1.13 1.60 5.56 17.8 1.00 NA NA NA NA
MW-15 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-15 12/20/21 0.145 J 2.07 0.39 J 2.36 7.74 17.0 1.21 J NA NA NA NA
MW-16MW-16 08/04/16 218 368 80.4 1,772 1.45 24.6 181 1,380 4,980 1,720 3.50 B J
MW-16 12/21/17 73.6 198 22.2 983 1.55 19.7 77.2 NA NA NA NA
MW-16 06/27/18 13.4 J 268 ND 1,432 ND ND 154.0 NA NA NA NA
MW-16 03/25/19 2.05 98.2 0.643 J 438 ND ND 79.1 NA NA NA NA
MW-16 11/21/19 234 36.5 0.766 J 164.5 3.27 14.3 47.4 NA NA NA NA
MW-16 06/18/20 1.90 J 13.7 ND 54.8 1.70 J ND 30.7 J NA NA NA NA
MW-16 11/18/20 ND 6.98 J ND 25.9 J 2.39 J ND 23.9 J NA NA NA NA
MW-16 06/08/21 28.9 7.45 J ND 29.8 J 1.26 J ND 10.3 J NA NA NA NA
MW-16 07/15/21 NS NS NS NS NS NS NS NS NS NS NS
MW-16 12/20/21 ND 14.0 ND 44.3 9.91 J 11.7 19.5 J NA NA NA NA
Bold values exceed NCGQS B - Same analyte is found in associated blankNote: the following NCGQS changes effective 1/13/10: Ethylbenzene 550 ug/L to 600 ug/L, Toluene 1000 ug/L to 600 ug/L, Total Xylenes 550 ug/L to 500 ug/L,
Note: the following NCSWQS and/or EPA NWQC changes effective 5/5/13: Ethylbenzene NE to 97 ug/L, Total Xylenes NE to 450 ug/L, MTBE NE to 1,500 ug/L, Napththalene NE to 12 ug/L,
Page 4 of 4
51 97 11 450 NE 1,500 12 1,400 NE NE 25
Stream #1Stream #1 04/13/12 13.5 4.99 15.6 15.86 ND ND 1.38 ND ND ND NAStream #1 08/16/12 10.5 2.06 2.44 7.46 ND 1.24 0.870 NA NA NA NAStream #1 02/14/13 15 5.2 16 6.5 ND 1.4 1.500 NA NA NA NAStream #1 09/05/13 0.71 2.3 1.1 7.2 ND ND 0.79J NA NA NA NAStream #1 05/02/14 6.6 5.0 10 16 ND ND ND NA NA NA NAStream #1 09/23/14 0.21 J 0.57 0.50 1.8 J ND ND ND NA NA NA NAStream #1 12/01/15 4.38 5.86 7.86 16.6 ND 1.11 1.45 J NA NA NA NAStream #1 08/03/16 ND ND ND ND ND ND ND NA NA NA NAStream #1 12/21/17 0.350 J 2.31 2.02 5.53 ND ND 1.60 J NA NA NA NAStream #1 06/27/18 0.464 J 2.38 1.61 7.64 ND ND 1.17 J NA NA NA NAStream #1 03/25/19 0.662 J 3.00 2.25 9.12 ND ND 2.67 J NA NA NA NAStream #1 11/21/19 ND ND ND ND ND ND ND NA NA NA NAStream #1 06/18/20 0.347 J 0.639 J 0.450 J 1.14 J 0.177 J ND ND NA NA NA NAStream #1 11/18/20 0.693 J 2.73 1.29 5.63 J 0.524 J 0.234 J 1.20 J NA NA NA NAStream #1 06/08/21 0.339 J 0.720 J ND 0.732 J 0.440 J 0.104 J ND NA NA NA NAStream #1 07/15/21 1.62 1.21 0.377 J 1.46 J 0.703 J 0.219 J ND NA NA NA NAStream #1 12/20/21 ND 0.569 J ND ND 0.272 J 0.143 J ND NA NA NA NA
Stream #2Stream #2 04/13/12 7.23 3.05 7.83 10.9 ND ND 0.970 ND ND ND NAStream #2 08/16/12 5.67 1.15 1.28 4.13 0.190J 1.55 0.530 NA NA NA NAStream #2 02/14/13 7.6 3.4 9.8 5.2 ND 1.2 0.99J NA NA NA NAStream #2 09/05/13 ND 1.1 0.53 3.4 ND ND ND NA NA NA NAStream #2 05/02/14 2.2 1.9 3.5 6.6 ND ND ND NA NA NA NAStream #2 09/23/14 1.4 1.6 13 11.3 ND ND 0.59 NA NA NA NAStream #2 12/01/15 1.66 1.76 2.74 J 5.96 ND 0.721 J ND NA NA NA NAStream #2 08/03/16 ND ND ND ND ND ND ND NA NA NA NAStream #2 12/21/17 ND 0.852 J 0.931 J 1.959 J ND ND ND NA NA NA NAStream #2 06/27/18 ND 1.32 0.906 J 3.923 J ND ND ND NA NA NA NAStream #2 03/25/19 ND 0.850 J 0.839 J 2.743 J ND ND ND NA NA NA NAStream #2 11/21/19 ND ND ND ND ND ND ND NA NA NA NAStream #2 06/18/20 0.161 J 0.276 J ND 0.523 J ND ND ND NA NA NA NAStream #2 11/18/20 0.455 J 1.56 1.11 3.38 J 0.468 J 0.209 ND NA NA NA NAStream #2 06/08/21 0.137 J 0.248 J ND ND 0.385 J ND ND NA NA NA NAStream #2 07/15/21 0.916 J 0.642 J ND 0.532 J 0.589 J 0.163 J ND NA NA NA NAStream #2 12/20/21 ND 0.268 J ND ND 0.626 J 0.167 J ND NA NA NA NA
Stream #3Stream #3 04/13/12 NS NS NS NS NS NS NS NS NS NS NSStream #3 08/16/12 ND ND ND ND ND ND ND NA NA NA NAStream #3 02/14/13 ND ND ND ND ND ND ND NA NA NA NAStream #3 09/05/13 ND ND ND ND ND ND ND NA NA NA NAStream #3 05/02/14 ND 0.15 J ND ND ND ND ND NA NA NA NAStream #3 09/23/14 ND ND 0.10 J ND ND ND ND NA NA NA NAStream #3 12/01/15 ND ND ND ND ND ND ND NA NA NA NAStream #3 08/03/16 ND ND ND ND ND ND ND NA NA NA NAStream #3 12/21/17 ND ND ND ND ND ND ND NA NA NA NAStream #3 06/27/18 ND ND ND ND ND ND ND NA NA NA NAStream #3 03/25/19 ND ND ND ND ND ND ND NA NA NA NAStream #3 11/21/19 ND ND ND ND ND ND ND NA NA NA NAStream #3 06/18/20 ND ND ND ND ND ND ND NA NA NA NAStream #3 11/18/20 ND ND ND ND ND ND ND NA NA NA NAStream #3 06/08/21 ND ND ND ND ND ND ND NA NA NA NAStream #3 07/15/21 ND ND ND ND ND ND ND NA NA NA NAStream #3 12/20/21 ND ND ND ND ND ND ND NA NA NA NA
Notes:NA - Not analyzed for this parameter DIPE - diisopropyl etherNE - Standard not established * C9-C12 Aliphatics (VPH) only. See laboratory report.NS - Not sampled ** C9-C10 Aromatics (VPH) only. See laboratory report.All concentrations reported in ug/L - micrograms per liter J- Estimated ValueBold values exceed NC Surface Water Quality Standards (NCSWQS) and EPA National Water Quality Criteria (NWQC)Note: This table summarizes results for selected compounds. Additional compounds may have been detected. Refer to laboratory reports for additional information
Diisopropyl ether (DIPE)MTBETotal Xylenes C9-C12 AliphaticsSample Location Sample Date Benzene Naphthalene
Not sampled on prior dates
Not sampled on prior dates
Ethylbenzene Toluene C5-C8 Aliphatics C9-C10 Aromatics Lead
Not sampled on prior dates
LOCATION DATE TOC (ft)DTW (ft),
BTOC SWLE (ft)OF DITCH
MW-2 06/02/11 98.52 7.90 90.62 ---8.25MW-2 08/29/11 98.52 8.45 90.07 ---7.70MW-2 04/27/12 98.52 7.27 91.25 ---8.88MW-2 08/16/12 98.52 8.39 90.13 ---7.76MW-2 02/13/13 98.52 8.09 90.43 ---8.06MW-2 09/05/13 98.52 8.32 90.20 ---7.83MW-2 05/01/14 98.52 8.14 90.38 ---8.01MW-2 09/23/14 98.52 8.51 90.01 ---7.64MW-2 10/28/15 98.52 8.06 90.46 ---8.09
MW-11 08/29/11 93.21 9.84 83.37 ---1.00MW-11 04/27/12 93.21 9.29 83.92 ---1.55MW-11 08/16/12 93.21 9.52 83.69 ---1.32MW-11 02/13/13 93.21 9.39 83.82 ---1.45MW-11 09/05/13 93.21 9.62 83.59 ---1.22MW-11 05/01/14 93.21 9.42 83.79 ---1.42MW-11 09/23/14 93.21 9.72 83.49 ---1.12MW-11 10/28/15 93.21 8.95 84.26 ---1.89MW-11 08/03/16 93.21 9.62 83.59 ---1.22MW-11 12/21/17 93.21 9.20 84.01 ---1.64MW-11 06/27/18 93.21 9.20 84.01 ---1.64MW-11 03/25/19 93.21 9.43 83.78 ---1.41MW-11 06/18/20 93.21 9.17 84.04 ---1.67MW-11 11/18/20 93.21 9.24 83.97 ---1.60MW-11 06/08/21 93.21 9.74 83.47 ---1.10MW-11 12/20/21 93.21 9.79 83.42 ---1.05
MW-12 08/29/11 94.31 10.17 84.14 ---1.77MW-12 04/27/12 94.31 9.74 84.57 ---2.20MW-12 08/16/12 94.31 10.12 84.19 ---1.82MW-12 02/13/13 94.31 9.88 84.43 ---2.06MW-12 09/05/13 94.31 10.14 84.17 ---1.80MW-12 05/01/14 94.31 9.94 84.37 ---2.00MW-12 09/23/14 94.31 10.28 84.03 ---1.66
Stream #1 04/13/12 82.37
04/13/12 81.72
MID-ATLANTIC JOB NO. 000R1760.25
TABLE 5.3ELEVATION COMPARISON OF THE WATER TABLE TO DRAINAGE DITCHSPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINADWM INCIDENT NO.: 28414
APPENDIX A SELECTED HISTORICAL SITE INFORMATION
Total Boring Depth (ft):
ft
-
b
g
s
Sampling
Interval,
Odors
TV
A
-
P
I
D
(
p
p
m
)
Re
c
o
v
e
r
y
SOIL DESCRIPTION (color, texture, moisture, etc.)Construction Deatails
Grout: 0.5'-3'
Plug: 3'-5'
Sand: 5'-17'
Screen: 7'-17'
Marocore to 20 feet BLS
*Boring terminated by technician at 17 feet BLS
Type II groundwater monitoring well set to 17 feet BLS
32 32
36 36
40 40
COMMENTS:in - indicates inches B - bentonite
Hollow stem augers (8" OD) used for well install ft - indicates depth in feet ppm - indicates parts per million
DTW - Depth to Water ft-bgs - indicates feet below ground surface TD - Total Depth of Boring for Sampling
12 12
Tan / White mottled, soft, Sandy Silt (Saprolite)
Black / White weathered rock. Strong petroleum odor
28 28
Black / White weathered rock. Strong petroleum odor
16 16
20 20
24 24
ft
-
b
g
s
Tan / White mottled, soft, Silty Clay (Saprolite)
8
4 4
Light Brown, micaceous, Silty Clay
Wet at 7 feet. Strong petroleum odor.8
G. Fischer
Date Started:8/3/2016 Driller :Kenny Sargent DTW (08/04/16):8.65
Date Completed:8/3/2016 Monitoring Equipment:MAA Field Staff:
17 ft
Location: Lenoir, NC Subcontractor/Drillers: Geologic Exploration Screen Depth (ft):7 - 17 ft
Project Number:R1760 Sampling Method:Macrocore Well Depth (ft):
Site Name: Speedway #7972 Drilling/Boring Method:Hollow Stem Auger 8" OD 17 ft
409 Rogers View Ct.
Raleigh, NC 27610Ph: (919) 250-9918
LOG OF BORING: MW-15
Page:1 of 1
Total Boring Depth (ft):
ft
-
b
g
s
Sampling
Interval,
Odors
TV
A
-
P
I
D
(
p
p
m
)
Re
c
o
v
e
r
y
SOIL DESCRIPTION (color, texture, moisture, etc.)Construction Deatails
Grout: 0.5'-3'
Plug: 3'-5'
Sand: 5'-17'
Screen: 6'-16'
Marocore to 20 feet BLS
*Boring terminated by technician at 16 feet BLS
Type II groundwater monitoring well set to 16 feet BLS
32 32
36 36
40 40
COMMENTS:in - indicates inches B - bentonite
Hollow stem augers (8" OD) used for well install ft - indicates depth in feet ppm - indicates parts per million
DTW - Depth to Water ft-bgs - indicates feet below ground surface TD - Total Depth of Boring for Sampling
409 Rogers View Ct.
Raleigh, NC 27610Ph: (919) 250-9918
LOG OF BORING: MW-16
Page:1 of 1
Site Name: Speedway #7972 Drilling/Boring Method:Hollow Stem Auger 8" OD 16 ft
16 ft
Location: Lenoir, NC Subcontractor/Drillers: Geologic Exploration Screen Depth (ft):6 - 16 ft
Project Number:R1760 Sampling Method:Macrocore Well Depth (ft):
G. Fischer
Date Started:8/3/2016 Driller :Kenny Sargent DTW (08/04/16):7.64
Date Completed:8/3/2016 Monitoring Equipment:MAA Field Staff:
ft
-
b
g
s
4 4
24
8 Tan / White / Black mottled, soft, Silty Clay (Saprolite)8
12 12
28 28
Orange Brown, micaceous, Clayey Silt
Wet at 8 feet. Strong petroleum odor.
Black / White weathered rock. Strong petroleum odor
Tan / White mottled, soft, Silty Clay
Black / White weathered rock. Strong petroleum odor
16 16
20 20
24
APPENDIX B MID-ATLANTIC FIELD PROCEDURES
Groundwater Sampling Procedures
I. Sample Collection
A. Monitoring Wells
Prior to sample collection, each well is purged of three to five standing well volumes
or to dryness to remove stagnant water from the well and well bore in an effort to
collect samples that are representative of the water quality in the formation
surrounding each well. Purging is performed either with a new, polyethylene bailer
dedicated to each well, or with a decontaminated pump. Samples are retrieved from
the monitoring well using the dedicated bailer. New nylon string is used on each
dedicated bailer, and new nitrile sampling gloves are donned prior to purging and
sampling of each well.
B. Geoprobe “Screen Point Sampler”
The screen point sampler is a “grab” sampling device that is driven into the
saturated zone and a surrounding metal sheath is retracted, exposing a screen.
Groundwater entering the screen is then drawn to land surface through disposable
tubing that is placed through the hollow push rods. The sample is collected from the
tubing into the appropriate sampling glassware.
C. Water-Supply Wells
Water samples are typically collected from the available spigot that is nearest to the
well. The water is allowed to run at a high flow from the spigot for approximately 10
to 15 minutes to allow the water in the delivery lines to be purged. The sample flow
is then reduced and the samples are collected directly into pre-labeled containers as
described below. New nitrile sampling gloves are donned prior to sampling of each
well.
D. Treatment System Influent/Effluent
Samples are typically collected from the influent or effluent of pump-and-treat
groundwater remediation systems using designated sampling ports in the influent
and effluent water transport lines. The water is typically allowed to run for several
seconds to clear potential debris in the sampling port. The sample is then collected
directly into sampling containers as described below. New nitrile sampling gloves
are donned prior to sample collection.
II. Preparation for Laboratory Analysis
Groundwater samples are decanted directly into laboratory-prepared, pre-labeled,
sampling containers, packed in ice, and shipped to a certified laboratory under chain-of-
custody control. Laboratory analyses performed on the samples are specified on the chain-
of-custody.
Surface Water Sampling Procedures
I. Sample Collection
Surface water samples are collected using properly decontaminated equipment or directly into
laboratory-supplied sampling containers. Samples are generally collected at or near a suspected
discharge point for contaminated groundwater. In small streams and ditches, samples are
collected as close to mid-channel as possible. Samples are not collected from stagnant areas or
areas of turbulent flow.
II. Preparation for Laboratory Analysis
Surface water samples are decanted directly into laboratory-prepared, pre-labeled, sampling
containers, packed in ice, and shipped to a certified laboratory under chain-of-custody control.
Laboratory analyses performed on the samples are specified on the chain-of-custody.
Hydraulic Gradient Determination Procedure The hydraulic gradient, which is a measure of the “steepness” of the water table, is
determined by dividing the change in the elevation (in feet) of the water table over the
change in horizontal distance (in feet) between two measuring points. Typically, the gradient is determined after the Water Table Elevation Contour Map is prepared. Two wells are typically selected that, when a line is drawn between the wells, the orientation of this line approximates the direction of groundwater flow. The greater the horizontal
distance between the lines, the more representative the hydraulic gradient value will be for
the site. If two wells are not arranged in line with groundwater flow, the hydraulic gradient can be estimated by performing the same calculation using the contours generated for the groundwater flow direction map. The units for the hydraulic gradient are feet/feet.
The hydraulic gradient (measured from MW-8 to MW-15) for the subject site was
determined as follows: Gradient = dh/dl = (90.36 – 83.62) / 102 = 0.066 ft/ft
where:
dh = change in head (more specifically, water table elevation) in feet dl = horizontal distance (in feet) between monitoring wells or other head measurement points.
APPENDIX C LABORATORY ANALYTICAL REPORTS AND CHAIN-
OF-CUSTODY RECORDS FOR GROUNDWATER & SURFACE WATER
SAMPLES
ANALYTICAL REPORT
January 04, 2022
Mid-Atlantic - Speedway NC
Sample Delivery Group:L1445294
Samples Received:12/22/2021
Project Number:R1760.14
Description:Speedway #7972
Site:7972
Report To:Cameron Moore
409 Rogers View Court
Raleigh, NC 27610
Entire Report Reviewed By:
January 04, 2022
[Preliminary Report]
T. Alan Harvill
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 www.pacenational.com
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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January 04, 2022
T. Alan Harvill
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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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-3 L1445294-01 6
MW-11 L1445294-02 8
MW-15 L1445294-03 10
MW-16 L1445294-04 12
STREAM #1 L1445294-05 14
STREAM #2 L1445294-06 16
STREAM #3 L1445294-07 18
TRIP BLANK L1445294-08 20
Qc: Quality Control Summary 22
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 22
Gl: Glossary of Terms 28
Al: Accreditations & Locations 29
Sc: Sample Chain of Custody 30
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
MW-3 L1445294-01 GW Gary A. Fischer 12/20/21 08:00 12/22/21 10:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1795877 1 12/29/21 02:44 12/29/21 02:44 BMB Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1797287 1 01/03/22 12:50 01/03/22 12:50 ACG Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-11 L1445294-02 GW Gary A. Fischer 12/20/21 08:35 12/22/21 10:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1795877 1 12/29/21 03:05 12/29/21 03:05 BMB Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-15 L1445294-03 GW Gary A. Fischer 12/20/21 08:45 12/22/21 10:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1795877 1 12/29/21 03:26 12/29/21 03:26 BMB Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1796906 1 01/02/22 13:15 01/02/22 13:15 BMB Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-16 L1445294-04 GW Gary A. Fischer 12/20/21 09:10 12/22/21 10:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1795877 10 12/29/21 05:33 12/29/21 05:33 BMB Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1796906 10 01/02/22 14:16 01/02/22 14:16 BMB Mt. Juliet, TN
Collected by Collected date/time Received date/time
STREAM #1 L1445294-05 GW Gary A. Fischer 12/20/21 10:30 12/22/21 10:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1795877 1 12/29/21 03:47 12/29/21 03:47 BMB Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1796906 1 01/02/22 13:35 01/02/22 13:35 BMB Mt. Juliet, TN
Collected by Collected date/time Received date/time
STREAM #2 L1445294-06 GW Gary A. Fischer 12/20/21 10:50 12/22/21 10:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1795877 1 12/29/21 04:08 12/29/21 04:08 BMB Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1796906 1 01/02/22 13:56 01/02/22 13:56 BMB Mt. Juliet, TN
Collected by Collected date/time Received date/time
STREAM #3 L1445294-07 GW Gary A. Fischer 12/20/21 10:15 12/22/21 10:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1795877 1 12/29/21 04:29 12/29/21 04:29 BMB Mt. Juliet, TN
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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SAMPLE SUMMARY
Collected by Collected date/time Received date/time
TRIP BLANK L1445294-08 GW Gary A. Fischer 12/20/21 00:00 12/22/21 10:30
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1795877 1 12/29/21 01:19 12/29/21 01:19 BMB Mt. Juliet, TN
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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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]
T. Alan Harvill
Project Manager
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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T. Alan Harvill
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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SAMPLE RESULTS - 01
L1445294
MW-3
Collected date/time: 12/20/21 08:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.147 1.00 1 12/29/2021 02:44 WG1795877
1,1,1-Trichloroethane U 0.149 1.00 1 12/29/2021 02:44 WG1795877
1,1,2,2-Tetrachloroethane U J4 0.133 1.00 1 12/29/2021 02:44 WG1795877
1,1,2-Trichloroethane U 0.158 1.00 1 12/29/2021 02:44 WG1795877
1,1-Dichloroethane U 0.100 1.00 1 12/29/2021 02:44 WG1795877
1,1-Dichloroethene U 0.188 1.00 1 12/29/2021 02:44 WG1795877
1,1-Dichloropropene U 0.142 1.00 1 12/29/2021 02:44 WG1795877
1,2,3-Trichlorobenzene U J4 0.230 1.00 1 12/29/2021 02:44 WG1795877
1,2,3-Trichloropropane U J4 0.237 2.50 1 12/29/2021 02:44 WG1795877
1,2,4-Trichlorobenzene U 0.481 1.00 1 12/29/2021 02:44 WG1795877
1,2,4-Trimethylbenzene 1.02 0.322 1.00 1 12/29/2021 02:44 WG1795877
1,2-Dibromo-3-Chloropropane U 0.276 5.00 1 12/29/2021 02:44 WG1795877
1,2-Dibromoethane U 0.126 1.00 1 12/29/2021 02:44 WG1795877
1,2-Dichlorobenzene U 0.107 1.00 1 12/29/2021 02:44 WG1795877
1,2-Dichloroethane U 0.0819 1.00 1 12/29/2021 02:44 WG1795877
1,2-Dichloropropane U 0.149 1.00 1 12/29/2021 02:44 WG1795877
1,3,5-Trimethylbenzene U 0.104 1.00 1 01/03/2022 12:50 WG1797287
1,3-Dichlorobenzene U 0.110 1.00 1 12/29/2021 02:44 WG1795877
1,3-Dichloropropane U 0.110 1.00 1 12/29/2021 02:44 WG1795877
1,4-Dichlorobenzene U 0.120 1.00 1 12/29/2021 02:44 WG1795877
2,2-Dichloropropane U 0.161 1.00 1 12/29/2021 02:44 WG1795877
2-Butanone (MEK)U 1.19 10.0 1 12/29/2021 02:44 WG1795877
2-Chlorotoluene U 0.106 1.00 1 12/29/2021 02:44 WG1795877
4-Chlorotoluene U 0.114 1.00 1 12/29/2021 02:44 WG1795877
4-Methyl-2-pentanone (MIBK)U 0.478 10.0 1 12/29/2021 02:44 WG1795877
Acetone U 11.3 50.0 1 12/29/2021 02:44 WG1795877
Acrolein U 2.54 50.0 1 12/29/2021 02:44 WG1795877
Acrylonitrile U 0.671 10.0 1 12/29/2021 02:44 WG1795877
Benzene 37.2 0.0941 1.00 1 12/29/2021 02:44 WG1795877
Bromobenzene U 0.118 1.00 1 12/29/2021 02:44 WG1795877
Bromodichloromethane U 0.136 1.00 1 12/29/2021 02:44 WG1795877
Bromoform U 0.129 1.00 1 12/29/2021 02:44 WG1795877
Bromomethane U 0.605 5.00 1 12/29/2021 02:44 WG1795877
Carbon tetrachloride U 0.128 1.00 1 12/29/2021 02:44 WG1795877
Chlorobenzene U 0.116 1.00 1 12/29/2021 02:44 WG1795877
Chloroethane U 0.192 5.00 1 12/29/2021 02:44 WG1795877
Chloroform U 0.111 5.00 1 12/29/2021 02:44 WG1795877
Chloromethane U 0.960 2.50 1 12/29/2021 02:44 WG1795877
Chlorodibromomethane U 0.140 1.00 1 12/29/2021 02:44 WG1795877
Dibromomethane U 0.122 1.00 1 12/29/2021 02:44 WG1795877
Dichlorodifluoromethane U 0.374 5.00 1 12/29/2021 02:44 WG1795877
Di-isopropyl ether 55.4 0.105 1.00 1 12/29/2021 02:44 WG1795877
Ethylbenzene 3.20 0.137 1.00 1 12/29/2021 02:44 WG1795877
Hexachloro-1,3-butadiene U J4 0.337 1.00 1 12/29/2021 02:44 WG1795877
Isopropylbenzene 1.11 0.105 1.00 1 12/29/2021 02:44 WG1795877
Methyl tert-butyl ether 8.02 0.101 1.00 1 12/29/2021 02:44 WG1795877
Methylene Chloride U 0.430 5.00 1 12/29/2021 02:44 WG1795877
Naphthalene 2.45 J 1.00 5.00 1 12/29/2021 02:44 WG1795877
Styrene U 0.118 1.00 1 12/29/2021 02:44 WG1795877
Tetrachloroethene U 0.300 1.00 1 12/29/2021 02:44 WG1795877
Toluene 1.11 0.278 1.00 1 12/29/2021 02:44 WG1795877
Trichloroethene U 0.190 1.00 1 12/29/2021 02:44 WG1795877
Trichlorofluoromethane U 0.160 5.00 1 12/29/2021 02:44 WG1795877
Vinyl chloride U 0.234 1.00 1 12/29/2021 02:44 WG1795877
cis-1,2-Dichloroethene U 0.126 1.00 1 12/29/2021 02:44 WG1795877
m&p-Xylenes U 0.430 2.00 1 12/29/2021 02:44 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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SAMPLE RESULTS - 01
L1445294
MW-3
Collected date/time: 12/20/21 08:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene 0.341 J 0.157 1.00 1 01/03/2022 12:50 WG1797287
n-Propylbenzene 1.18 0.0993 1.00 1 01/03/2022 12:50 WG1797287
o-Xylene 1.11 0.174 1.00 1 12/29/2021 02:44 WG1795877
p-Isopropyltoluene U 0.120 1.00 1 12/29/2021 02:44 WG1795877
sec-Butylbenzene 0.507 J 0.125 1.00 1 01/03/2022 12:50 WG1797287
tert-Butylbenzene U 0.127 1.00 1 12/29/2021 02:44 WG1795877
trans-1,2-Dichloroethene U 0.149 1.00 1 12/29/2021 02:44 WG1795877
(S) Toluene-d8 95.9 80.0-120 12/29/2021 02:44 WG1795877
(S) Toluene-d8 96.3 80.0-120 01/03/2022 12:50 WG1797287
(S) 4-Bromofluorobenzene 91.6 77.0-126 12/29/2021 02:44 WG1795877
(S) 4-Bromofluorobenzene 98.5 77.0-126 01/03/2022 12:50 WG1797287
(S) 1,2-Dichloroethane-d4 110 70.0-130 12/29/2021 02:44 WG1795877
(S) 1,2-Dichloroethane-d4 91.3 70.0-130 01/03/2022 12:50 WG1797287
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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SAMPLE RESULTS - 02
L1445294
MW-11
Collected date/time: 12/20/21 08:35
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.147 1.00 1 12/29/2021 03:05 WG1795877
1,1,1-Trichloroethane U 0.149 1.00 1 12/29/2021 03:05 WG1795877
1,1,2,2-Tetrachloroethane U J4 0.133 1.00 1 12/29/2021 03:05 WG1795877
1,1,2-Trichloroethane U 0.158 1.00 1 12/29/2021 03:05 WG1795877
1,1-Dichloroethane U 0.100 1.00 1 12/29/2021 03:05 WG1795877
1,1-Dichloroethene U 0.188 1.00 1 12/29/2021 03:05 WG1795877
1,1-Dichloropropene U 0.142 1.00 1 12/29/2021 03:05 WG1795877
1,2,3-Trichlorobenzene U J4 0.230 1.00 1 12/29/2021 03:05 WG1795877
1,2,3-Trichloropropane U J4 0.237 2.50 1 12/29/2021 03:05 WG1795877
1,2,4-Trichlorobenzene U 0.481 1.00 1 12/29/2021 03:05 WG1795877
1,2,4-Trimethylbenzene U 0.322 1.00 1 12/29/2021 03:05 WG1795877
1,2-Dibromo-3-Chloropropane U 0.276 5.00 1 12/29/2021 03:05 WG1795877
1,2-Dibromoethane U 0.126 1.00 1 12/29/2021 03:05 WG1795877
1,2-Dichlorobenzene U 0.107 1.00 1 12/29/2021 03:05 WG1795877
1,2-Dichloroethane U 0.0819 1.00 1 12/29/2021 03:05 WG1795877
1,2-Dichloropropane U 0.149 1.00 1 12/29/2021 03:05 WG1795877
1,3,5-Trimethylbenzene U J4 0.104 1.00 1 12/29/2021 03:05 WG1795877
1,3-Dichlorobenzene U 0.110 1.00 1 12/29/2021 03:05 WG1795877
1,3-Dichloropropane U 0.110 1.00 1 12/29/2021 03:05 WG1795877
1,4-Dichlorobenzene U 0.120 1.00 1 12/29/2021 03:05 WG1795877
2,2-Dichloropropane U 0.161 1.00 1 12/29/2021 03:05 WG1795877
2-Butanone (MEK)U 1.19 10.0 1 12/29/2021 03:05 WG1795877
2-Chlorotoluene U 0.106 1.00 1 12/29/2021 03:05 WG1795877
4-Chlorotoluene U 0.114 1.00 1 12/29/2021 03:05 WG1795877
4-Methyl-2-pentanone (MIBK)U 0.478 10.0 1 12/29/2021 03:05 WG1795877
Acetone U 11.3 50.0 1 12/29/2021 03:05 WG1795877
Acrolein U 2.54 50.0 1 12/29/2021 03:05 WG1795877
Acrylonitrile U 0.671 10.0 1 12/29/2021 03:05 WG1795877
Benzene U 0.0941 1.00 1 12/29/2021 03:05 WG1795877
Bromobenzene U 0.118 1.00 1 12/29/2021 03:05 WG1795877
Bromodichloromethane U 0.136 1.00 1 12/29/2021 03:05 WG1795877
Bromoform U 0.129 1.00 1 12/29/2021 03:05 WG1795877
Bromomethane U 0.605 5.00 1 12/29/2021 03:05 WG1795877
Carbon tetrachloride U 0.128 1.00 1 12/29/2021 03:05 WG1795877
Chlorobenzene U 0.116 1.00 1 12/29/2021 03:05 WG1795877
Chloroethane U 0.192 5.00 1 12/29/2021 03:05 WG1795877
Chloroform U 0.111 5.00 1 12/29/2021 03:05 WG1795877
Chloromethane U 0.960 2.50 1 12/29/2021 03:05 WG1795877
Chlorodibromomethane U 0.140 1.00 1 12/29/2021 03:05 WG1795877
Dibromomethane U 0.122 1.00 1 12/29/2021 03:05 WG1795877
Dichlorodifluoromethane U 0.374 5.00 1 12/29/2021 03:05 WG1795877
Di-isopropyl ether 36.1 0.105 1.00 1 12/29/2021 03:05 WG1795877
Ethylbenzene U 0.137 1.00 1 12/29/2021 03:05 WG1795877
Hexachloro-1,3-butadiene U J4 0.337 1.00 1 12/29/2021 03:05 WG1795877
Isopropylbenzene U 0.105 1.00 1 12/29/2021 03:05 WG1795877
Methyl tert-butyl ether 3.69 0.101 1.00 1 12/29/2021 03:05 WG1795877
Methylene Chloride U 0.430 5.00 1 12/29/2021 03:05 WG1795877
Naphthalene U 1.00 5.00 1 12/29/2021 03:05 WG1795877
Styrene U 0.118 1.00 1 12/29/2021 03:05 WG1795877
Tetrachloroethene U 0.300 1.00 1 12/29/2021 03:05 WG1795877
Toluene U 0.278 1.00 1 12/29/2021 03:05 WG1795877
Trichloroethene U 0.190 1.00 1 12/29/2021 03:05 WG1795877
Trichlorofluoromethane U 0.160 5.00 1 12/29/2021 03:05 WG1795877
Vinyl chloride U 0.234 1.00 1 12/29/2021 03:05 WG1795877
cis-1,2-Dichloroethene U 0.126 1.00 1 12/29/2021 03:05 WG1795877
m&p-Xylenes U 0.430 2.00 1 12/29/2021 03:05 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 8 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 8 of 32
SAMPLE RESULTS - 02
L1445294
MW-11
Collected date/time: 12/20/21 08:35
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U J4 0.157 1.00 1 12/29/2021 03:05 WG1795877
n-Propylbenzene U J4 0.0993 1.00 1 12/29/2021 03:05 WG1795877
o-Xylene U 0.174 1.00 1 12/29/2021 03:05 WG1795877
p-Isopropyltoluene U 0.120 1.00 1 12/29/2021 03:05 WG1795877
sec-Butylbenzene U J4 0.125 1.00 1 12/29/2021 03:05 WG1795877
tert-Butylbenzene U 0.127 1.00 1 12/29/2021 03:05 WG1795877
trans-1,2-Dichloroethene U 0.149 1.00 1 12/29/2021 03:05 WG1795877
(S) Toluene-d8 97.1 80.0-120 12/29/2021 03:05 WG1795877
(S) 4-Bromofluorobenzene 90.4 77.0-126 12/29/2021 03:05 WG1795877
(S) 1,2-Dichloroethane-d4 113 70.0-130 12/29/2021 03:05 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 9 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 9 of 32
SAMPLE RESULTS - 03
L1445294
MW-15
Collected date/time: 12/20/21 08:45
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.147 1.00 1 12/29/2021 03:26 WG1795877
1,1,1-Trichloroethane U 0.149 1.00 1 12/29/2021 03:26 WG1795877
1,1,2,2-Tetrachloroethane U J4 0.133 1.00 1 12/29/2021 03:26 WG1795877
1,1,2-Trichloroethane U 0.158 1.00 1 12/29/2021 03:26 WG1795877
1,1-Dichloroethane U 0.100 1.00 1 12/29/2021 03:26 WG1795877
1,1-Dichloroethene U 0.188 1.00 1 12/29/2021 03:26 WG1795877
1,1-Dichloropropene U 0.142 1.00 1 12/29/2021 03:26 WG1795877
1,2,3-Trichlorobenzene U J4 0.230 1.00 1 12/29/2021 03:26 WG1795877
1,2,3-Trichloropropane U J4 0.237 2.50 1 12/29/2021 03:26 WG1795877
1,2,4-Trichlorobenzene U 0.481 1.00 1 12/29/2021 03:26 WG1795877
1,2,4-Trimethylbenzene 1.94 0.322 1.00 1 12/29/2021 03:26 WG1795877
1,2-Dibromo-3-Chloropropane U 0.276 5.00 1 12/29/2021 03:26 WG1795877
1,2-Dibromoethane U 0.126 1.00 1 12/29/2021 03:26 WG1795877
1,2-Dichlorobenzene U 0.107 1.00 1 12/29/2021 03:26 WG1795877
1,2-Dichloroethane U 0.0819 1.00 1 12/29/2021 03:26 WG1795877
1,2-Dichloropropane U 0.149 1.00 1 12/29/2021 03:26 WG1795877
1,3,5-Trimethylbenzene 0.482 J 0.104 1.00 1 01/02/2022 13:15 WG1796906
1,3-Dichlorobenzene U 0.110 1.00 1 12/29/2021 03:26 WG1795877
1,3-Dichloropropane U 0.110 1.00 1 12/29/2021 03:26 WG1795877
1,4-Dichlorobenzene U 0.120 1.00 1 12/29/2021 03:26 WG1795877
2,2-Dichloropropane U 0.161 1.00 1 12/29/2021 03:26 WG1795877
2-Butanone (MEK)U 1.19 10.0 1 12/29/2021 03:26 WG1795877
2-Chlorotoluene U 0.106 1.00 1 12/29/2021 03:26 WG1795877
4-Chlorotoluene U 0.114 1.00 1 12/29/2021 03:26 WG1795877
4-Methyl-2-pentanone (MIBK)U 0.478 10.0 1 12/29/2021 03:26 WG1795877
Acetone U 11.3 50.0 1 12/29/2021 03:26 WG1795877
Acrolein U 2.54 50.0 1 12/29/2021 03:26 WG1795877
Acrylonitrile U 0.671 10.0 1 12/29/2021 03:26 WG1795877
Benzene 0.145 J 0.0941 1.00 1 12/29/2021 03:26 WG1795877
Bromobenzene U 0.118 1.00 1 12/29/2021 03:26 WG1795877
Bromodichloromethane U 0.136 1.00 1 12/29/2021 03:26 WG1795877
Bromoform U 0.129 1.00 1 12/29/2021 03:26 WG1795877
Bromomethane U 0.605 5.00 1 12/29/2021 03:26 WG1795877
Carbon tetrachloride U 0.128 1.00 1 12/29/2021 03:26 WG1795877
Chlorobenzene U 0.116 1.00 1 12/29/2021 03:26 WG1795877
Chloroethane U 0.192 5.00 1 12/29/2021 03:26 WG1795877
Chloroform U 0.111 5.00 1 12/29/2021 03:26 WG1795877
Chloromethane U 0.960 2.50 1 12/29/2021 03:26 WG1795877
Chlorodibromomethane U 0.140 1.00 1 12/29/2021 03:26 WG1795877
Dibromomethane U 0.122 1.00 1 12/29/2021 03:26 WG1795877
Dichlorodifluoromethane U 0.374 5.00 1 12/29/2021 03:26 WG1795877
Di-isopropyl ether 7.74 0.105 1.00 1 12/29/2021 03:26 WG1795877
Ethylbenzene 2.07 0.137 1.00 1 12/29/2021 03:26 WG1795877
Hexachloro-1,3-butadiene U J4 0.337 1.00 1 12/29/2021 03:26 WG1795877
Isopropylbenzene 0.344 J 0.105 1.00 1 12/29/2021 03:26 WG1795877
Methyl tert-butyl ether 17.0 0.101 1.00 1 12/29/2021 03:26 WG1795877
Methylene Chloride U 0.430 5.00 1 12/29/2021 03:26 WG1795877
Naphthalene 1.21 J 1.00 5.00 1 12/29/2021 03:26 WG1795877
Styrene U 0.118 1.00 1 12/29/2021 03:26 WG1795877
Tetrachloroethene U 0.300 1.00 1 12/29/2021 03:26 WG1795877
Toluene 0.388 J 0.278 1.00 1 12/29/2021 03:26 WG1795877
Trichloroethene U 0.190 1.00 1 12/29/2021 03:26 WG1795877
Trichlorofluoromethane U 0.160 5.00 1 12/29/2021 03:26 WG1795877
Vinyl chloride U 0.234 1.00 1 12/29/2021 03:26 WG1795877
cis-1,2-Dichloroethene U 0.126 1.00 1 12/29/2021 03:26 WG1795877
m&p-Xylenes 2.15 0.430 2.00 1 12/29/2021 03:26 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 10 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 10 of 32
SAMPLE RESULTS - 03
L1445294
MW-15
Collected date/time: 12/20/21 08:45
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U J4 0.157 1.00 1 12/29/2021 03:26 WG1795877
n-Propylbenzene 0.764 J 0.0993 1.00 1 01/02/2022 13:15 WG1796906
o-Xylene 0.212 J 0.174 1.00 1 12/29/2021 03:26 WG1795877
p-Isopropyltoluene U 0.120 1.00 1 12/29/2021 03:26 WG1795877
sec-Butylbenzene 0.811 J 0.125 1.00 1 01/02/2022 13:15 WG1796906
tert-Butylbenzene U 0.127 1.00 1 12/29/2021 03:26 WG1795877
trans-1,2-Dichloroethene U 0.149 1.00 1 12/29/2021 03:26 WG1795877
(S) Toluene-d8 96.3 80.0-120 12/29/2021 03:26 WG1795877
(S) Toluene-d8 100 80.0-120 01/02/2022 13:15 WG1796906
(S) 4-Bromofluorobenzene 90.3 77.0-126 12/29/2021 03:26 WG1795877
(S) 4-Bromofluorobenzene 94.9 77.0-126 01/02/2022 13:15 WG1796906
(S) 1,2-Dichloroethane-d4 109 70.0-130 12/29/2021 03:26 WG1795877
(S) 1,2-Dichloroethane-d4 93.6 70.0-130 01/02/2022 13:15 WG1796906
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 11 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 11 of 32
SAMPLE RESULTS - 04
L1445294
MW-16
Collected date/time: 12/20/21 09:10
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 1.47 10.0 10 12/29/2021 05:33 WG1795877
1,1,1-Trichloroethane U 1.49 10.0 10 12/29/2021 05:33 WG1795877
1,1,2,2-Tetrachloroethane U J4 1.33 10.0 10 12/29/2021 05:33 WG1795877
1,1,2-Trichloroethane U 1.58 10.0 10 12/29/2021 05:33 WG1795877
1,1-Dichloroethane U 1.00 10.0 10 12/29/2021 05:33 WG1795877
1,1-Dichloroethene U 1.88 10.0 10 12/29/2021 05:33 WG1795877
1,1-Dichloropropene U 1.42 10.0 10 12/29/2021 05:33 WG1795877
1,2,3-Trichlorobenzene U J4 2.30 10.0 10 12/29/2021 05:33 WG1795877
1,2,3-Trichloropropane U J4 2.37 25.0 10 12/29/2021 05:33 WG1795877
1,2,4-Trichlorobenzene U 4.81 10.0 10 12/29/2021 05:33 WG1795877
1,2,4-Trimethylbenzene 258 3.22 10.0 10 12/29/2021 05:33 WG1795877
1,2-Dibromo-3-Chloropropane U 2.76 50.0 10 12/29/2021 05:33 WG1795877
1,2-Dibromoethane U 1.26 10.0 10 12/29/2021 05:33 WG1795877
1,2-Dichlorobenzene U 1.07 10.0 10 12/29/2021 05:33 WG1795877
1,2-Dichloroethane U 0.819 10.0 10 12/29/2021 05:33 WG1795877
1,2-Dichloropropane U 1.49 10.0 10 12/29/2021 05:33 WG1795877
1,3,5-Trimethylbenzene 47.0 1.04 10.0 10 01/02/2022 14:16 WG1796906
1,3-Dichlorobenzene U 1.10 10.0 10 12/29/2021 05:33 WG1795877
1,3-Dichloropropane U 1.10 10.0 10 12/29/2021 05:33 WG1795877
1,4-Dichlorobenzene U 1.20 10.0 10 12/29/2021 05:33 WG1795877
2,2-Dichloropropane U 1.61 10.0 10 12/29/2021 05:33 WG1795877
2-Butanone (MEK)U 11.9 100 10 12/29/2021 05:33 WG1795877
2-Chlorotoluene U 1.06 10.0 10 12/29/2021 05:33 WG1795877
4-Chlorotoluene U 1.14 10.0 10 12/29/2021 05:33 WG1795877
4-Methyl-2-pentanone (MIBK)U 4.78 100 10 12/29/2021 05:33 WG1795877
Acetone U 113 500 10 12/29/2021 05:33 WG1795877
Acrolein U 25.4 500 10 12/29/2021 05:33 WG1795877
Acrylonitrile U 6.71 100 10 12/29/2021 05:33 WG1795877
Benzene U 0.941 10.0 10 12/29/2021 05:33 WG1795877
Bromobenzene U 1.18 10.0 10 12/29/2021 05:33 WG1795877
Bromodichloromethane U 1.36 10.0 10 12/29/2021 05:33 WG1795877
Bromoform U 1.29 10.0 10 12/29/2021 05:33 WG1795877
Bromomethane U 6.05 50.0 10 12/29/2021 05:33 WG1795877
Carbon tetrachloride U 1.28 10.0 10 12/29/2021 05:33 WG1795877
Chlorobenzene U 1.16 10.0 10 12/29/2021 05:33 WG1795877
Chloroethane U 1.92 50.0 10 12/29/2021 05:33 WG1795877
Chloroform U 1.11 50.0 10 12/29/2021 05:33 WG1795877
Chloromethane U 9.60 25.0 10 12/29/2021 05:33 WG1795877
Chlorodibromomethane U 1.40 10.0 10 12/29/2021 05:33 WG1795877
Dibromomethane U 1.22 10.0 10 12/29/2021 05:33 WG1795877
Dichlorodifluoromethane U 3.74 50.0 10 12/29/2021 05:33 WG1795877
Di-isopropyl ether 9.91 J 1.05 10.0 10 12/29/2021 05:33 WG1795877
Ethylbenzene 14.0 1.37 10.0 10 12/29/2021 05:33 WG1795877
Hexachloro-1,3-butadiene U J4 3.37 10.0 10 12/29/2021 05:33 WG1795877
Isopropylbenzene 7.41 J 1.05 10.0 10 12/29/2021 05:33 WG1795877
Methyl tert-butyl ether 11.7 1.01 10.0 10 12/29/2021 05:33 WG1795877
Methylene Chloride U 4.30 50.0 10 12/29/2021 05:33 WG1795877
Naphthalene 19.5 J 10.0 50.0 10 12/29/2021 05:33 WG1795877
Styrene U 1.18 10.0 10 12/29/2021 05:33 WG1795877
Tetrachloroethene U 3.00 10.0 10 12/29/2021 05:33 WG1795877
Toluene U 2.78 10.0 10 12/29/2021 05:33 WG1795877
Trichloroethene U 1.90 10.0 10 12/29/2021 05:33 WG1795877
Trichlorofluoromethane U 1.60 50.0 10 12/29/2021 05:33 WG1795877
Vinyl chloride U 2.34 10.0 10 12/29/2021 05:33 WG1795877
cis-1,2-Dichloroethene U 1.26 10.0 10 12/29/2021 05:33 WG1795877
m&p-Xylenes 30.9 4.30 20.0 10 12/29/2021 05:33 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 12 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 12 of 32
SAMPLE RESULTS - 04
L1445294
MW-16
Collected date/time: 12/20/21 09:10
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U 1.57 10.0 10 01/02/2022 14:16 WG1796906
n-Propylbenzene 21.5 0.993 10.0 10 01/02/2022 14:16 WG1796906
o-Xylene 13.4 1.74 10.0 10 12/29/2021 05:33 WG1795877
p-Isopropyltoluene U 1.20 10.0 10 12/29/2021 05:33 WG1795877
sec-Butylbenzene U 1.25 10.0 10 01/02/2022 14:16 WG1796906
tert-Butylbenzene U 1.27 10.0 10 12/29/2021 05:33 WG1795877
trans-1,2-Dichloroethene U 1.49 10.0 10 12/29/2021 05:33 WG1795877
(S) Toluene-d8 102 80.0-120 12/29/2021 05:33 WG1795877
(S) Toluene-d8 98.6 80.0-120 01/02/2022 14:16 WG1796906
(S) 4-Bromofluorobenzene 104 77.0-126 12/29/2021 05:33 WG1795877
(S) 4-Bromofluorobenzene 95.6 77.0-126 01/02/2022 14:16 WG1796906
(S) 1,2-Dichloroethane-d4 111 70.0-130 12/29/2021 05:33 WG1795877
(S) 1,2-Dichloroethane-d4 90.3 70.0-130 01/02/2022 14:16 WG1796906
Sample Narrative:
L1445294-04 WG1795877: Target compounds too high to run at a lower dilution.
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 13 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 13 of 32
SAMPLE RESULTS - 05
L1445294
STREAM #1
Collected date/time: 12/20/21 10:30
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.147 1.00 1 12/29/2021 03:47 WG1795877
1,1,1-Trichloroethane U 0.149 1.00 1 12/29/2021 03:47 WG1795877
1,1,2,2-Tetrachloroethane U J4 0.133 1.00 1 12/29/2021 03:47 WG1795877
1,1,2-Trichloroethane U 0.158 1.00 1 12/29/2021 03:47 WG1795877
1,1-Dichloroethane U 0.100 1.00 1 12/29/2021 03:47 WG1795877
1,1-Dichloroethene U 0.188 1.00 1 12/29/2021 03:47 WG1795877
1,1-Dichloropropene U 0.142 1.00 1 12/29/2021 03:47 WG1795877
1,2,3-Trichlorobenzene U J4 0.230 1.00 1 12/29/2021 03:47 WG1795877
1,2,3-Trichloropropane U J4 0.237 2.50 1 12/29/2021 03:47 WG1795877
1,2,4-Trichlorobenzene U 0.481 1.00 1 12/29/2021 03:47 WG1795877
1,2,4-Trimethylbenzene 1.28 0.322 1.00 1 12/29/2021 03:47 WG1795877
1,2-Dibromo-3-Chloropropane U 0.276 5.00 1 12/29/2021 03:47 WG1795877
1,2-Dibromoethane U 0.126 1.00 1 12/29/2021 03:47 WG1795877
1,2-Dichlorobenzene U 0.107 1.00 1 12/29/2021 03:47 WG1795877
1,2-Dichloroethane U 0.0819 1.00 1 12/29/2021 03:47 WG1795877
1,2-Dichloropropane U 0.149 1.00 1 12/29/2021 03:47 WG1795877
1,3,5-Trimethylbenzene 0.202 J 0.104 1.00 1 01/02/2022 13:35 WG1796906
1,3-Dichlorobenzene U 0.110 1.00 1 12/29/2021 03:47 WG1795877
1,3-Dichloropropane U 0.110 1.00 1 12/29/2021 03:47 WG1795877
1,4-Dichlorobenzene U 0.120 1.00 1 12/29/2021 03:47 WG1795877
2,2-Dichloropropane U 0.161 1.00 1 12/29/2021 03:47 WG1795877
2-Butanone (MEK)U 1.19 10.0 1 12/29/2021 03:47 WG1795877
2-Chlorotoluene U 0.106 1.00 1 12/29/2021 03:47 WG1795877
4-Chlorotoluene U 0.114 1.00 1 12/29/2021 03:47 WG1795877
4-Methyl-2-pentanone (MIBK)U 0.478 10.0 1 12/29/2021 03:47 WG1795877
Acetone U 11.3 50.0 1 12/29/2021 03:47 WG1795877
Acrolein U 2.54 50.0 1 12/29/2021 03:47 WG1795877
Acrylonitrile U 0.671 10.0 1 12/29/2021 03:47 WG1795877
Benzene U 0.0941 1.00 1 12/29/2021 03:47 WG1795877
Bromobenzene U 0.118 1.00 1 12/29/2021 03:47 WG1795877
Bromodichloromethane U 0.136 1.00 1 12/29/2021 03:47 WG1795877
Bromoform U 0.129 1.00 1 12/29/2021 03:47 WG1795877
Bromomethane U 0.605 5.00 1 12/29/2021 03:47 WG1795877
Carbon tetrachloride U 0.128 1.00 1 12/29/2021 03:47 WG1795877
Chlorobenzene U 0.116 1.00 1 12/29/2021 03:47 WG1795877
Chloroethane U 0.192 5.00 1 12/29/2021 03:47 WG1795877
Chloroform 0.147 J 0.111 5.00 1 12/29/2021 03:47 WG1795877
Chloromethane U 0.960 2.50 1 12/29/2021 03:47 WG1795877
Chlorodibromomethane U 0.140 1.00 1 12/29/2021 03:47 WG1795877
Dibromomethane U 0.122 1.00 1 12/29/2021 03:47 WG1795877
Dichlorodifluoromethane U 0.374 5.00 1 12/29/2021 03:47 WG1795877
Di-isopropyl ether 0.272 J 0.105 1.00 1 12/29/2021 03:47 WG1795877
Ethylbenzene 0.569 J 0.137 1.00 1 12/29/2021 03:47 WG1795877
Hexachloro-1,3-butadiene U J4 0.337 1.00 1 12/29/2021 03:47 WG1795877
Isopropylbenzene U 0.105 1.00 1 12/29/2021 03:47 WG1795877
Methyl tert-butyl ether 0.143 J 0.101 1.00 1 12/29/2021 03:47 WG1795877
Methylene Chloride U 0.430 5.00 1 12/29/2021 03:47 WG1795877
Naphthalene U 1.00 5.00 1 12/29/2021 03:47 WG1795877
Styrene U 0.118 1.00 1 12/29/2021 03:47 WG1795877
Tetrachloroethene U 0.300 1.00 1 12/29/2021 03:47 WG1795877
Toluene U 0.278 1.00 1 12/29/2021 03:47 WG1795877
Trichloroethene U 0.190 1.00 1 12/29/2021 03:47 WG1795877
Trichlorofluoromethane U 0.160 5.00 1 12/29/2021 03:47 WG1795877
Vinyl chloride U 0.234 1.00 1 12/29/2021 03:47 WG1795877
cis-1,2-Dichloroethene U 0.126 1.00 1 12/29/2021 03:47 WG1795877
m&p-Xylenes U 0.430 2.00 1 12/29/2021 03:47 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 14 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 14 of 32
SAMPLE RESULTS - 05
L1445294
STREAM #1
Collected date/time: 12/20/21 10:30
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U J4 0.157 1.00 1 12/29/2021 03:47 WG1795877
n-Propylbenzene 0.216 J 0.0993 1.00 1 01/02/2022 13:35 WG1796906
o-Xylene U 0.174 1.00 1 12/29/2021 03:47 WG1795877
p-Isopropyltoluene U 0.120 1.00 1 12/29/2021 03:47 WG1795877
sec-Butylbenzene U J4 0.125 1.00 1 12/29/2021 03:47 WG1795877
tert-Butylbenzene U 0.127 1.00 1 12/29/2021 03:47 WG1795877
trans-1,2-Dichloroethene U 0.149 1.00 1 12/29/2021 03:47 WG1795877
(S) Toluene-d8 93.5 80.0-120 12/29/2021 03:47 WG1795877
(S) Toluene-d8 101 80.0-120 01/02/2022 13:35 WG1796906
(S) 4-Bromofluorobenzene 88.3 77.0-126 12/29/2021 03:47 WG1795877
(S) 4-Bromofluorobenzene 97.6 77.0-126 01/02/2022 13:35 WG1796906
(S) 1,2-Dichloroethane-d4 111 70.0-130 12/29/2021 03:47 WG1795877
(S) 1,2-Dichloroethane-d4 85.8 70.0-130 01/02/2022 13:35 WG1796906
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 15 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 15 of 32
SAMPLE RESULTS - 06
L1445294
STREAM #2
Collected date/time: 12/20/21 10:50
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.147 1.00 1 12/29/2021 04:08 WG1795877
1,1,1-Trichloroethane U 0.149 1.00 1 12/29/2021 04:08 WG1795877
1,1,2,2-Tetrachloroethane U J4 0.133 1.00 1 12/29/2021 04:08 WG1795877
1,1,2-Trichloroethane U 0.158 1.00 1 12/29/2021 04:08 WG1795877
1,1-Dichloroethane U 0.100 1.00 1 12/29/2021 04:08 WG1795877
1,1-Dichloroethene U 0.188 1.00 1 12/29/2021 04:08 WG1795877
1,1-Dichloropropene U 0.142 1.00 1 12/29/2021 04:08 WG1795877
1,2,3-Trichlorobenzene U J4 0.230 1.00 1 12/29/2021 04:08 WG1795877
1,2,3-Trichloropropane U J4 0.237 2.50 1 12/29/2021 04:08 WG1795877
1,2,4-Trichlorobenzene U 0.481 1.00 1 12/29/2021 04:08 WG1795877
1,2,4-Trimethylbenzene 0.554 J 0.322 1.00 1 12/29/2021 04:08 WG1795877
1,2-Dibromo-3-Chloropropane U 0.276 5.00 1 12/29/2021 04:08 WG1795877
1,2-Dibromoethane U 0.126 1.00 1 12/29/2021 04:08 WG1795877
1,2-Dichlorobenzene U 0.107 1.00 1 12/29/2021 04:08 WG1795877
1,2-Dichloroethane U 0.0819 1.00 1 12/29/2021 04:08 WG1795877
1,2-Dichloropropane U 0.149 1.00 1 12/29/2021 04:08 WG1795877
1,3,5-Trimethylbenzene U 0.104 1.00 1 01/02/2022 13:56 WG1796906
1,3-Dichlorobenzene U 0.110 1.00 1 12/29/2021 04:08 WG1795877
1,3-Dichloropropane U 0.110 1.00 1 12/29/2021 04:08 WG1795877
1,4-Dichlorobenzene U 0.120 1.00 1 12/29/2021 04:08 WG1795877
2,2-Dichloropropane U 0.161 1.00 1 12/29/2021 04:08 WG1795877
2-Butanone (MEK)U 1.19 10.0 1 12/29/2021 04:08 WG1795877
2-Chlorotoluene U 0.106 1.00 1 12/29/2021 04:08 WG1795877
4-Chlorotoluene U 0.114 1.00 1 12/29/2021 04:08 WG1795877
4-Methyl-2-pentanone (MIBK)U 0.478 10.0 1 12/29/2021 04:08 WG1795877
Acetone U 11.3 50.0 1 12/29/2021 04:08 WG1795877
Acrolein U 2.54 50.0 1 12/29/2021 04:08 WG1795877
Acrylonitrile U 0.671 10.0 1 12/29/2021 04:08 WG1795877
Benzene U 0.0941 1.00 1 12/29/2021 04:08 WG1795877
Bromobenzene U 0.118 1.00 1 12/29/2021 04:08 WG1795877
Bromodichloromethane U 0.136 1.00 1 12/29/2021 04:08 WG1795877
Bromoform U 0.129 1.00 1 12/29/2021 04:08 WG1795877
Bromomethane U 0.605 5.00 1 12/29/2021 04:08 WG1795877
Carbon tetrachloride U 0.128 1.00 1 12/29/2021 04:08 WG1795877
Chlorobenzene U 0.116 1.00 1 12/29/2021 04:08 WG1795877
Chloroethane U 0.192 5.00 1 12/29/2021 04:08 WG1795877
Chloroform 0.146 J 0.111 5.00 1 12/29/2021 04:08 WG1795877
Chloromethane U 0.960 2.50 1 12/29/2021 04:08 WG1795877
Chlorodibromomethane U 0.140 1.00 1 12/29/2021 04:08 WG1795877
Dibromomethane U 0.122 1.00 1 12/29/2021 04:08 WG1795877
Dichlorodifluoromethane U 0.374 5.00 1 12/29/2021 04:08 WG1795877
Di-isopropyl ether 0.626 J 0.105 1.00 1 12/29/2021 04:08 WG1795877
Ethylbenzene 0.268 J 0.137 1.00 1 12/29/2021 04:08 WG1795877
Hexachloro-1,3-butadiene U J4 0.337 1.00 1 12/29/2021 04:08 WG1795877
Isopropylbenzene U 0.105 1.00 1 12/29/2021 04:08 WG1795877
Methyl tert-butyl ether 0.167 J 0.101 1.00 1 12/29/2021 04:08 WG1795877
Methylene Chloride U 0.430 5.00 1 12/29/2021 04:08 WG1795877
Naphthalene U 1.00 5.00 1 12/29/2021 04:08 WG1795877
Styrene U 0.118 1.00 1 12/29/2021 04:08 WG1795877
Tetrachloroethene U 0.300 1.00 1 12/29/2021 04:08 WG1795877
Toluene U 0.278 1.00 1 12/29/2021 04:08 WG1795877
Trichloroethene U 0.190 1.00 1 12/29/2021 04:08 WG1795877
Trichlorofluoromethane U 0.160 5.00 1 12/29/2021 04:08 WG1795877
Vinyl chloride U 0.234 1.00 1 12/29/2021 04:08 WG1795877
cis-1,2-Dichloroethene U 0.126 1.00 1 12/29/2021 04:08 WG1795877
m&p-Xylenes U 0.430 2.00 1 12/29/2021 04:08 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 16 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 16 of 32
SAMPLE RESULTS - 06
L1445294
STREAM #2
Collected date/time: 12/20/21 10:50
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U J4 0.157 1.00 1 12/29/2021 04:08 WG1795877
n-Propylbenzene U 0.0993 1.00 1 01/02/2022 13:56 WG1796906
o-Xylene U 0.174 1.00 1 12/29/2021 04:08 WG1795877
p-Isopropyltoluene U 0.120 1.00 1 12/29/2021 04:08 WG1795877
sec-Butylbenzene U J4 0.125 1.00 1 12/29/2021 04:08 WG1795877
tert-Butylbenzene U 0.127 1.00 1 12/29/2021 04:08 WG1795877
trans-1,2-Dichloroethene U 0.149 1.00 1 12/29/2021 04:08 WG1795877
(S) Toluene-d8 95.2 80.0-120 12/29/2021 04:08 WG1795877
(S) Toluene-d8 98.9 80.0-120 01/02/2022 13:56 WG1796906
(S) 4-Bromofluorobenzene 89.4 77.0-126 12/29/2021 04:08 WG1795877
(S) 4-Bromofluorobenzene 97.1 77.0-126 01/02/2022 13:56 WG1796906
(S) 1,2-Dichloroethane-d4 113 70.0-130 12/29/2021 04:08 WG1795877
(S) 1,2-Dichloroethane-d4 91.2 70.0-130 01/02/2022 13:56 WG1796906
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 17 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 17 of 32
SAMPLE RESULTS - 07
L1445294
STREAM #3
Collected date/time: 12/20/21 10:15
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.147 1.00 1 12/29/2021 04:29 WG1795877
1,1,1-Trichloroethane U 0.149 1.00 1 12/29/2021 04:29 WG1795877
1,1,2,2-Tetrachloroethane U J4 0.133 1.00 1 12/29/2021 04:29 WG1795877
1,1,2-Trichloroethane U 0.158 1.00 1 12/29/2021 04:29 WG1795877
1,1-Dichloroethane U 0.100 1.00 1 12/29/2021 04:29 WG1795877
1,1-Dichloroethene U 0.188 1.00 1 12/29/2021 04:29 WG1795877
1,1-Dichloropropene U 0.142 1.00 1 12/29/2021 04:29 WG1795877
1,2,3-Trichlorobenzene U J4 0.230 1.00 1 12/29/2021 04:29 WG1795877
1,2,3-Trichloropropane U J4 0.237 2.50 1 12/29/2021 04:29 WG1795877
1,2,4-Trichlorobenzene U 0.481 1.00 1 12/29/2021 04:29 WG1795877
1,2,4-Trimethylbenzene U 0.322 1.00 1 12/29/2021 04:29 WG1795877
1,2-Dibromo-3-Chloropropane U 0.276 5.00 1 12/29/2021 04:29 WG1795877
1,2-Dibromoethane U 0.126 1.00 1 12/29/2021 04:29 WG1795877
1,2-Dichlorobenzene U 0.107 1.00 1 12/29/2021 04:29 WG1795877
1,2-Dichloroethane U 0.0819 1.00 1 12/29/2021 04:29 WG1795877
1,2-Dichloropropane U 0.149 1.00 1 12/29/2021 04:29 WG1795877
1,3,5-Trimethylbenzene U J4 0.104 1.00 1 12/29/2021 04:29 WG1795877
1,3-Dichlorobenzene U 0.110 1.00 1 12/29/2021 04:29 WG1795877
1,3-Dichloropropane U 0.110 1.00 1 12/29/2021 04:29 WG1795877
1,4-Dichlorobenzene U 0.120 1.00 1 12/29/2021 04:29 WG1795877
2,2-Dichloropropane U 0.161 1.00 1 12/29/2021 04:29 WG1795877
2-Butanone (MEK)U 1.19 10.0 1 12/29/2021 04:29 WG1795877
2-Chlorotoluene U 0.106 1.00 1 12/29/2021 04:29 WG1795877
4-Chlorotoluene U 0.114 1.00 1 12/29/2021 04:29 WG1795877
4-Methyl-2-pentanone (MIBK)U 0.478 10.0 1 12/29/2021 04:29 WG1795877
Acetone U 11.3 50.0 1 12/29/2021 04:29 WG1795877
Acrolein U 2.54 50.0 1 12/29/2021 04:29 WG1795877
Acrylonitrile U 0.671 10.0 1 12/29/2021 04:29 WG1795877
Benzene U 0.0941 1.00 1 12/29/2021 04:29 WG1795877
Bromobenzene U 0.118 1.00 1 12/29/2021 04:29 WG1795877
Bromodichloromethane U 0.136 1.00 1 12/29/2021 04:29 WG1795877
Bromoform U 0.129 1.00 1 12/29/2021 04:29 WG1795877
Bromomethane U 0.605 5.00 1 12/29/2021 04:29 WG1795877
Carbon tetrachloride U 0.128 1.00 1 12/29/2021 04:29 WG1795877
Chlorobenzene U 0.116 1.00 1 12/29/2021 04:29 WG1795877
Chloroethane U 0.192 5.00 1 12/29/2021 04:29 WG1795877
Chloroform 0.208 J 0.111 5.00 1 12/29/2021 04:29 WG1795877
Chloromethane U 0.960 2.50 1 12/29/2021 04:29 WG1795877
Chlorodibromomethane U 0.140 1.00 1 12/29/2021 04:29 WG1795877
Dibromomethane U 0.122 1.00 1 12/29/2021 04:29 WG1795877
Dichlorodifluoromethane U 0.374 5.00 1 12/29/2021 04:29 WG1795877
Di-isopropyl ether U 0.105 1.00 1 12/29/2021 04:29 WG1795877
Ethylbenzene U 0.137 1.00 1 12/29/2021 04:29 WG1795877
Hexachloro-1,3-butadiene U J4 0.337 1.00 1 12/29/2021 04:29 WG1795877
Isopropylbenzene U 0.105 1.00 1 12/29/2021 04:29 WG1795877
Methyl tert-butyl ether U 0.101 1.00 1 12/29/2021 04:29 WG1795877
Methylene Chloride U 0.430 5.00 1 12/29/2021 04:29 WG1795877
Naphthalene U 1.00 5.00 1 12/29/2021 04:29 WG1795877
Styrene U 0.118 1.00 1 12/29/2021 04:29 WG1795877
Tetrachloroethene U 0.300 1.00 1 12/29/2021 04:29 WG1795877
Toluene U 0.278 1.00 1 12/29/2021 04:29 WG1795877
Trichloroethene U 0.190 1.00 1 12/29/2021 04:29 WG1795877
Trichlorofluoromethane U 0.160 5.00 1 12/29/2021 04:29 WG1795877
Vinyl chloride U 0.234 1.00 1 12/29/2021 04:29 WG1795877
cis-1,2-Dichloroethene U 0.126 1.00 1 12/29/2021 04:29 WG1795877
m&p-Xylenes U 0.430 2.00 1 12/29/2021 04:29 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 18 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 18 of 32
SAMPLE RESULTS - 07
L1445294
STREAM #3
Collected date/time: 12/20/21 10:15
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U J4 0.157 1.00 1 12/29/2021 04:29 WG1795877
n-Propylbenzene U J4 0.0993 1.00 1 12/29/2021 04:29 WG1795877
o-Xylene U 0.174 1.00 1 12/29/2021 04:29 WG1795877
p-Isopropyltoluene U 0.120 1.00 1 12/29/2021 04:29 WG1795877
sec-Butylbenzene U J4 0.125 1.00 1 12/29/2021 04:29 WG1795877
tert-Butylbenzene U 0.127 1.00 1 12/29/2021 04:29 WG1795877
trans-1,2-Dichloroethene U 0.149 1.00 1 12/29/2021 04:29 WG1795877
(S) Toluene-d8 95.3 80.0-120 12/29/2021 04:29 WG1795877
(S) 4-Bromofluorobenzene 90.6 77.0-126 12/29/2021 04:29 WG1795877
(S) 1,2-Dichloroethane-d4 112 70.0-130 12/29/2021 04:29 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 14:58 19 of 32
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.14 L1445294 01/04/22 15:16 19 of 32
SAMPLE RESULTS - 08
L1445294
TRIP BLANK
Collected date/time: 12/20/21 00:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.147 1.00 1 12/29/2021 01:19 WG1795877
1,1,1-Trichloroethane U 0.149 1.00 1 12/29/2021 01:19 WG1795877
1,1,2,2-Tetrachloroethane U J4 0.133 1.00 1 12/29/2021 01:19 WG1795877
1,1,2-Trichloroethane U 0.158 1.00 1 12/29/2021 01:19 WG1795877
1,1-Dichloroethane U 0.100 1.00 1 12/29/2021 01:19 WG1795877
1,1-Dichloroethene U 0.188 1.00 1 12/29/2021 01:19 WG1795877
1,1-Dichloropropene U 0.142 1.00 1 12/29/2021 01:19 WG1795877
1,2,3-Trichlorobenzene U J4 0.230 1.00 1 12/29/2021 01:19 WG1795877
1,2,3-Trichloropropane U J4 0.237 2.50 1 12/29/2021 01:19 WG1795877
1,2,4-Trichlorobenzene U 0.481 1.00 1 12/29/2021 01:19 WG1795877
1,2,4-Trimethylbenzene U 0.322 1.00 1 12/29/2021 01:19 WG1795877
1,2-Dibromo-3-Chloropropane U 0.276 5.00 1 12/29/2021 01:19 WG1795877
1,2-Dibromoethane U 0.126 1.00 1 12/29/2021 01:19 WG1795877
1,2-Dichlorobenzene U 0.107 1.00 1 12/29/2021 01:19 WG1795877
1,2-Dichloroethane U 0.0819 1.00 1 12/29/2021 01:19 WG1795877
1,2-Dichloropropane U 0.149 1.00 1 12/29/2021 01:19 WG1795877
1,3,5-Trimethylbenzene U J4 0.104 1.00 1 12/29/2021 01:19 WG1795877
1,3-Dichlorobenzene U 0.110 1.00 1 12/29/2021 01:19 WG1795877
1,3-Dichloropropane U 0.110 1.00 1 12/29/2021 01:19 WG1795877
1,4-Dichlorobenzene U 0.120 1.00 1 12/29/2021 01:19 WG1795877
2,2-Dichloropropane U 0.161 1.00 1 12/29/2021 01:19 WG1795877
2-Butanone (MEK)U 1.19 10.0 1 12/29/2021 01:19 WG1795877
2-Chlorotoluene U 0.106 1.00 1 12/29/2021 01:19 WG1795877
4-Chlorotoluene U 0.114 1.00 1 12/29/2021 01:19 WG1795877
4-Methyl-2-pentanone (MIBK)U 0.478 10.0 1 12/29/2021 01:19 WG1795877
Acetone U 11.3 50.0 1 12/29/2021 01:19 WG1795877
Acrolein U 2.54 50.0 1 12/29/2021 01:19 WG1795877
Acrylonitrile U 0.671 10.0 1 12/29/2021 01:19 WG1795877
Benzene U 0.0941 1.00 1 12/29/2021 01:19 WG1795877
Bromobenzene U 0.118 1.00 1 12/29/2021 01:19 WG1795877
Bromodichloromethane U 0.136 1.00 1 12/29/2021 01:19 WG1795877
Bromoform U 0.129 1.00 1 12/29/2021 01:19 WG1795877
Bromomethane U 0.605 5.00 1 12/29/2021 01:19 WG1795877
Carbon tetrachloride U 0.128 1.00 1 12/29/2021 01:19 WG1795877
Chlorobenzene U 0.116 1.00 1 12/29/2021 01:19 WG1795877
Chloroethane U 0.192 5.00 1 12/29/2021 01:19 WG1795877
Chloroform U 0.111 5.00 1 12/29/2021 01:19 WG1795877
Chloromethane U 0.960 2.50 1 12/29/2021 01:19 WG1795877
Chlorodibromomethane U 0.140 1.00 1 12/29/2021 01:19 WG1795877
Dibromomethane U 0.122 1.00 1 12/29/2021 01:19 WG1795877
Dichlorodifluoromethane U 0.374 5.00 1 12/29/2021 01:19 WG1795877
Di-isopropyl ether U 0.105 1.00 1 12/29/2021 01:19 WG1795877
Ethylbenzene U 0.137 1.00 1 12/29/2021 01:19 WG1795877
Hexachloro-1,3-butadiene U J4 0.337 1.00 1 12/29/2021 01:19 WG1795877
Isopropylbenzene U 0.105 1.00 1 12/29/2021 01:19 WG1795877
Methyl tert-butyl ether U 0.101 1.00 1 12/29/2021 01:19 WG1795877
Methylene Chloride U 0.430 5.00 1 12/29/2021 01:19 WG1795877
Naphthalene U 1.00 5.00 1 12/29/2021 01:19 WG1795877
Styrene U 0.118 1.00 1 12/29/2021 01:19 WG1795877
Tetrachloroethene U 0.300 1.00 1 12/29/2021 01:19 WG1795877
Toluene U 0.278 1.00 1 12/29/2021 01:19 WG1795877
Trichloroethene U 0.190 1.00 1 12/29/2021 01:19 WG1795877
Trichlorofluoromethane U 0.160 5.00 1 12/29/2021 01:19 WG1795877
Vinyl chloride U 0.234 1.00 1 12/29/2021 01:19 WG1795877
cis-1,2-Dichloroethene U 0.126 1.00 1 12/29/2021 01:19 WG1795877
m&p-Xylenes U 0.430 2.00 1 12/29/2021 01:19 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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SAMPLE RESULTS - 08
L1445294
TRIP BLANK
Collected date/time: 12/20/21 00:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U J4 0.157 1.00 1 12/29/2021 01:19 WG1795877
n-Propylbenzene U J4 0.0993 1.00 1 12/29/2021 01:19 WG1795877
o-Xylene U 0.174 1.00 1 12/29/2021 01:19 WG1795877
p-Isopropyltoluene U 0.120 1.00 1 12/29/2021 01:19 WG1795877
sec-Butylbenzene U J4 0.125 1.00 1 12/29/2021 01:19 WG1795877
tert-Butylbenzene U 0.127 1.00 1 12/29/2021 01:19 WG1795877
trans-1,2-Dichloroethene U 0.149 1.00 1 12/29/2021 01:19 WG1795877
(S) Toluene-d8 108 80.0-120 12/29/2021 01:19 WG1795877
(S) 4-Bromofluorobenzene 103 77.0-126 12/29/2021 01:19 WG1795877
(S) 1,2-Dichloroethane-d4 114 70.0-130 12/29/2021 01:19 WG1795877
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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QUALITY CONTROL SUMMARYWG1795877
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1445294-01,02,03,04,05,06,07,08
Method Blank (MB)
(MB) R3746503-2 12/29/21 00:57
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/l ug/l ug/l
Acetone U 11.3 50.0
Acrolein U 2.54 50.0
Acrylonitrile U 0.671 10.0
Benzene U 0.0941 1.00
Bromobenzene U 0.118 1.00
Bromodichloromethane U 0.136 1.00
Bromoform U 0.129 1.00
Bromomethane U 0.605 5.00
n-Butylbenzene U 0.157 1.00
sec-Butylbenzene U 0.125 1.00
tert-Butylbenzene U 0.127 1.00
Carbon tetrachloride U 0.128 1.00
Chlorobenzene U 0.116 1.00
Chlorodibromomethane U 0.140 1.00
Chloroethane U 0.192 5.00
Chloroform U 0.111 5.00
Chloromethane U 0.960 2.50
2-Chlorotoluene U 0.106 1.00
4-Chlorotoluene U 0.114 1.00
1,2-Dibromo-3-Chloropropane U 0.276 5.00
1,2-Dibromoethane U 0.126 1.00
Dibromomethane U 0.122 1.00
1,2-Dichlorobenzene U 0.107 1.00
1,3-Dichlorobenzene U 0.110 1.00
1,4-Dichlorobenzene U 0.120 1.00
Dichlorodifluoromethane U 0.374 5.00
1,1-Dichloroethane U 0.100 1.00
1,2-Dichloroethane U 0.0819 1.00
1,1-Dichloroethene U 0.188 1.00
cis-1,2-Dichloroethene U 0.126 1.00
trans-1,2-Dichloroethene U 0.149 1.00
1,2-Dichloropropane U 0.149 1.00
1,1-Dichloropropene U 0.142 1.00
1,3-Dichloropropane U 0.110 1.00
2,2-Dichloropropane U 0.161 1.00
Di-isopropyl ether U 0.105 1.00
Ethylbenzene U 0.137 1.00
Hexachloro-1,3-butadiene U 0.337 1.00
Isopropylbenzene U 0.105 1.00
p-Isopropyltoluene U 0.120 1.00
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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QUALITY CONTROL SUMMARYWG1795877
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1445294-01,02,03,04,05,06,07,08
Method Blank (MB)
(MB) R3746503-2 12/29/21 00:57
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/l ug/l ug/l
2-Butanone (MEK)U 1.19 10.0
Methylene Chloride U 0.430 5.00
4-Methyl-2-pentanone (MIBK)U 0.478 10.0
Methyl tert-butyl ether U 0.101 1.00
Naphthalene U 1.00 5.00
n-Propylbenzene U 0.0993 1.00
Styrene U 0.118 1.00
1,1,1,2-Tetrachloroethane U 0.147 1.00
1,1,2,2-Tetrachloroethane U 0.133 1.00
Tetrachloroethene U 0.300 1.00
Toluene U 0.278 1.00
1,2,3-Trichlorobenzene U 0.230 1.00
1,2,4-Trichlorobenzene U 0.481 1.00
1,1,1-Trichloroethane U 0.149 1.00
1,1,2-Trichloroethane U 0.158 1.00
Trichloroethene U 0.190 1.00
Trichlorofluoromethane U 0.160 5.00
1,2,3-Trichloropropane U 0.237 2.50
1,2,4-Trimethylbenzene U 0.322 1.00
1,3,5-Trimethylbenzene U 0.104 1.00
Vinyl chloride U 0.234 1.00
o-Xylene U 0.174 1.00
m&p-Xylenes U 0.430 2.00
(S) Toluene-d8 99.1 80.0-120
(S) 4-Bromofluorobenzene 91.0 77.0-126
(S) 1,2-Dichloroethane-d4 105 70.0-130
Laboratory Control Sample (LCS)
(LCS) R3746503-1 12/29/21 00:15
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte ug/l ug/l %%
Acetone 25.0 35.4 142 19.0-160
Acrolein 25.0 20.5 82.0 10.0-160
Acrylonitrile 25.0 26.2 105 55.0-149
Benzene 5.00 5.31 106 70.0-123
Bromobenzene 5.00 5.24 105 73.0-121
Bromodichloromethane 5.00 5.22 104 75.0-120
Bromoform 5.00 4.48 89.6 68.0-132
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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QUALITY CONTROL SUMMARYWG1795877
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1445294-01,02,03,04,05,06,07,08
Laboratory Control Sample (LCS)
(LCS) R3746503-1 12/29/21 00:15
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte ug/l ug/l %%
Bromomethane 5.00 4.99 99.8 10.0-160
n-Butylbenzene 5.00 6.84 137 73.0-125 J4
sec-Butylbenzene 5.00 6.33 127 75.0-125 J4
tert-Butylbenzene 5.00 5.97 119 76.0-124
Carbon tetrachloride 5.00 5.18 104 68.0-126
Chlorobenzene 5.00 4.39 87.8 80.0-121
Chlorodibromomethane 5.00 4.40 88.0 77.0-125
Chloroethane 5.00 4.50 90.0 47.0-150
Chloroform 5.00 5.60 112 73.0-120
Chloromethane 5.00 3.43 68.6 41.0-142
2-Chlorotoluene 5.00 5.27 105 76.0-123
4-Chlorotoluene 5.00 5.36 107 75.0-122
1,2-Dibromo-3-Chloropropane 5.00 6.57 131 58.0-134
1,2-Dibromoethane 5.00 4.58 91.6 80.0-122
Dibromomethane 5.00 5.56 111 80.0-120
1,2-Dichlorobenzene 5.00 5.45 109 79.0-121
1,3-Dichlorobenzene 5.00 5.07 101 79.0-120
1,4-Dichlorobenzene 5.00 5.53 111 79.0-120
Dichlorodifluoromethane 5.00 5.14 103 51.0-149
1,1-Dichloroethane 5.00 5.35 107 70.0-126
1,2-Dichloroethane 5.00 5.35 107 70.0-128
1,1-Dichloroethene 5.00 5.35 107 71.0-124
cis-1,2-Dichloroethene 5.00 5.06 101 73.0-120
trans-1,2-Dichloroethene 5.00 4.85 97.0 73.0-120
1,2-Dichloropropane 5.00 4.65 93.0 77.0-125
1,1-Dichloropropene 5.00 5.67 113 74.0-126
1,3-Dichloropropane 5.00 5.27 105 80.0-120
2,2-Dichloropropane 5.00 6.22 124 58.0-130
Di-isopropyl ether 5.00 3.99 79.8 58.0-138
Ethylbenzene 5.00 4.52 90.4 79.0-123
Hexachloro-1,3-butadiene 5.00 6.99 140 54.0-138 J4
Isopropylbenzene 5.00 4.99 99.8 76.0-127
p-Isopropyltoluene 5.00 6.13 123 76.0-125
2-Butanone (MEK)25.0 26.4 106 44.0-160
Methylene Chloride 5.00 4.93 98.6 67.0-120
4-Methyl-2-pentanone (MIBK)25.0 22.8 91.2 68.0-142
Methyl tert-butyl ether 5.00 5.14 103 68.0-125
Naphthalene 5.00 6.13 123 54.0-135
n-Propylbenzene 5.00 6.56 131 77.0-124 J4
Styrene 5.00 4.66 93.2 73.0-130
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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QUALITY CONTROL SUMMARYWG1795877
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1445294-01,02,03,04,05,06,07,08
Laboratory Control Sample (LCS)
(LCS) R3746503-1 12/29/21 00:15
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte ug/l ug/l %%
1,1,1,2-Tetrachloroethane 5.00 4.45 89.0 75.0-125
1,1,2,2-Tetrachloroethane 5.00 6.91 138 65.0-130 J4
Tetrachloroethene 5.00 4.07 81.4 72.0-132
Toluene 5.00 4.63 92.6 79.0-120
1,2,3-Trichlorobenzene 5.00 7.49 150 50.0-138 J4
1,2,4-Trichlorobenzene 5.00 6.76 135 57.0-137
1,1,1-Trichloroethane 5.00 5.50 110 73.0-124
1,1,2-Trichloroethane 5.00 4.80 96.0 80.0-120
Trichloroethene 5.00 4.16 83.2 78.0-124
Trichlorofluoromethane 5.00 4.96 99.2 59.0-147
1,2,3-Trichloropropane 5.00 6.64 133 73.0-130 J4
1,2,4-Trimethylbenzene 5.00 5.86 117 76.0-121
1,3,5-Trimethylbenzene 5.00 6.30 126 76.0-122 J4
Vinyl chloride 5.00 4.25 85.0 67.0-131
o-Xylene 5.00 4.41 88.2 80.0-122
m&p-Xylenes 10.0 8.73 87.3 80.0-122
(S) Toluene-d8 93.4 80.0-120
(S) 4-Bromofluorobenzene 90.7 77.0-126
(S) 1,2-Dichloroethane-d4 108 70.0-130
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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QUALITY CONTROL SUMMARYWG1796906
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1445294-03,04,05,06
Method Blank (MB)
(MB) R3746720-4 01/02/22 12:11
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/l ug/l ug/l
n-Butylbenzene U 0.157 1.00
sec-Butylbenzene U 0.125 1.00
n-Propylbenzene U 0.0993 1.00
1,3,5-Trimethylbenzene U 0.104 1.00
(S) Toluene-d8 102 80.0-120
(S) 4-Bromofluorobenzene 93.9 77.0-126
(S) 1,2-Dichloroethane-d4 94.9 70.0-130
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3746720-1 01/02/22 10:28 • (LCSD) R3746720-2 01/02/22 10:48
Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte ug/l ug/l ug/l %%%%%
n-Butylbenzene 5.00 4.15 4.57 83.0 91.4 73.0-125 9.63 20
sec-Butylbenzene 5.00 4.41 4.34 88.2 86.8 75.0-125 1.60 20
n-Propylbenzene 5.00 4.50 4.38 90.0 87.6 77.0-124 2.70 20
1,3,5-Trimethylbenzene 5.00 4.31 4.52 86.2 90.4 76.0-122 4.76 20
(S) Toluene-d8 97.6 99.5 80.0-120
(S) 4-Bromofluorobenzene 94.8 92.1 77.0-126
(S) 1,2-Dichloroethane-d4 88.6 91.8 70.0-130
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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QUALITY CONTROL SUMMARYWG1797287
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1445294-01
Method Blank (MB)
(MB) R3746909-5 01/03/22 12:00
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/l ug/l ug/l
n-Butylbenzene U 0.157 1.00
sec-Butylbenzene U 0.125 1.00
n-Propylbenzene U 0.0993 1.00
1,3,5-Trimethylbenzene U 0.104 1.00
(S) Toluene-d8 97.8 80.0-120
(S) 4-Bromofluorobenzene 95.4 77.0-126
(S) 1,2-Dichloroethane-d4 92.3 70.0-130
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3746909-1 01/03/22 10:17 • (LCSD) R3746909-2 01/03/22 10:38
Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte ug/l ug/l ug/l %%%%%
n-Butylbenzene 5.00 4.88 4.83 97.6 96.6 73.0-125 1.03 20
sec-Butylbenzene 5.00 4.40 4.60 88.0 92.0 75.0-125 4.44 20
n-Propylbenzene 5.00 4.59 4.83 91.8 96.6 77.0-124 5.10 20
1,3,5-Trimethylbenzene 5.00 4.71 5.01 94.2 100 76.0-122 6.17 20
(S) Toluene-d8 97.8 96.3 80.0-120
(S) 4-Bromofluorobenzene 93.9 95.9 77.0-126
(S) 1,2-Dichloroethane-d4 93.9 92.9 70.0-130
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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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.
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
J The identification of the analyte is acceptable; the reported value is an estimate.
J4 The associated batch QC was outside the established quality control range for accuracy.
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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* 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
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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Chain-of-Custody-Record
Printed: 01/04/2022
1,1,1,2-Tetrachloroethane ug/L, 1,1,1-Trichloroethane ug/L, 1,1,2,2-Tetrachloroethane ug/L, 1,1,2-Trichloroethane ug/L, 1,1-Dichloroethane ug/L, 1,1-Dichloroethene ug/L, 1,1-Dichloropropene ug/L,
1,2,3-Trichlorobenzene ug/L, 1,2,3-Trichloropropane ug/L, 1,2,4-Trichlorobenzene ug/L, 1,2,4-Trimethylbenzene ug/L, 1,2-Dibromo-3-chloropropane ug/L, 1,2-Dibromoethane ug/L, 1,2-Dichlorobenzene ug/L,
1,2-Dichloroethane ug/L, 1,2-Dichloropropane ug/L, 1,3,5-Trimethylbenzene ug/L, 1,3-Dichlorobenzene ug/L, 1,3-Dichloropropane ug/L, 1,4-Dichlorobenzene ug/L, 2,2-Dichloropropane ug/L, 2-Butanone ug/L,
2-Chlorotoluene ug/L, 4-Chlorotoluene ug/L, 4-Methyl-2-pentanone ug/L, Acetone ug/L, Acrolein ug/L, Acrylonitrile ug/L, Benzene ug/L, Bromobenzene ug/L, Bromodichloromethane ug/L, Bromoform ug/L, Bromomethane
ug/L, Carbon tetrachloride ug/L, Chlorobenzene ug/L, Chloroethane ug/L, Chloroform ug/L, Chloromethane ug/L, Dibromochloromethane ug/L, Dibromomethane ug/L, Dichlorodifluoromethane ug/L, Diisopropyl ether ug/L,
Ethylbenzene ug/L, Hexachlorobutadiene ug/L, Isopropylbenzene ug/L, Methyl tert butyl ether ug/L, Methylene chloride ug/L, Naphthalene ug/L, Styrene ug/L, Tetrachloroethene ug/L, Toluene ug/L, Trichloroethene ug/L,
Trichlorofluoromethane ug/L, Vinyl chloride ug/L, cis-1,2-Dichloroethene ug/L, m,p-Xylene ug/L, n-Butylbenzene ug/L, n-Propylbenzene ug/L, o-Xylene ug/L, p-Isopropyltoluene ug/L, sec-Butylbenzene ug/L,
tert-Butylbenzene ug/L, trans-1,2-Dichloroethene ug/L
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