MO-27965_47256_CA_LSA_20210621_Phase II LSA

June 21, 2021

Mr. Dan Bowser
NCDEQ-UST Section
610 East Center Avenue, Suite 301
Mooresville, North Carolina 28115

Re: Phase I-II LSA Report
Kwick Mart-Mint Hill
10308 Albemarle Road
Charlotte, Mecklenburg County, North Carolina
Facility ID No.: 00-0-034068
Incident Number: 47256

Dear Mr. Bowser:

Attached for your review is the Phase I-II LSA report for the above referenced site located in Charlotte,
North Carolina. If you require additional information, please contact the undersigned at [phone].

Sincerely,
Resolve Environmental Services, PLLC

Laura Minor
Operations Manager

cc: Brewer-Hendley Oil Company, Inc.
file

PHASE I-II LIMITED SITE ASSESSMENT REPORT
KWICK MART-MINT HILL
10308 ALBEMARLE ROAD
CHARLOTTE, MECKLENBURG COUNTY
NORTH CAROLINA
INCIDENT NUMBER 47256
FACILITY ID NUMBER 00-0-034068

Prepared for:

Mr. John Hendley
Brewer-Hendley Oil Company, Inc.
Post Office Box 769
Marshville, North Carolina 28103

Prepared by:

Resolve Environmental Services, PLLC
500 Devonport Drive
Matthews, North Carolina 28104

June 21, 2021

Laura Minor
Project Manager

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EXECUTIVE SUMMARY
The Kwick Mart-Mint Hill is an underground storage tank (UST) site located at 10308 Albemarle Road in
Charlotte, Mecklenburg County, North Carolina. A total of three (3) USTs (one 12,000-gallon gasoline
UST, one 8,000-gallon gasoline UST and one (1) 4,000-gallon kerosene UST) have existed at the property
since June 1994 to the present. The adjoining properties are commercial and residential.

A previous release at the site was reported on August 19, 2002, following a Site Check assessment. The
release was identified as NCDEQ Incident 24539. The USTs were owned and operated by Brewer-Hendley
Oil Company at the time of the release. A monitoring well was installed during LSA activities at the site
in December 2002. No detectable concentrations of target compounds were reported in the ground water
sample collected during the 2002 LSA. The incident was issued a no further action status on February 19,
2003.

During a routine compliance inspection conducted by the North Carolina Department of Environmental
Quality (NCDEQ) on August 27, 2019, the spill bucket at the 12,000-gallon regular gasoline UST was
noted to need repair/replacement. A NCDEQ Notice of Violation dated August 28, 2019 requesting a Site
Check was sent to Mr. John N. Hendley, Registered Agent, of Brewer-Hendley Oil Company, Inc. (BHOC)
of Marshville, North Carolina.

A soil sample was collected adjacent to the regular gasoline spill bucket on September 18, 2019. The
sample was submitted for analyses for gasoline-range organics (GRO) by Method 8015C. TPH-GRO was
not detected in the soil sample. Therefore, no further assessment was required.

In May 2020, Resolve was contracted to perform a Phase II Environmental Site Assessment (ESA) at the
site by BHOC. Four (4) temporary monitoring wells were installed at the site. Soil and ground water
samples were collected from each sampling point. No detectable concentrations of TPH-GRO or diesel-
range organics (DRO) were reported in the soil samples. A concentration of benzene that exceeded the
maximum allowable concentration (MAC) was reported in one of the ground water samples (TMW-4).
Based on the ground water quality violation, a UST-61 form dated September 10, 2020 was submitted to
the NCDEQ.

A Notice of Regulatory Requirements (NORR) dated September 15, 2020 was prepared by the NCDEQ
which requested Limited Site Assessment (LSA) activities. Resolve supervised the installation of one (1)

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Type II monitoring well (MW-1) on September 16, 2020 in the former location of Phase II ESA sampling
point TMW-4. The well was completed to a depth of 35 feet on September 18, 2020.

With the exception of an estimated concentration of acetone in soil sample MW-1-5’, no other requested
method constituents were reported in the collected soil samples.

Concentrations of benzene, MTBE, EDB and lead that exceeded the MACs were reported in the ground
water sample collected from MW-1. None of the concentrations exceeded the gross contamination levels
(GCLs) nor 10 times the 2L ground water quality standards. In addition, detectable and/or estimated
concentrations of other requested method constituents were reported in the ground water sample collected
from MW-1; however, none of the concentrations exceeded the MACs.

During the September 2020 receptor survey, a total of thirteen water supply wells (WSW-1 through WSW-
13) were identified within 1,500-feet of the source area. Four (4) potable wells (WSW-1, WSW-2, WSW-
5 and WSW-10) are located with 1,000 feet of the sources area. An additional potable well, WSW-13 is
located approximately 1,200 feet from the source area. The remaining identified ells are presumed to be
used for irrigation purposes only, since all of the corresponding properties are connected to municipal water.
County water is available to all properties in the surrounding area of the site.

No surface water body was identified with a 500-foot radius of the site. Azusa Grotto Lake is located
approximately 1,300 feet to the southwest of the site and an unnamed tributary of Clear Creek is located
approximately 1,300 feet east of the site. County water is available to all properties in the surrounding area
of the site.

Based on the receptor survey information and ground water quality data collected to date, the site meets the
criteria for a high-risk classification. It should be noted that the detectable concentrations of identified
compounds exceeding 2L and the distance to the nearest receptor (480 feet) make the potential for affecting
the receptor at or above the EPA’s MCL extremely low. In addition, the presence of MTBE indicates that
the release occurred prior to 2009.

Based on the high-risk classification, Phase II LSA activities, including the installation of two (2) additional
Type II monitoring wells (MW-2 and MW-3) were installed on April 7, 2021. MW-2 and MW-3 were
installed to 35 feel BGS. Please note that monitoring well MW-1A (installed during the 2002 LSA was

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located on the property and used during Phase II LSA activities, in lieu of the installation of proposed
monitoring well MW-4.

Concentrations of benzene, toluene, ethylbenzene, xylenes, naphthalene, EDB, 1,2-DCA, 2-Hexanone,
isopropylbenzene, MIBK, n-propylbenzene, 1,2,4-trimethylbenzene, 1,3,5-trimethylbenzene, C5-C8
aliphatics and C9-C10 aromatics that exceeded the MACs were reported in the ground water sample
collected from MW-3. A concentration of MTBE that exceeded the MAC was also reported in the ground
water sample collected from MW-2. The concentration of benzene in MW-3 also exceeded the GCL.
Detectable and/or estimated concentrations of other requested method constituents were reported in the
ground water samples collected from MW-1 through MW-3; however, none of the concentrations exceeded
the MACs.

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SITE INFORMATION
1. Site Identification:
Date of Report: June 21, 2021
Facility ID No. 00-0-034068
Incident Number: 42756
Site Name: Kwick Mart-Mint Hill
Site Street Address: 10308 Albemarle Road
City: Charlotte Zip Code: 28227 County: Mecklenburg
Description of Geographic Data Point: Calculated from top of the gasoline (regular) spill bucket
Location Method: Online lat/long finder
Latitude: 35.204020° N Longitude: 80.751270° W

2. Contacts Associated with Leaking UST System:

UST Owner: Brewer-Hendley Oil Company, Inc. (Table 1)
P.O. Box 769
Marshville, North Carolina 28103
[phone]

UST Operator: Kwick Mart Yohannes Inc. (Table 1)
10308 Albemarle Road
Charlotte, North Carolina 28227
[phone]

Property Owner: Hendley Family LLC
P.O. Box 769
Marshville, North Carolina 28103

Drilling Contractor: Geological Resources, Inc.
3502 Hayes Road
Monroe, North Carolina 28110
(704) 6845-4010
Primary Consultant: Resolve Environmental Services, PLLC
500 Devonport Drive
Matthews, North Carolina 28104
[phone]
Laboratory: SGS North America, Inc.
4405 Vineland Road, Suite C-15
Orlando, Florida 32811
[phone]
North Carolina Certification No. 573
3. Release Information
Date Discovered: The release was discovered during Phase II ESA activities conducted on
August 20, 2020
Estimated Quantity of Release: Undetermined
Cause of Release: Damaged spill bucket
Source of Release: 12,000-gallon gasoline UST

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UST Size and contents: (1) 12,000-gallon gasoline UST
(1) 8,000-gallon gasoline UST
(1) 4,000-gallon kerosene UST (Table 2)

Certification:

I, Terry D. Kennedy, a Licensed Geologist for Resolve Environmental Services, PLLC, do certify that the
information contained in this report is correct and accurate to the best of my knowledge.

Resolve Environmental Services, PLLC, is licensed to practice geology in North Carolina. The certification
number of the corporation is C-416.

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TABLE OF CONTENTS

1. RISK CHARACTERIZATION ....................................................................................... 1
2. RECEPTOR INFORMATION ........................................................................................ 3
3. SITE GEOLOGY AND HYDROGEOLOGY ................................................................ 5
4. SITE INVESTIGATION .................................................................................................. 5
5. CONCLUSIONS AND RECOMMENDATIONS .......................................................... 8
6. LIMITATIONS ................................................................................................................. 8

FIGURES
Figure 1: Site Location Map
Figure 2: Site Vicinity Map
Figure 3: Site Map
Figure 4: Ground Water Flow Direction Map
Figure 5: Ground Water Quality Map

TABLES

Table 1: UST Owner/Operator Information
Table 2: UST System Information
Table 3: Water Supply Well Owner Information
Table 4: Adjacent Property Owner Information
Table 5: Well Construction and Gauging Information
Table 6: Summary of Ground Water Sample Analytical Results

APPENDICES

Appendix A: Well Construction Records and Subsurface Logs
Appendix B: Laboratory Analytical Report

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1. RISK CHARACTERIZATION
Limited Site Assessment Risk Classification and Land Use Form
Part I – Groundwater/Surface Water/Vapor Impacts
High Risk
1. Has the release contaminated any water supply well including any well used for non-drinking
purposes? NO
2. Is a water supply well used for drinking water located within 1,000 feet of the source area of the
release? YES
3. Is a water supply well not used for drinking water (e.g., irrigation, washing cars, industrial cooling
water, filling swimming pools) located within 250 feet of the source area of the release?
NO
4. Does ground water within 500 feet of the source area of the release have the potential for future use
(there is no other source of water supply other than the groundwater)? NO
Potable wells are located within 100 feet of the source area. However, public water is available to
the site and surrounding properties.
5. Do vapors from the release pose a threat of explosion because of accumulation of the vapors in a
confined space or pose any other serious threat to public health, public safety or the environment?
NO
6. Are there any other factors that would cause the release to pose an imminent danger to public health,
public safety, or the environment? NO
If YES, explain:
Intermediate Risk
7. Is a surface water body located within 500 feet of the source area of the release? NO
No surface water bodies were identified within a 500-foot radius of the site.
If YES, does the maximum groundwater contaminant concentration exceed the surface water
quality standards and criteria found in 15A NCAC 2B .0200 by a factor of 10? NA
8. Is the source area of the release located within an approved or planned wellhead protection area as
defined in 42 USC 300h-7(e)? NO
9. Is the release located in the Coastal Plain physiographic region as designated on a map entitled
“Geology of North Carolina” published by the Department in 1985? NO
If YES, is the source area of the release located in an area in which there is recharge to an
unconfined or semi-confined deeper aquifer that is being used or may be used as a source of

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drinking water?
10. Do the levels of ground water contamination for any contaminant exceed the gross contamination
levels established by the Department? NO

Part II - Land Use
Property Containing Source Area of Release
The questions below pertain to the property containing the source area of the release.
1. Does the property contain one or more primary or secondary residences (permanent or temporary)?
NO
Explain: The subject property contains a petroleum retail facility/convenience store.
2. Does the property contain a school, daycare center, hospital, playground, park, recreation area,
church, nursing home, or other place of public assembly? NO
Explain: The subject property contains a petroleum retail facility.
3. Does the property contain a commercial (e.g., retail, warehouse, office/business space, etc.) or
industrial (e.g., manufacturing, utilities, industrial research and development, chemical/petroleum
bulk storage, etc.) enterprise, an inactive commercial or industrial enterprise, or is the land
undeveloped? YES
Explain: The subject property contains a petroleum retail facility/convenience store.
4. Do children visit the property? YES
Explain: The subject property contains a petroleum retail facility and children visit the property.
6. Is access to the property reliably restricted consistent with its use (e.g., by fences, security personnel
or both)? NO
Explain: The property is easily accessible to pedestrian and vehicular traffic.
7. Do pavement, buildings, or other structures cap the contaminated soil? YES
Explain: The UST basin and dispenser areas are capped with asphalt or concrete.
If yes, what mechanisms are in place or can be put into place to ensure that the contaminated soil
will remain capped in the foreseeable future?
The site use is expected to remain the same for the foreseeable future.
7. What is the zoning status of the property?
According to the City of Charlotte, the property is zoned General Business.

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8. Is the use of the property likely to change in the next 20 years? NO
Explain:

Property Surrounding Source Area of Release
The questions below pertain to the area within 1,500 feet of the source area of the release (excludes
property containing source area of the release):
9. What is the distance from the source area of the release to the nearest primary or secondary
residence (permanent or temporary)?
A mobile home park is located on the adjacent property to the east with the closest trailer being
approximately 325’ east/southeast from the source area.
11. What is the distance from the source area of the release to the nearest school, daycare center,
hospital, playground, park, recreation area, church, nursing home or other place of public
assembly?
Wilson Grove Baptist Church is located approximately 960 feet south of the source area.
12. What is the zoning status of properties in the surrounding area?
According to the City of Charlotte, the area surrounding the site to the east, west and south is zoned
Business and the area to the north is zoned Industrial.
13. Briefly characterize the use and activities of the land in the surrounding area.
Used auto lots are located across Wilgrove Mint Hill Road to the west and across Albemarle Road,
north of the site. A medical office and mobile home park is located to the south and west of the
site, respectively.

2. RECEPTOR INFORMATION
1. Water Supply Wells:
Thirteen (13) water supply wells (WSW-1 through WSW-13) were identified within a 1,500-foot
radius of the subject site. Four potable water supply wells (WSW-1, WSW-2, WSW-5 and WSW-

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10) were identified within 1,000 feet of the source area. Potable well, WSW-13, was identified
within 1,200 feet of the source area. The remaining identified wells are presumed to be used for
irrigation purposes only, since the corresponding properties are connected to municipal water. A
site location map is provided as Figure 1 and a Site Vicinity Map showing property boundaries for
the site and surrounding properties have been included as Figure 2. Water supply well owner
information is summarized in Table 3. Water supply well usage questionnaires dated October 22,
2020 were mailed to all property owners located within 500-feet of the source area. The
questionnaires will be forwarded to the NCDEQ incident manager upon receipt. Please note that
addresses tied to each parcel that a water supply well was identified to be present were verified of
either having active water accounts with the City of Charlotte or alternatively, not possessing active
water accounts with the City of Charlotte by Resolve personnel on October 27, 2020.
2. Public Water Supplies:
Are public water supplies available within 1,500 feet of the source area of the release? YES
If yes, where is the location of the nearest public water lines and the source(s) of the public water
supply. Explain:
Municipal water is available to the site and the surrounding properties. Water lines run parallel to
Albemarle Road and Wilgrove Mint Hill Road, north and west of the onsite structure, respectively.
3. Surface Water:
Identify all surface water bodies (e.g., ditch, pond, stream, lake, river) within 1,500 feet of the
source area of the release. This information must be shown on the USGS topographic map.
Azusa Grotto Lake is located approximately 1,300 feet southwest of the source area. An unnamed
tributary of Clear Creek is located approximately 1,300 feet east of the source area.
4. Wellhead Protection Areas:
Identify all planned or approved wellhead protection areas in the vicinity of the source area. This
information must be shown on the USGS topographic map. Wellhead protection areas are defined
in 42 USC 300h-7(e).
On October 24, 2020, Resolve personnel accessed the North Carolina Department of
Environmental Quality (NCDEQ) Source Water Assessment and Protection (SWAP) Program’s
website to identify wellhead protection areas in the vicinity of the subject site. There were no
designated wellhead protection areas near the subject site.

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5. Deep Aquifers in the Coastal Plain Physiographic Region:
The site is not located in the Coastal Plan Physiographic Region.
6. Subsurface Structures:
No structures with basements were observed in the vicinity of the source area. Utilities in the area
do not appear to intersect the seasonal high water table.
7. Property Owners and Occupants:
The names and addresses of the owners of properties adjacent to the site are presented in Table 4.
Property boundaries are shown on Figure 2.
3. SITE GEOLOGY AND HYDROGEOLOGY
According to the 1985 Geologic Map of North Carolina, the site is located in the Charlotte Belt of
metamorphic rocks. The underlying rock consists of interbedded felsic to mafic tuffs and flowrock. Ground
water in the area moves through fractures and cleavage planes within the metamorphic rock.

Red clayey silt was encountered during the borehole drilling for MW-2 and MW-3. Water was encountered
during the installation of MW-2 and MW-3 at a depth of approximately 20 feet and the wells were set to
total depths of 35 feet BGS with a 20-foot section of screen. Copies of the well construction records and
subsurface logs have been included as Appendix A. A Site Map is included as Figure 3. Well construction
and gauging information is presented in Table 5.

4. SITE INVESTIGATION
A previous release at the site was reported on August 19, 2002, following a Site Check assessment. The
release was identified as NCDEQ Incident 24539. The USTs were owned and operated by Brewer-Hendley
Oil Company at the time of the release. A monitoring well was installed during LSA activities at the site
in December 2002. No detectable concentrations of target compounds were reported in the ground water
sample collected during the 2002 LS. The incident was issued a no further action status on February 19,
2003.
Following the identification of a faulty spill bucket at the 12,000-gallon gasoline tank during a routine
compliance inspection conducted by NCDEQ on August 27, 2019, Resolve conducted site check activities
in September 2019. A soil sample was collected near the 12,000-gallon gasoline spill bucket on September
18, 2019. TPH-GRO was not detected in the soil sample. Per BHOC’s request, Resolve conducted a Phase
II ESA at the site in May 2020. Four (4) temporary monitoring wells (TMW-1 through TMW-4) were
installed at the site on August 20, 2020. Soil and ground water samples were collected from each sampling

6

point. No detectable concentrations of TPH-GRO or TPH-DRO were reported in the soil samples. A
concentration of benzene that exceeded the MAC was reported in one of the ground water samples (TMW-
4). Based on the ground water quality violation, a UST-61 form dated September 10, 2020 was submitted
to the NCDEQ.

A Notice of Regulatory Requirements (NORR) dated September 15, 2020 was prepared by the NCDEQ
which requested Limited Site Assessment (LSA) activities. Resolve supervised the installation of one (1)
Type II monitoring well (MW-1) beginning on September 16, 2020. MW-1 was initially installed to a total
depth of 25 feet and completed with a 10-foot screened interval set to bracket the water table at the time of
installation. However, due to lack of water, MW-1 was re-installed on September 18, 2020 to a total depth
of 35 feet and completed with a 20-foot screened interval set to bracket the water table. MW-1 was installed
in the former location of the Phase II ESA sampling point, TMW-4. Based on ground water quality
violations detected in MW-1, Phase II LSA activities commenced at the site in April 2021. Two additional
monitoring wells (MW-2 and MW-3) were installed at the site on April 7, 2021 to total depths of 35 feet
BGS and completed with 20-foot screened intervals. Previously installed monitoring well from the 2002
LSA currently identified as MW-1A was sampled and surveyed during Phase II LSA activities. According
to the well tag, MW-1A was installed in 2002 to a total depth of 40 feet BGS and completed with a 20-foot
screened interval. The depths to water in MW-1, MW-2, MW-3 and MW-1A were 21.72 feet, 21.33 feet,
21.44 feet and 19.28 feet, respectively. Ground water elevations ranged from 78.24 feet to 79.66 feet in
April 2021. Based on that, ground water flow direction is to the north/northwest. A Ground Water Flow
Direction Map is included as Figure 4.

1. Soil Sampling:
On September 16, 2020, three (3) soil samples (MW-1-5’, MW-1-10’ and MW-1-15’) were collected
during the initial installation of monitoring well MW-1 on September 16, 2020. The soil samples were
submitted for laboratory analyses of volatile organic compounds (VOCs) by SW846 Method 8260B
and for volatile petroleum hydrocarbons (VPH) using the MADEP Method.

With the exception of an estimated concentration of acetone in MW-1-5’, no other detectable
concentrations of requested method constituents were reported in the soil samples. The concentration
of acetone did not exceed the soil-to-ground water maximum contaminant concentration (MCC). No
additional soil samples were collected during Phase II LSA activities.

7

2. Ground Water Sampling:
On September 22, 2020, a ground water sample was collected from MW-1 and submitted for laboratory
analyses of VOCs by EPA Method 6200B, VPH/EPH by the MADEP Method, EDB by Method 504.1,
625 BNAs + 10 tics and lead. Concentrations of benzene, MTBE, EDB and lead that exceeded the
MACs were reported in the ground water sample collected from MW-1. None of the concentrations
exceeded the GCLs. In addition, detectable and/or estimated concentrations of other requested method
constituents were reported in the ground water sample collected from MW-1; however, none of the
concentrations exceeded the MACs nor 10 times the 2L ground water quality standards.

On April 8, 2021, ground water samples were collected from MW-1 through MW-3 and MW-1A and
submitted for laboratory analyses of VOCs by EPA Method 6200B, VPH by the MADEP Method, EDB
by Method 504.1 and lead.

Concentrations of benzene, toluene, ethylbenzene, xylenes, naphthalene, EDB, 1,2-DCA, 2-Hexanone,
isopropylbenzene, MIBK, n-propylbenzene, 1,2,4-trimethylbenzene, 1,3,5-trimethylbenzene, C5-C8
aliphatics and C9-C10 aromatics that exceeded the MACs were reported in the ground water sample
collected from MW-3. A concentration of MTBE that exceeded the MAC was also reported in the
ground water sample collected from MW-2. The concentration of benzene in MW-3 also exceeded the
GCL. Detectable and/or estimated concentrations of other requested method constituents were
reported in the ground water samples collected from MW-1 through MW-3; however, none of the
concentrations exceeded the MACs. A summary of ground water sample analytical results is presented
in Table 6. A Ground Water Quality Map is included as Figure 5. A copy of the laboratory analytical
report is presented as Appendix B.

3. Quality Control:
The soil and ground water samples were immediately placed in laboratory-supplied containers, which
were then placed in iced coolers. New disposable bailers were used to sample the monitoring well and
new nitrile gloves were worn during soil and ground water sampling. Samples were logged using
proper chain-of-custody procedures. The samples were transported to a North Carolina certified
laboratory for analysis.

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5. CONCLUSIONS AND RECOMMENDATIONS
 The site contains a petroleum retail facility/convenience store. Land use in the area primarily
consists of commercial properties mixed with residential properties.
 During the September 2020 receptor survey, a total of thirteen (13) water supply wells (WSW-1
through WSW-13) were identified within 1,500-feet of the source area. One (1) potable well
(WSW-1) is located approximately 480 feet of the release. Four (4) additional potable wells
(WSW-2, WSW-5, WSW-10 and WSW-13) were identified between 700 feet and 1,200 feet from
the source area. The remaining wells are presumed to be used for irrigation purposes only. County
water is available to all properties in the surrounding area of the site.
 Azusa Grotto Lake is located approximately 1,300 feet southwest of the source area. A stream is
located approximately 1,300 feet east of the source area. Underground utilities in the source areas
are not likely to intersect the water table.
 An estimated concentration of acetone was reported in soil sample MW-1-5’ collected at the site in
September 2020; however, the concentration did not exceed the MCC. Concentrations of benzene,
MTBE, EDB and lead that exceeded the MAC were reported in the ground water sample collected
from MW-1 in September 2020. None of the concentrations exceeded the GCLs.
 Two additional Type II monitoring wells (MW-2 and MW-3) were installed at the site April 7,
2021. One existing monitoring well, labeled MW-1A was identified and utilized during Phase II
LSA activities. Ground water elevations ranged from 78.24 feet to 79.66 feet in April 2021. Based
on that, ground water flow direction is to the north/northwest.
 Based on the April 2021 ground water sampling event, concentrations of benzene, toluene,
ethylbenzene, xylenes, naphthalene, EDB, 1,2-DCA, 2-Hexanone, isopropylbenzene, MIBK, n-
propylbenzene, 1,2,4-trimethylbenzene, 1,3,5-trimethylbenzene, C5-C8 aliphatics and C9-C10
aromatics that exceeded the MACs were reported in the ground water sample collected from MW-
3. A concentration of MTBE that exceeded the MAC was also reported in the ground water sample
collected from MW-2. The concentration of benzene in MW-3 also exceeded the GCL.
 Based on this information, the site risk should be classified as high risk. The presence of MTBE
and EDB indicates that the release occurred prior to 2009. A CSA should be conducted at the site.
6. LIMITATIONS
This report has been prepared for the exclusive use of Mr. John Hendley and Brewer-Hendley Oil Company,
Inc. for specific application to the referenced site in Mecklenburg County, North Carolina. The assessment
was conducted based on the scope of work and level of effort specified by NCDEQ and with resources

9

adequate only for that scope of work. Our findings have been developed in accordance with generally
accepted standards of geology and hydrogeology practices in the State of North Carolina, available
information and our professional judgment. No other warranty is expressed or implied.

The data that are presented in this report are indicative of conditions that existed at the precise locations
sampled and at the time the samples were collected. In addition, the data obtained from samples would be
interpreted as being meaningful with respect to parameters indicated in the laboratory report. No additional
information can logically be inferred from these data.

FIGURES
SITE LOCATIONFigure 1 Site LocationKwick Mart- Mint Hill10308 Albemarle Road Mint Hill, Mecklenburg County, NC Incident No. 47256Resolve Project No. 5209500 M2000 FTDate: 09/12/2020Location: 35.208904° N -80.669633 ° W Dad
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Sunway Dr Guice Crossing LnDoblinway DrFIGURE 2: SITE VICINITY MAPKWICK MART-MINT HILL10308 ALBEMARLE ROADCHARLOTTE, MECKLENBURG COUNTYNORTH CAROLINAINCIDENT NO. 42756
PREPARED BY:RESOLVE ENVIRONMENTAL SERVICES, PLLCSEPTEMBER 11, 2020
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LEGEND
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Well Owners and Adjacent Properties
Mecklenburg County, NC Parcels
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reekAZUSAGROTTO LAKE
RESOLVEENVIRONMENTALSERVICES, PLLCKWICK MART - MINT HILL10308 ALBERMARLE ROADMINT HILL, MECKLENBURG COUNTY, NCINCIDENT NO: 47256RESOLVE PROJECT NO. 5209FIGURE 3SITE MAP
RESOLVEENVIRONMENTALSERVICES, PLLCKWICK MART - MINT HILL10308 ALBERMARLE ROADMINT HILL, MECKLENBURG COUNTY, NCINCIDENT NO: 47256RESOLVE PROJECT NO. 5209FIGURE 4GROUND WATER FLOW DIRECTION MAP
RESOLVEENVIRONMENTALSERVICES, PLLCKWICK MART - MINT HILL10308 ALBERMARLE ROADMINT HILL, MECKLENBURG COUNTY, NCINCIDENT NO: 47256RESOLVE PROJECT NO. 5209FIGURE 5GROUND WATER QUALITY MAP (4/8/21)

TABLES
UST ID Number 1 - 3 Facility ID Number
Owner or Operator?
Owner/Operator
NA NA
Name of Owner or Operator Dates of Ownership / Operation
TABLE 1
UST OWNER/OPERATOR INFORMATION
KWICK MART - MINT HILL
00-0-00000034068
Brewer Hendley Oil Company 6/1/1994
Address Telephone Number
P.O. Box 769, Marshville, NC 28103 704.233.2600
INCIDENT NO. 47256
Page 1 of 1
Was Release
Associated
with UST
System?
(Yes / No)
1 Gasoline Gasoline 8,000 06/01/94 Single wall FRP 8' x 21' 4"Single wall FRP Current No
2 Gasoline Gasoline 12,000 06/01/94 Single wall FRP 8' x 32'Single wall FRP Current Yes
4 Kerosene Kerosene 4,000 06/01/94 Single wall FRP 64" x 24'Single wall FRP Current No
Notes:
• Data obtained from the NCDEQ registered tank database.
• FRP: Fiberglass Reinforced Plastic.
Construction
Details
Tank
Dimensions
Description of
Associated
Product Piping
and
Pumps
Status
of
UST
TABLE 2
UST SYSTEM INFORMATION
KWICK MART - MINT HILL
Date: 9/28/2020 Facility ID 0-00-0000034068
UST
ID
No.
Current
or Most
Recent
Contents
Previous
Contents
Capacity
(gallons)
Date
Installed
INCIDENT NO. 47256
Page 1 of 1
Date 9/28/2020 Facility ID 00-0-0000034068
Well #Parcel ID
Number Well Owner Well Location (Addresses
Tied to Parcel)Phone Number Well Use Well Depth
(ft BGS)
Well Casing
Depth
(ft BGS)
Well Screen
Interval
(x to y ft BGS)
Distance from
source area of
release (ft.) and
direction
WSW-1 11116407 Terry J Wilson 10417 Albemarle Road Unknown
Potable
(No active City
of CLT water
account)
Unknown Unknown Unknown 480 NE
WSW-2 11116421 Steve R & Evelyn S
Berrier
10522 Parkton Rd &
10510 Parkton Rd Unknown
Potable
(10522: no
active City of
CLT water
account;
10510: active
City of CLT
water account)
Unknown Unknown Unknown 700 NE
WSW-3 11116211
Yohannes Tzeggai &
Teclemariam
Letehawariat
10335 Parkton Rd Unknown
Irrigation
(active City of
CLT water
account)
Unknown Unknown Unknown 600 N/NE
WSW-4 11116210 Maria M & Ioannis
Fourtounis 10311 Parkton Rd Unknown
Irrigation
(active City of
CLT water
account)
Unknown Unknown Unknown 575 N
WSW-5 11116208 Joanne A & TR Craft 10303 Parkton Rd Unknown
Potable
(No active City
of CLT water
account)
Unknown Unknown Unknown 680 NW
WSW-6 10940208 Gene Eric Privette 6719 Huntley Rd Unknown
Irrigation
(active City of
CLT water
account)
Unknown Unknown Unknown 650 SW
WSW-7 10940209 Meldona T Gladden 6725 Huntley Rd Unknown
Irrigation
(active City of
CLT water
account)
Unknown Unknown Unknown 635 SW
9820 Thornridge Dr
Indian Trail NC 28079
TABLE 3
WATER SUPPLY WELL OWNER INFORMATION
KWICK MART - MINT HILL
INCIDENT NO. 47256
Mailing Address
8513 Rolling Fields Rd
Charlotte NC 28227
Wells Within 500'
Wells Within 1,000'
2022 Tanfield Dr
Matthews NC 28104
4716 Dawnwood Dr
Charlotte NC 28212
6023 Wilgrove Mint Hill
Rd
Charlotte NC 28227
7017 Indian Trail Fairview
Rd
Indian Trail NC 28079
6416 Oak Hill Rd
Charlotte NC 28227
Date 9/28/2020 Facility ID 00-0-0000034068
Well #Parcel ID
Number Well Owner Well Location (Addresses
Tied to Parcel)Phone Number Well Use Well Depth
(ft BGS)
Well Casing
Depth
(ft BGS)
Well Screen
Interval
(x to y ft BGS)
Distance from
source area of
release (ft.) and
direction
TABLE 3
WATER SUPPLY WELL OWNER INFORMATION
KWICK MART - MINT HILL
INCIDENT NO. 47256
Mailing Address
WSW-8 10940210 Joyce M & William Lee
Gladden 6811 Huntley Rd Unknown
Irrigation
(active City of
CLT water
account)
Unknown Unknown Unknown 775 S/SW
WSW-9 10940106 William Lee Gladden 6814 Huntley Rd Unknown
Irrigation
(active City of
CLT water
account)
Unknown Unknown Unknown 900 SW
WSW-10 13707612
Ted Douglas Harkey
&
Marcia Mauney
6708 Wilgrove Mint Hill
Rd Unknown
Potable
(No active City
of CLT water
account)
Unknown Unknown Unknown 750 S
WSW-11 13707613 Wilson Grove Baptist
Church
6700 Wilgrove Mint Hill
Rd Unknown
Irrigation
(active City of
CLT water
account)
Unknown Unknown Unknown 875 S/SE
WSW-12 10940104 Joyce M & William Lee
Gladden 6822 Huntley Rd Unknown
Irrigation
(active City of
CLT water
account)
Unknown Unknown Unknown 1,080 SW
WSW-13 10940103 Joyce M & William
Lee Gladden
7731 Wilgrove Mint Hill
Rd Unknown
Potable: No
active City of
CLT water
account)
Unknown Unknown Unknown 1,200 SW
Notes: 1. Owner information current as of 9/28/2020 and obtained via Mecklenburg County NC GIS website: http://polaris3g.mecklenburgcountync.gov/.
2. City of Charlotte water department information current as of October 27, 2020.
6811 Huntley Rd
Charlotte NC 28227
6811 Huntley Rd
Charlotte NC 28227
Wells Within 1,500'
6811 Huntley Rd
Charlotte NC 28227
6811 Huntley Rd
Charlotte NC 28227
11055 Flowes Store Rd
Midland NC 28107
6624 Wilgrove Mint Hill
Rd
Charlotte NC 28227
Date: 9/28/2020 Facility ID 00-0-0000034068
13707605 (Site) & 13707637 Hendley Family LLC P.O. Box 769
Marshville NC 28103
10940201 Letha Joanne Craft &
Billy Edward Arant
6023 Wilgrove Mint Hill Rd.
Charlotte NC 28227
11116406A Robert S Furr Jr.P.O. Box 5647
Charlotte NC 28299
137070604 L&K Leasing LLC 6824 Wilgrove Mint Hill Rd.
Charlotte NC 28227
Note:
• Property information current as of September 28, 2020. Information obtained from
Mecklenburg County NC GIS website: https://polaris3g.mecklenburgcountync.gov/.
TABLE 4
ADJACENT PROPERTY OWNER INFORMATION
KWICK MART - MINT HILL
INCIDENT NO. 47256
Parcel ID Number Property Owner Property Owner Address
Date:6/17/21 Facility ID #: 00-0-0000034068
9/18/2020 21.05 NA 78.95
4/8/2021 21.72 NA 78.28
MW-2 4/7/2021 4/8/2021 15 15-35 35 99.68 21.33 NA 78.35
MW-3 4/7/2021 4/8/2021 15 15-35 35 99.68 21.44 NA 78.24
MW-1A 11/2002 4/8/2021 20 20-40 40 98.94 19.28 NA 79.66
Notes:
• ft BGS : feet below ground surface.
• NA: Not appicable.
• NM: Not measured.
TABLE 5
WELL CONSTRUCTION AND GAUGING INFORMATION
KWICK MART - MINT HILL
INCIDENT NO. 47256
Well ID Date Installed
(mm/dd/yy)
Date Water Level
Measured
(mm/dd/yy)
Well
Casing
Depth
(ft. BGS)
Screened
Interval
(x to y ft.
BGS)
Bottom
of Well
(ft. BGS)
Top of
Casing
Elevation
(ft.)
Depth to Water
from Top of
Casing
(ft.)
Free Product
Thickness
(ft.)
Groundwater
Elevation
(ft.)
Comments
100.00MW-1 9/18/2020 15 15-35 35
Date: 06/17/21
EPA 504.1 SW846
6010D
Well ID
Date
Collected
(mm/dd/yy)
1 600 600 500 20 6 0.02 0.4 40 70 100 70 400 400 0.02 15 400 200
5,000 260,000 84,500 85,500 20,000 6,000 50 400 40,000 25,000 100,000 30,000 28,500 25,000 50 15,000 NE NE
09/22/20 8.8 <0.13 <0.13 0.91 41.5 1.8 <0.13 <0.13 NR 0.23 J NR <0.13 1.3 <0.13 0.10 137 <35 <35
04/08/21 <0.13 <0.13 0.15 J <0.25 2.4 0.18 J <0.13 <0.13 <1.0 <0.13 3.3 <0.13 <0.13 <0.13 <0.0038 <5.0 <35 <35
MW-1A 04/08/21 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <1.3 <0.13 <0.13 <0.13 <0.0037 <5.0 <35 <35
MW-2 04/08/21 <0.31 <0.31 <0.31 <0.63 80.5 <0.31 <0.31 <0.31 <2.5 <0.31 <3.1 <0.31 <0.31 <0.31 <0.0038 <5.0 <35 <35
MW-3 04/08/21 7,380 11,600 1,710 8,380 <31 243 49.5 J 267 822 J 148 404 J 208 1,550 410 0.53 <5.0 12,400 12,000
Notes:
• Results reported in micrograms per liter (µg/l).
• < : Less than the method detection limit specified in the laboratory report.
• 2L Standard specified in T15A NCAC 2L.0202.
• GCL: Gross contamination level.
• NE: Not Established
• Concentrations in bold face type exceeded the 2L standards.
• Concentrations in bold face type and italics exceeded the gross contamination levels.
• Refer to laboratory report for detected constituents that did not exceed the MACs, or for which no standard has been established.
• NR: Compound not requested.
• J: Estimated concentration.
TABLE 6
SUMMARY OF GROUND WATER SAMPLE ANALYTICAL RESULTS
KWICK MART - MINT HILL
INCIDENT NO: 47526
Facility ID: 00-0-0000034068
Analytical Method SM 6200B MADEP VPH REV 2.1
Contaminant of Concern
BenzeneTolueneEthylbenzeneTotal XylenesMethyl-tert-butyl ether(MTBE)Naphthalene1,2-Dibromoethane(EDB)LeadC5-C8 AliphaticsC9-C10 Aromatics1,2-Dibromoethane(EDB)1,2-DichloroethaneGCL (µg/l)
MW-1 1,2,4-Trimethylbenzene1,3,5-Trimethylbenzene2-HexanoneIsopropylbenzeneMethyl isobutyl ketone (MIBK)n-Propylbenzene2L Standard (µg/l)
Page 1 of 1

APPENDICES

APPENDIX A
Well Construction Records and Subsurface Logs
Resolve Environmental Services, PLLC Phone:[phone]
500 Devonport Drive
Matthews, NC 28104
SUBSURFACE LOG
Project Kwick Mart - Mint Hill
Address 10308 Albemarle Road, Charlotte
Boring Number MW-2 Date Drilled
Sample Method Grab Drilling Method Auger
Completion Details Well completed with 20 feet of screen set to bracket the water table.
Driller S. Bowers Log By Ball
Lab Sample OVA
Depth Sample Interval(ft)ppm LITHOLOGY/COMMENTS
0 0-0.5' Asphalt
0.5'-35'Red clayey SILT
2
4
6
8
10

12
14
16

18
20
22

24
26
28

30
32
34
TD 35'
36
38

40
04/07/21
Resolve Environmental Services, PLLC Phone:[phone]
500 Devonport Drive
Matthews, NC 28104
SUBSURFACE LOG
Project Kwick Mart - Mint Hill
Address 10308 Albemarle Road, Charlotte
Boring Number MW-3 Date Drilled
Sample Method Grab Drilling Method Auger
Completion Details Well completed with 20 feet of screen set to bracket the water table.
Driller S. Bowers Log By WSB
Lab Sample OVA
Depth Sample Interval(ft)ppm LITHOLOGY/COMMENTS
0 0-0.5'Asphalt
0.5'-3.5'Argillite and brown clayey SILT
2
3.5'-8'Dark brown clayey SILT
4
6
8 8'-35'Red clayey SILT; petroleum odor
10

12
14
16

18
20
22

24
26
28

30
32
34
TD 35'
36
38

40
04/07/21

APPENDIX B
Laboratory Analytical Report
04/21/21
Technical Report for
Resolve Environmental
Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
SGS Job Number: FA84556
Sampling Date: 04/08/21
Report to:
Resolve Environmental
500 Devonport Dr
Matthews, NC 28104
[e-mail]
ATTN: Laura Minor
Total number of pages in report:
Certifications: FL(E83510), LA(03051), KS(E-10327), IL(200063), NC(573), NJ(FL002), NY(12022), SC(96038001)
DoD ELAP(ANAB L2229), AZ(AZ0806), CA(2937), TX(T104704404), PA(68-03573), VA(460177),
AK, AR, IA, KY, MA, MS, ND, NH, NV, OK, OR, UT, WA, WV
This report shall not be reproduced, except in its entirety, without the written approval of SGS.
Test results relate only to samples analyzed.
SGS North America Inc. • 4405 Vineland Road • Suite C-15 • Orlando, FL 32811 • tel: [phone] • fax: [phone]
Test results contained within this data package meet the requirements
of the National Environmental Laboratory Accreditation Program
and/or state specific certification programs as applicable.
Client Service contact: Muna Mohammed 407-425-6700
Norm Farmer
Technical Director
Orlando, FL 04/21/21
e-Hardcopy 2.0
Automated Report
81
SGS is the sole authority for authorizing edits or modifications to this document.
Unauthorized modification of this report is strictly prohibited.
Review standard terms at: http://www.sgs.com/en/terms-and-conditions
The results set forth herein are provided by SGS North America Inc.
Please share your ideas about
how we can serve you better at:
[e-mail]
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FA84556
Table of Contents
-1-
Sections:
Section 1: Sample Summary ...................................................................................................3
Section 2: Summary of Hits ....................................................................................................4
Section 3: Sample Results ........................................................................................................6
3.1: FA84556-1: MW-1A .....................................................................................................7
3.2: FA84556-2: MW-1 ........................................................................................................13
3.3: FA84556-3: MW-2 ........................................................................................................19
3.4: FA84556-4: MW-3 ........................................................................................................25
Section 4: Misc. Forms ............................................................................................................30
4.1: Chain of Custody ...........................................................................................................31
Section 5: MS Volatiles - QC Data Summaries .....................................................................33
5.1: Method Blank Summary ................................................................................................34
5.2: Blank Spike Summary ...................................................................................................43
5.3: Matrix Spike/Matrix Spike Duplicate Summary ...........................................................52
Section 6: GC Volatiles - QC Data Summaries .....................................................................61
6.1: Method Blank Summary ................................................................................................62
6.2: Blank Spike/Blank Spike Duplicate Summary ..............................................................63
6.3: Matrix Spike Summary ..................................................................................................64
6.4: Duplicate Summary .......................................................................................................65
Section 7: Metals Analysis - QC Data Summaries ................................................................66
7.1: Prep QC MP38791: Pb ..................................................................................................67
Section 8: Misc. Forms (SGS Scott, LA) ................................................................................73
8.1: Chain of Custody ...........................................................................................................74
Section 9: GC Volatiles - QC Data (SGS Scott, LA) .............................................................77
9.1: Method Blank Summary ................................................................................................78
9.2: Blank Spike/Blank Spike Duplicate Summary ..............................................................80 1234567892 of 81
FA84556
SGS North America Inc.
Sample Summary
Resolve Environmental
Job No:FA84556
Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample Collected Matrix Client
Number Date Time By Received Code Type Sample ID
This report contains results reported as ND = Not detected. The following applies:
Organics ND = Not detected above the MDL
FA84556-1 04/08/21 07:56 SB 04/09/21 AQ Ground Water MW-1A
FA84556-2 04/08/21 08:20 SB 04/09/21 AQ Ground Water MW-1
FA84556-3 04/08/21 08:08 SB 04/09/21 AQ Ground Water MW-2
FA84556-4 04/08/21 07:42 SB 04/09/21 AQ Ground Water MW-3
3 of 81
FA845561
Summary of Hits Page 1 of 2
Job Number:FA84556
Account:Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Collected:04/08/21
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FA84556-1 MW-1A
Methyl Tert Butyl Ether 1.2 J 2.0 1.0 ug/l MADEP VPH REV 2.1
FA84556-2 MW-1
Acetone 8.2 J 10 2.0 ug/l SM 6200B
2-Butanone (MEK)1.6 J 2.5 1.3 ug/l SM 6200B
Ethylbenzene 0.15 J 0.50 0.13 ug/l SM 6200B
4-Methyl-2-pentanone (MIBK)3.3 2.5 1.3 ug/l SM 6200B
Methyl Tert Butyl Ether 2.4 0.50 0.13 ug/l SM 6200B
Naphthalene 0.18 J 0.50 0.13 ug/l SM 6200B
Methyl Tert Butyl Ether 2.1 2.0 1.0 ug/l MADEP VPH REV 2.1
FA84556-3 MW-2
Chloroform 1.2 J 1.3 0.31 ug/l SM 6200B
Methyl Tert Butyl Ether 80.5 1.3 0.31 ug/l SM 6200B
Methyl Tert Butyl Ether 104 2.0 1.0 ug/l MADEP VPH REV 2.1
C5- C8 Aliphatics (Unadj.)53.5 J 100 35 ug/l MADEP VPH REV 2.1
FA84556-4 MW-3
Benzene 7380 130 31 ug/l SM 6200B
1,2-Dibromoethane 49.5 J 130 31 ug/l SM 6200B
1,2-Dichloroethane 267 130 31 ug/l SM 6200B
Ethylbenzene 1710 130 31 ug/l SM 6200B
2-Hexanone 822 J 1300 250 ug/l SM 6200B
Isopropylbenzene 148 130 31 ug/l SM 6200B
4-Methyl-2-pentanone (MIBK)404 J 630 310 ug/l SM 6200B
Naphthalene 243 130 31 ug/l SM 6200B
n-Propylbenzene 208 130 31 ug/l SM 6200B
Toluene 11600 130 31 ug/l SM 6200B
1,2,4-Trimethylbenzene 1550 130 31 ug/l SM 6200B
1,3,5-Trimethylbenzene 410 130 31 ug/l SM 6200B
m,p-Xylene 6190 250 31 ug/l SM 6200B
o-Xylene 2190 130 31 ug/l SM 6200B
Xylene (total)8380 380 63 ug/l SM 6200B
1,2-Dibromoethane a 0.53 0.020 0.0038 ug/l EPA 504.1
Benzene 6860 50 50 ug/l MADEP VPH REV 2.1
Ethylbenzene 1590 100 50 ug/l MADEP VPH REV 2.1
Methyl Tert Butyl Ether 148 100 50 ug/l MADEP VPH REV 2.1
Naphthalene 265 250 150 ug/l MADEP VPH REV 2.1
Toluene 10400 100 50 ug/l MADEP VPH REV 2.1
m,p-Xylene 5830 200 100 ug/l MADEP VPH REV 2.1
4 of 81
FA845562
Summary of Hits Page 2 of 2
Job Number:FA84556
Account:Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Collected:04/08/21
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
o-Xylene 2210 100 50 ug/l MADEP VPH REV 2.1
C5- C8 Aliphatics (Unadj.)29800 5000 1800 ug/l MADEP VPH REV 2.1
C9- C12 Aliphatics (Unadj.)3800 J 5000 1800 ug/l MADEP VPH REV 2.1
C9- C10 Aromatics (Unadj.)12000 5000 1800 ug/l MADEP VPH REV 2.1
C5- C8 Aliphatics 12400 5000 1800 ug/l MADEP VPH REV 2.1
C9- C10 Aromatics 12000 5000 1800 ug/l MADEP VPH REV 2.1
(a) Analysis performed at SGS Scott, LA.
5 of 81
FA845562
SGS North America Inc.
Sample Results
Report of Analysis
Orlando, FL
Section 3
6 of 81
FA845563
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-1A
Lab Sample ID:FA84556-1 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0225871.D 1 04/14/21 22:22 LR n/a n/a VA2878
Run #2
Purge Volume
Run #1 10.0 ml
Run #2
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone ND 10 2.0 ug/l
71-43-2 Benzene ND 0.50 0.13 ug/l
108-86-1 Bromobenzene ND 0.50 0.13 ug/l
74-97-5 Bromochloromethane ND 0.50 0.13 ug/l
75-27-4 Bromodichloromethane ND 0.50 0.13 ug/l
75-25-2 Bromoform ND 0.50 0.13 ug/l
78-93-3 2-Butanone (MEK)ND 2.5 1.3 ug/l
104-51-8 n-Butylbenzene ND 0.50 0.13 ug/l
135-98-8 sec-Butylbenzene ND 0.50 0.13 ug/l
98-06-6 tert-Butylbenzene ND 0.50 0.13 ug/l
56-23-5 Carbon Tetrachloride ND 0.50 0.13 ug/l
108-90-7 Chlorobenzene ND 0.50 0.13 ug/l
75-00-3 Chloroethane ND 0.50 0.20 ug/l
67-66-3 Chloroform ND 0.50 0.13 ug/l
95-49-8 o-Chlorotoluene ND 0.50 0.13 ug/l
106-43-4 p-Chlorotoluene ND 0.50 0.13 ug/l
124-48-1 Dibromochloromethane ND 0.50 0.13 ug/l
106-93-4 1,2-Dibromoethane ND 0.50 0.13 ug/l
75-71-8 Dichlorodifluoromethane ND 0.50 0.20 ug/l
95-50-1 1,2-Dichlorobenzene ND 0.50 0.13 ug/l
541-73-1 1,3-Dichlorobenzene ND 0.50 0.13 ug/l
106-46-7 1,4-Dichlorobenzene ND 0.50 0.13 ug/l
75-34-3 1,1-Dichloroethane ND 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane ND 0.50 0.13 ug/l
75-35-4 1,1-Dichloroethylene ND 0.50 0.13 ug/l
156-59-2 cis-1,2-Dichloroethylene ND 0.50 0.13 ug/l
156-60-5 trans-1,2-Dichloroethylene ND 0.50 0.13 ug/l
78-87-5 1,2-Dichloropropane ND 0.50 0.13 ug/l
142-28-9 1,3-Dichloropropane ND 0.50 0.13 ug/l
594-20-7 2,2-Dichloropropane ND 0.50 0.13 ug/l
563-58-6 1,1-Dichloropropene ND 0.50 0.13 ug/l
10061-01-5 cis-1,3-Dichloropropene ND 0.50 0.13 ug/l
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
7 of 81
FA8455633.1
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-1A
Lab Sample ID:FA84556-1 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
10061-02-6 trans-1,3-Dichloropropene ND 0.50 0.13 ug/l
108-20-3 Di-Isopropyl Ether ND 0.50 0.13 ug/l
64-17-5 Ethyl Alcohol a ND 100 65 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
591-78-6 2-Hexanone ND 5.0 1.0 ug/l
98-82-8 Isopropylbenzene ND 0.50 0.13 ug/l
99-87-6 p-Isopropyltoluene ND 0.50 0.13 ug/l
74-83-9 Methyl Bromide ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride ND 2.0 1.0 ug/l
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 0.50 0.13 ug/l
91-20-3 Naphthalene ND 0.50 0.13 ug/l
103-65-1 n-Propylbenzene ND 0.50 0.13 ug/l
100-42-5 Styrene ND 0.50 0.13 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 0.50 0.13 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 0.50 0.13 ug/l
127-18-4 Tetrachloroethylene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 0.50 0.13 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 0.50 0.13 ug/l
71-55-6 1,1,1-Trichloroethane ND 0.50 0.13 ug/l
79-00-5 1,1,2-Trichloroethane ND 0.50 0.13 ug/l
79-01-6 Trichloroethylene ND 0.50 0.13 ug/l
75-69-4 Trichlorofluoromethane ND 0.50 0.20 ug/l
96-18-4 1,2,3-Trichloropropane ND 0.50 0.13 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 0.50 0.13 ug/l
108-67-8 1,3,5-Trimethylbenzene ND 0.50 0.13 ug/l
108-05-4 Vinyl Acetate ND 5.0 1.0 ug/l
75-01-4 Vinyl Chloride ND 0.50 0.13 ug/l
m,p-Xylene ND 1.0 0.13 ug/l
95-47-6 o-Xylene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 101%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%70-130%
2037-26-5 Toluene-D8 99%70-130%
460-00-4 4-Bromofluorobenzene 97%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
8 of 81
FA8455633.1
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-1A
Lab Sample ID:FA84556-1 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated BS recovery outside control limits high; however sample is ND.
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
9 of 81
FA8455633.1
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-1A
Lab Sample ID:FA84556-1 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:MADEP VPH REV 2.1 Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 1S6156.D 1 04/19/21 17:33 BJ n/a n/a G1S209
Run #2
Purge Volume
Run #1 5.0 ml
Run #2
MADEP VPH List
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 1.0 1.0 ug/l
100-41-4 Ethylbenzene ND 2.0 1.0 ug/l
1634-04-4 Methyl Tert Butyl Ether 1.2 2.0 1.0 ug/l J
91-20-3 Naphthalene ND 5.0 3.0 ug/l
108-88-3 Toluene ND 2.0 1.0 ug/l
m,p-Xylene ND 4.0 2.0 ug/l
95-47-6 o-Xylene ND 2.0 1.0 ug/l
C5- C8 Aliphatics (Unadj.)ND 100 35 ug/l
C9- C12 Aliphatics (Unadj.)ND 100 35 ug/l
C9- C10 Aromatics (Unadj.)ND 100 35 ug/l
C5- C8 Aliphatics ND 100 35 ug/l
C9- C12 Aliphatics ND 100 35 ug/l
C9- C10 Aromatics ND 100 35 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 BFB 103%70-130%
460-00-4 BFB 105%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
10 of 81
FA8455633.1
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-1A
Lab Sample ID:FA84556-1 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:EPA 504.1 EPA 504 Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 a LI132625.D 1 04/12/21 19:48 ALA 04/12/21 11:30 L:OP18400 L:GLI1085
Run #2
Initial Volume Final Volume
Run #1 35.8 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.020 0.0037 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
348-51-6 1-Chloro-2-fluorobenzene 103%70-130%
(a) Analysis performed at SGS Scott, LA.
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
11 of 81
FA8455633.1
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-1A
Lab Sample ID:FA84556-1 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Total Metals Analysis
Analyte Result RL Units DF Prep Analyzed By Method Prep Method
Lead <5.0 5.0 ug/l 1 04/12/21 04/12/21 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA17606
(2) Prep QC Batch: MP38791
RL = Reporting Limit
12 of 81
FA8455633.1
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-1
Lab Sample ID:FA84556-2 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0225872.D 1 04/14/21 22:46 LR n/a n/a VA2878
Run #2
Purge Volume
Run #1 10.0 ml
Run #2
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone 8.2 10 2.0 ug/l J
71-43-2 Benzene ND 0.50 0.13 ug/l
108-86-1 Bromobenzene ND 0.50 0.13 ug/l
74-97-5 Bromochloromethane ND 0.50 0.13 ug/l
75-27-4 Bromodichloromethane ND 0.50 0.13 ug/l
75-25-2 Bromoform ND 0.50 0.13 ug/l
78-93-3 2-Butanone (MEK)1.6 2.5 1.3 ug/l J
104-51-8 n-Butylbenzene ND 0.50 0.13 ug/l
135-98-8 sec-Butylbenzene ND 0.50 0.13 ug/l
98-06-6 tert-Butylbenzene ND 0.50 0.13 ug/l
56-23-5 Carbon Tetrachloride ND 0.50 0.13 ug/l
108-90-7 Chlorobenzene ND 0.50 0.13 ug/l
75-00-3 Chloroethane ND 0.50 0.20 ug/l
67-66-3 Chloroform ND 0.50 0.13 ug/l
95-49-8 o-Chlorotoluene ND 0.50 0.13 ug/l
106-43-4 p-Chlorotoluene ND 0.50 0.13 ug/l
124-48-1 Dibromochloromethane ND 0.50 0.13 ug/l
106-93-4 1,2-Dibromoethane ND 0.50 0.13 ug/l
75-71-8 Dichlorodifluoromethane ND 0.50 0.20 ug/l
95-50-1 1,2-Dichlorobenzene ND 0.50 0.13 ug/l
541-73-1 1,3-Dichlorobenzene ND 0.50 0.13 ug/l
106-46-7 1,4-Dichlorobenzene ND 0.50 0.13 ug/l
75-34-3 1,1-Dichloroethane ND 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane ND 0.50 0.13 ug/l
75-35-4 1,1-Dichloroethylene ND 0.50 0.13 ug/l
156-59-2 cis-1,2-Dichloroethylene ND 0.50 0.13 ug/l
156-60-5 trans-1,2-Dichloroethylene ND 0.50 0.13 ug/l
78-87-5 1,2-Dichloropropane ND 0.50 0.13 ug/l
142-28-9 1,3-Dichloropropane ND 0.50 0.13 ug/l
594-20-7 2,2-Dichloropropane ND 0.50 0.13 ug/l
563-58-6 1,1-Dichloropropene ND 0.50 0.13 ug/l
10061-01-5 cis-1,3-Dichloropropene ND 0.50 0.13 ug/l
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
13 of 81
FA8455633.2
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-1
Lab Sample ID:FA84556-2 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
10061-02-6 trans-1,3-Dichloropropene ND 0.50 0.13 ug/l
108-20-3 Di-Isopropyl Ether ND 0.50 0.13 ug/l
64-17-5 Ethyl Alcohol a ND 100 65 ug/l
100-41-4 Ethylbenzene 0.15 0.50 0.13 ug/l J
591-78-6 2-Hexanone ND 5.0 1.0 ug/l
98-82-8 Isopropylbenzene ND 0.50 0.13 ug/l
99-87-6 p-Isopropyltoluene ND 0.50 0.13 ug/l
74-83-9 Methyl Bromide ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride ND 2.0 1.0 ug/l
108-10-1 4-Methyl-2-pentanone (MIBK)3.3 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 2.4 0.50 0.13 ug/l
91-20-3 Naphthalene 0.18 0.50 0.13 ug/l J
103-65-1 n-Propylbenzene ND 0.50 0.13 ug/l
100-42-5 Styrene ND 0.50 0.13 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 0.50 0.13 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 0.50 0.13 ug/l
127-18-4 Tetrachloroethylene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 0.50 0.13 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 0.50 0.13 ug/l
71-55-6 1,1,1-Trichloroethane ND 0.50 0.13 ug/l
79-00-5 1,1,2-Trichloroethane ND 0.50 0.13 ug/l
79-01-6 Trichloroethylene ND 0.50 0.13 ug/l
75-69-4 Trichlorofluoromethane ND 0.50 0.20 ug/l
96-18-4 1,2,3-Trichloropropane ND 0.50 0.13 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 0.50 0.13 ug/l
108-67-8 1,3,5-Trimethylbenzene ND 0.50 0.13 ug/l
108-05-4 Vinyl Acetate ND 5.0 1.0 ug/l
75-01-4 Vinyl Chloride ND 0.50 0.13 ug/l
m,p-Xylene ND 1.0 0.13 ug/l
95-47-6 o-Xylene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 102%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%70-130%
2037-26-5 Toluene-D8 98%70-130%
460-00-4 4-Bromofluorobenzene 96%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
14 of 81
FA8455633.2
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-1
Lab Sample ID:FA84556-2 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated BS recovery outside control limits high; however sample is ND.
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
15 of 81
FA8455633.2
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-1
Lab Sample ID:FA84556-2 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:MADEP VPH REV 2.1 Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 1S6147.D 1 04/19/21 13:21 BJ n/a n/a G1S209
Run #2
Purge Volume
Run #1 5.0 ml
Run #2
MADEP VPH List
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 1.0 1.0 ug/l
100-41-4 Ethylbenzene ND 2.0 1.0 ug/l
1634-04-4 Methyl Tert Butyl Ether 2.1 2.0 1.0 ug/l
91-20-3 Naphthalene ND 5.0 3.0 ug/l
108-88-3 Toluene ND 2.0 1.0 ug/l
m,p-Xylene ND 4.0 2.0 ug/l
95-47-6 o-Xylene ND 2.0 1.0 ug/l
C5- C8 Aliphatics (Unadj.)ND 100 35 ug/l
C9- C12 Aliphatics (Unadj.)ND 100 35 ug/l
C9- C10 Aromatics (Unadj.)ND 100 35 ug/l
C5- C8 Aliphatics ND 100 35 ug/l
C9- C12 Aliphatics ND 100 35 ug/l
C9- C10 Aromatics ND 100 35 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 BFB 100%70-130%
460-00-4 BFB 104%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
16 of 81
FA8455633.2
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-1
Lab Sample ID:FA84556-2 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:EPA 504.1 EPA 504 Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 a LI132626.D 1 04/12/21 20:07 ALA 04/12/21 11:30 L:OP18400 L:GLI1085
Run #2
Initial Volume Final Volume
Run #1 34.7 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.020 0.0038 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
348-51-6 1-Chloro-2-fluorobenzene 105%70-130%
(a) Analysis performed at SGS Scott, LA.
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
17 of 81
FA8455633.2
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-1
Lab Sample ID:FA84556-2 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Total Metals Analysis
Analyte Result RL Units DF Prep Analyzed By Method Prep Method
Lead <5.0 5.0 ug/l 1 04/12/21 04/12/21 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA17606
(2) Prep QC Batch: MP38791
RL = Reporting Limit
18 of 81
FA8455633.2
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-2
Lab Sample ID:FA84556-3 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0225886.D 2.5 04/15/21 14:35 LR n/a n/a VA2879
Run #2
Purge Volume
Run #1 10.0 ml
Run #2
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone ND 25 5.0 ug/l
71-43-2 Benzene ND 1.3 0.31 ug/l
108-86-1 Bromobenzene ND 1.3 0.31 ug/l
74-97-5 Bromochloromethane ND 1.3 0.31 ug/l
75-27-4 Bromodichloromethane ND 1.3 0.31 ug/l
75-25-2 Bromoform ND 1.3 0.31 ug/l
78-93-3 2-Butanone (MEK)ND 6.3 3.1 ug/l
104-51-8 n-Butylbenzene ND 1.3 0.31 ug/l
135-98-8 sec-Butylbenzene ND 1.3 0.31 ug/l
98-06-6 tert-Butylbenzene ND 1.3 0.31 ug/l
56-23-5 Carbon Tetrachloride a ND 1.3 0.31 ug/l
108-90-7 Chlorobenzene ND 1.3 0.31 ug/l
75-00-3 Chloroethane ND 1.3 0.50 ug/l
67-66-3 Chloroform 1.2 1.3 0.31 ug/l J
95-49-8 o-Chlorotoluene ND 1.3 0.31 ug/l
106-43-4 p-Chlorotoluene ND 1.3 0.31 ug/l
124-48-1 Dibromochloromethane ND 1.3 0.31 ug/l
106-93-4 1,2-Dibromoethane ND 1.3 0.31 ug/l
75-71-8 Dichlorodifluoromethane ND 1.3 0.50 ug/l
95-50-1 1,2-Dichlorobenzene ND 1.3 0.31 ug/l
541-73-1 1,3-Dichlorobenzene ND 1.3 0.31 ug/l
106-46-7 1,4-Dichlorobenzene ND 1.3 0.31 ug/l
75-34-3 1,1-Dichloroethane a ND 1.3 0.31 ug/l
107-06-2 1,2-Dichloroethane ND 1.3 0.31 ug/l
75-35-4 1,1-Dichloroethylene a ND 1.3 0.31 ug/l
156-59-2 cis-1,2-Dichloroethylene ND 1.3 0.31 ug/l
156-60-5 trans-1,2-Dichloroethylene a ND 1.3 0.31 ug/l
78-87-5 1,2-Dichloropropane ND 1.3 0.31 ug/l
142-28-9 1,3-Dichloropropane ND 1.3 0.31 ug/l
594-20-7 2,2-Dichloropropane ND 1.3 0.31 ug/l
563-58-6 1,1-Dichloropropene ND 1.3 0.31 ug/l
10061-01-5 cis-1,3-Dichloropropene ND 1.3 0.31 ug/l
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
19 of 81
FA8455633.3
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-2
Lab Sample ID:FA84556-3 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
10061-02-6 trans-1,3-Dichloropropene ND 1.3 0.31 ug/l
108-20-3 Di-Isopropyl Ether ND 1.3 0.31 ug/l
64-17-5 Ethyl Alcohol b ND 250 160 ug/l
100-41-4 Ethylbenzene ND 1.3 0.31 ug/l
591-78-6 2-Hexanone ND 13 2.5 ug/l
98-82-8 Isopropylbenzene ND 1.3 0.31 ug/l
99-87-6 p-Isopropyltoluene ND 1.3 0.31 ug/l
74-83-9 Methyl Bromide ND 1.3 0.50 ug/l
74-87-3 Methyl Chloride ND 1.3 0.50 ug/l
75-09-2 Methylene Chloride ND 5.0 2.5 ug/l
108-10-1 4-Methyl-2-pentanone (MIBK)ND 6.3 3.1 ug/l
1634-04-4 Methyl Tert Butyl Ether 80.5 1.3 0.31 ug/l
91-20-3 Naphthalene ND 1.3 0.31 ug/l
103-65-1 n-Propylbenzene ND 1.3 0.31 ug/l
100-42-5 Styrene ND 1.3 0.31 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 1.3 0.31 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 1.3 0.31 ug/l
127-18-4 Tetrachloroethylene a ND 1.3 0.31 ug/l
108-88-3 Toluene ND 1.3 0.31 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 1.3 0.31 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 1.3 0.31 ug/l
71-55-6 1,1,1-Trichloroethane ND 1.3 0.31 ug/l
79-00-5 1,1,2-Trichloroethane ND 1.3 0.31 ug/l
79-01-6 Trichloroethylene ND 1.3 0.31 ug/l
75-69-4 Trichlorofluoromethane ND 1.3 0.50 ug/l
96-18-4 1,2,3-Trichloropropane ND 1.3 0.31 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 1.3 0.31 ug/l
108-67-8 1,3,5-Trimethylbenzene ND 1.3 0.31 ug/l
108-05-4 Vinyl Acetate ND 13 2.5 ug/l
75-01-4 Vinyl Chloride ND 1.3 0.31 ug/l
m,p-Xylene ND 2.5 0.31 ug/l
95-47-6 o-Xylene ND 1.3 0.31 ug/l
1330-20-7 Xylene (total)ND 3.8 0.63 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 100%70-130%
17060-07-0 1,2-Dichloroethane-D4 102%70-130%
2037-26-5 Toluene-D8 99%70-130%
460-00-4 4-Bromofluorobenzene 98%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
20 of 81
FA8455633.3
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-2
Lab Sample ID:FA84556-3 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated BS recovery outside control limits high; however sample is ND.
(b) Associated CCV, ECC, and BS recovery outside control limits high; however sample is ND.
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
21 of 81
FA8455633.3
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-2
Lab Sample ID:FA84556-3 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:MADEP VPH REV 2.1 Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 1S6157.D 1 04/19/21 18:01 BJ n/a n/a G1S209
Run #2
Purge Volume
Run #1 5.0 ml
Run #2
MADEP VPH List
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 1.0 1.0 ug/l
100-41-4 Ethylbenzene ND 2.0 1.0 ug/l
1634-04-4 Methyl Tert Butyl Ether 104 2.0 1.0 ug/l
91-20-3 Naphthalene ND 5.0 3.0 ug/l
108-88-3 Toluene ND 2.0 1.0 ug/l
m,p-Xylene ND 4.0 2.0 ug/l
95-47-6 o-Xylene ND 2.0 1.0 ug/l
C5- C8 Aliphatics (Unadj.)53.5 100 35 ug/l J
C9- C12 Aliphatics (Unadj.)ND 100 35 ug/l
C9- C10 Aromatics (Unadj.)ND 100 35 ug/l
C5- C8 Aliphatics ND 100 35 ug/l
C9- C12 Aliphatics ND 100 35 ug/l
C9- C10 Aromatics ND 100 35 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 BFB 104%70-130%
460-00-4 BFB 106%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
22 of 81
FA8455633.3
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-2
Lab Sample ID:FA84556-3 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:EPA 504.1 EPA 504 Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 a LI132627.D 1 04/12/21 20:25 ALA 04/12/21 11:30 L:OP18400 L:GLI1085
Run #2
Initial Volume Final Volume
Run #1 35.2 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.020 0.0038 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
348-51-6 1-Chloro-2-fluorobenzene 101%70-130%
(a) Analysis performed at SGS Scott, LA.
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-2
Lab Sample ID:FA84556-3 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Total Metals Analysis
Analyte Result RL Units DF Prep Analyzed By Method Prep Method
Lead <5.0 5.0 ug/l 1 04/12/21 04/12/21 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA17606
(2) Prep QC Batch: MP38791
RL = Reporting Limit
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SGS North America Inc.
Report of Analysis Page 1 of 2
Client Sample ID:MW-3
Lab Sample ID:FA84556-4 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 E106529.D 250 04/14/21 15:00 LR n/a n/a VE2454
Run #2
Purge Volume
Run #1 10.0 ml
Run #2
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone ND 2500 500 ug/l
71-43-2 Benzene 7380 130 31 ug/l
108-86-1 Bromobenzene ND 130 31 ug/l
74-97-5 Bromochloromethane ND 130 31 ug/l
75-27-4 Bromodichloromethane ND 130 31 ug/l
75-25-2 Bromoform ND 130 31 ug/l
78-93-3 2-Butanone (MEK)ND 630 310 ug/l
104-51-8 n-Butylbenzene ND 130 31 ug/l
135-98-8 sec-Butylbenzene ND 130 31 ug/l
98-06-6 tert-Butylbenzene ND 130 31 ug/l
56-23-5 Carbon Tetrachloride ND 130 31 ug/l
108-90-7 Chlorobenzene ND 130 31 ug/l
75-00-3 Chloroethane ND 130 50 ug/l
67-66-3 Chloroform ND 130 31 ug/l
95-49-8 o-Chlorotoluene ND 130 31 ug/l
106-43-4 p-Chlorotoluene ND 130 31 ug/l
124-48-1 Dibromochloromethane ND 130 31 ug/l
106-93-4 1,2-Dibromoethane 49.5 130 31 ug/l J
75-71-8 Dichlorodifluoromethane ND 130 50 ug/l
95-50-1 1,2-Dichlorobenzene ND 130 31 ug/l
541-73-1 1,3-Dichlorobenzene ND 130 31 ug/l
106-46-7 1,4-Dichlorobenzene ND 130 31 ug/l
75-34-3 1,1-Dichloroethane ND 130 31 ug/l
107-06-2 1,2-Dichloroethane 267 130 31 ug/l
75-35-4 1,1-Dichloroethylene ND 130 31 ug/l
156-59-2 cis-1,2-Dichloroethylene ND 130 31 ug/l
156-60-5 trans-1,2-Dichloroethylene ND 130 31 ug/l
78-87-5 1,2-Dichloropropane ND 130 31 ug/l
142-28-9 1,3-Dichloropropane ND 130 31 ug/l
594-20-7 2,2-Dichloropropane ND 130 31 ug/l
563-58-6 1,1-Dichloropropene ND 130 31 ug/l
10061-01-5 cis-1,3-Dichloropropene ND 130 31 ug/l
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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FA8455633.4
SGS North America Inc.
Report of Analysis Page 2 of 2
Client Sample ID:MW-3
Lab Sample ID:FA84556-4 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:SM 6200B Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
10061-02-6 trans-1,3-Dichloropropene ND 130 31 ug/l
108-20-3 Di-Isopropyl Ether ND 130 31 ug/l
64-17-5 Ethyl Alcohol ND 25000 16000 ug/l
100-41-4 Ethylbenzene 1710 130 31 ug/l
591-78-6 2-Hexanone 822 1300 250 ug/l J
98-82-8 Isopropylbenzene 148 130 31 ug/l
99-87-6 p-Isopropyltoluene ND 130 31 ug/l
74-83-9 Methyl Bromide ND 130 50 ug/l
74-87-3 Methyl Chloride ND 130 50 ug/l
75-09-2 Methylene Chloride ND 500 250 ug/l
108-10-1 4-Methyl-2-pentanone (MIBK)404 630 310 ug/l J
1634-04-4 Methyl Tert Butyl Ether ND 130 31 ug/l
91-20-3 Naphthalene 243 130 31 ug/l
103-65-1 n-Propylbenzene 208 130 31 ug/l
100-42-5 Styrene ND 130 31 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 130 31 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 130 31 ug/l
127-18-4 Tetrachloroethylene ND 130 31 ug/l
108-88-3 Toluene 11600 130 31 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 130 31 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 130 31 ug/l
71-55-6 1,1,1-Trichloroethane ND 130 31 ug/l
79-00-5 1,1,2-Trichloroethane ND 130 31 ug/l
79-01-6 Trichloroethylene ND 130 31 ug/l
75-69-4 Trichlorofluoromethane ND 130 50 ug/l
96-18-4 1,2,3-Trichloropropane ND 130 31 ug/l
95-63-6 1,2,4-Trimethylbenzene 1550 130 31 ug/l
108-67-8 1,3,5-Trimethylbenzene 410 130 31 ug/l
108-05-4 Vinyl Acetate ND 1300 250 ug/l
75-01-4 Vinyl Chloride ND 130 31 ug/l
m,p-Xylene 6190 250 31 ug/l
95-47-6 o-Xylene 2190 130 31 ug/l
1330-20-7 Xylene (total)8380 380 63 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 98%70-130%
17060-07-0 1,2-Dichloroethane-D4 102%70-130%
2037-26-5 Toluene-D8 100%70-130%
460-00-4 4-Bromofluorobenzene 99%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-3
Lab Sample ID:FA84556-4 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:MADEP VPH REV 2.1 Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 1S6158.D 50 04/19/21 18:29 BJ n/a n/a G1S209
Run #2
Purge Volume
Run #1 5.0 ml
Run #2
MADEP VPH List
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene 6860 50 50 ug/l
100-41-4 Ethylbenzene 1590 100 50 ug/l
1634-04-4 Methyl Tert Butyl Ether 148 100 50 ug/l
91-20-3 Naphthalene 265 250 150 ug/l
108-88-3 Toluene 10400 100 50 ug/l
m,p-Xylene 5830 200 100 ug/l
95-47-6 o-Xylene 2210 100 50 ug/l
C5- C8 Aliphatics (Unadj.)29800 5000 1800 ug/l
C9- C12 Aliphatics (Unadj.)3800 5000 1800 ug/l J
C9- C10 Aromatics (Unadj.)12000 5000 1800 ug/l
C5- C8 Aliphatics 12400 5000 1800 ug/l
C9- C12 Aliphatics ND 5000 1800 ug/l
C9- C10 Aromatics 12000 5000 1800 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 BFB 102%70-130%
460-00-4 BFB 105%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
27 of 81
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SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-3
Lab Sample ID:FA84556-4 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Method:EPA 504.1 EPA 504 Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 a LI132653.D 1 04/14/21 15:12 ALA 04/14/21 09:45 L:OP18409 L:GLI1086
Run #2
Initial Volume Final Volume
Run #1 35.3 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane 0.53 0.020 0.0038 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
348-51-6 1-Chloro-2-fluorobenzene 0% b 70-130%
(a) Analysis performed at SGS Scott, LA.
(b) Outside control limits due to dilution.
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
28 of 81
FA8455633.4
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-3
Lab Sample ID:FA84556-4 Date Sampled:04/08/21
Matrix:AQ - Ground Water Date Received:04/09/21
Percent Solids:n/a
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Total Metals Analysis
Analyte Result RL Units DF Prep Analyzed By Method Prep Method
Lead <5.0 5.0 ug/l 1 04/12/21 04/12/21 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA17606
(2) Prep QC Batch: MP38791
RL = Reporting Limit
29 of 81
FA8455633.4
SGS North America Inc.
Misc. Forms
Custody Documents and Other Forms
Includes the following where applicable:
• Chain of Custody
Orlando, FL
Section 4
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FA845564
FA84556: Chain of Custody
Page 1 of 2
31 of 81
FA8455644.1
Job Number:FA84556 Client:RESOLVE ENVIRONMENTAL
Date / Time Received:4/9/2021 10:00:00 AM Delivery Method:FX
Project:KWICK MART
Airbill #'s:1009 6378 7220
Cooler Information
1. Custody Seals Present
2. Custody Seals Intact
4. Cooler temp verification
3. Temp criteria achieved
5. Cooler media
IR Gun
Ice (Bag)
Trip Blank Information
1. Trip Blank present / cooler
2. Trip Blank listed on COC
2. Samples preserved properly
Sample Information
1. Sample labels present on bottles
5. Sample recvd within HT
4. Condition of sample
3. Sufficient volume/containers recvd for analysis:
Intact
Comments
SM001Rev. Date 05/24/17
SGS Sample Receipt Summary
Cooler Temps (Raw Measured) °C:
Cooler Temps (Corrected) °C:
Cooler 1: (3.0);
Cooler 1: (1.2);
3. Type Of TB Received
W or S N/A
6. Dates/Times/IDs on COC match Sample Label
7. VOCs have headspace
8. Bottles received for unspecified tests
9. Compositing instructions clear
10. Voa Soil Kits/Jars received past 48hrs?
11. % Solids Jar received?
Misc. Information
25-Gram 5-GramNumber of Encores:Number of 5035 Field Kits:Number of Lab Filtered Metals:
Test Strip Lot #s:pH 0-3 230315 pH 10-12 219813A Other: (Specify)
Y or N N/A
Y or N
Therm ID:IR 1; Therm CF:-1.8; # of Coolers:1
Y or N N/A
12. Residual Chlorine Present?
Residual Chlorine Test Strip Lot #:
Technician:Reviewer:PETERH Date:Date:4/9/2021 10:00:00 AM
FA84556: Chain of Custody
Page 2 of 2
32 of 81
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SGS North America Inc.
MS Volatiles
QC Data Summaries
Includes the following where applicable:
• Method Blank Summaries
• Blank Spike Summaries
• Matrix Spike and Duplicate Summaries
Orlando, FL
Section 5
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FA845565
Method Blank Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VE2454-MB E106525.D 1 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone ND 10 2.0 ug/l
71-43-2 Benzene ND 0.50 0.13 ug/l
108-86-1 Bromobenzene ND 0.50 0.13 ug/l
74-97-5 Bromochloromethane ND 0.50 0.13 ug/l
75-27-4 Bromodichloromethane ND 0.50 0.13 ug/l
75-25-2 Bromoform ND 0.50 0.13 ug/l
78-93-3 2-Butanone (MEK)ND 2.5 1.3 ug/l
104-51-8 n-Butylbenzene ND 0.50 0.13 ug/l
135-98-8 sec-Butylbenzene ND 0.50 0.13 ug/l
98-06-6 tert-Butylbenzene ND 0.50 0.13 ug/l
56-23-5 Carbon Tetrachloride ND 0.50 0.13 ug/l
108-90-7 Chlorobenzene ND 0.50 0.13 ug/l
75-00-3 Chloroethane ND 0.50 0.20 ug/l
67-66-3 Chloroform ND 0.50 0.13 ug/l
95-49-8 o-Chlorotoluene ND 0.50 0.13 ug/l
106-43-4 p-Chlorotoluene ND 0.50 0.13 ug/l
124-48-1 Dibromochloromethane ND 0.50 0.13 ug/l
106-93-4 1,2-Dibromoethane ND 0.50 0.13 ug/l
75-71-8 Dichlorodifluoromethane ND 0.50 0.20 ug/l
95-50-1 1,2-Dichlorobenzene ND 0.50 0.13 ug/l
541-73-1 1,3-Dichlorobenzene ND 0.50 0.13 ug/l
106-46-7 1,4-Dichlorobenzene ND 0.50 0.13 ug/l
75-34-3 1,1-Dichloroethane ND 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane ND 0.50 0.13 ug/l
75-35-4 1,1-Dichloroethylene ND 0.50 0.13 ug/l
156-59-2 cis-1,2-Dichloroethylene ND 0.50 0.13 ug/l
156-60-5 trans-1,2-Dichloroethylene ND 0.50 0.13 ug/l
78-87-5 1,2-Dichloropropane ND 0.50 0.13 ug/l
142-28-9 1,3-Dichloropropane ND 0.50 0.13 ug/l
594-20-7 2,2-Dichloropropane ND 0.50 0.13 ug/l
563-58-6 1,1-Dichloropropene ND 0.50 0.13 ug/l
10061-01-5 cis-1,3-Dichloropropene ND 0.50 0.13 ug/l
10061-02-6 trans-1,3-Dichloropropene ND 0.50 0.13 ug/l
108-20-3 Di-Isopropyl Ether ND 0.50 0.13 ug/l
64-17-5 Ethyl Alcohol ND 100 65 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
34 of 81
FA8455655.1.1
Method Blank Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VE2454-MB E106525.D 1 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
CAS No.Compound Result RL MDL Units Q
591-78-6 2-Hexanone ND 5.0 1.0 ug/l
98-82-8 Isopropylbenzene ND 0.50 0.13 ug/l
99-87-6 p-Isopropyltoluene ND 0.50 0.13 ug/l
74-83-9 Methyl Bromide ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride ND 2.0 1.0 ug/l
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 0.50 0.13 ug/l
91-20-3 Naphthalene ND 0.50 0.13 ug/l
103-65-1 n-Propylbenzene ND 0.50 0.13 ug/l
100-42-5 Styrene ND 0.50 0.13 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 0.50 0.13 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 0.50 0.13 ug/l
127-18-4 Tetrachloroethylene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 0.50 0.13 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 0.50 0.13 ug/l
71-55-6 1,1,1-Trichloroethane ND 0.50 0.13 ug/l
79-00-5 1,1,2-Trichloroethane ND 0.50 0.13 ug/l
79-01-6 Trichloroethylene ND 0.50 0.13 ug/l
75-69-4 Trichlorofluoromethane ND 0.50 0.20 ug/l
96-18-4 1,2,3-Trichloropropane ND 0.50 0.13 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 0.50 0.13 ug/l
108-67-8 1,3,5-Trimethylbenzene ND 0.50 0.13 ug/l
108-05-4 Vinyl Acetate ND 5.0 1.0 ug/l
75-01-4 Vinyl Chloride ND 0.50 0.13 ug/l
m,p-Xylene ND 1.0 0.13 ug/l
95-47-6 o-Xylene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
CAS No.Surrogate Recoveries Limits
1868-53-7 Dibromofluoromethane 97%70-130%
17060-07-0 1,2-Dichloroethane-D4 101%70-130%
2037-26-5 Toluene-D8 100%70-130%
35 of 81
FA8455655.1.1
Method Blank Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VE2454-MB E106525.D 1 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 102%70-130%
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FA8455655.1.1
Method Blank Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2878-MB A0225851.D 1 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone ND 10 2.0 ug/l
71-43-2 Benzene ND 0.50 0.13 ug/l
108-86-1 Bromobenzene ND 0.50 0.13 ug/l
74-97-5 Bromochloromethane ND 0.50 0.13 ug/l
75-27-4 Bromodichloromethane ND 0.50 0.13 ug/l
75-25-2 Bromoform ND 0.50 0.13 ug/l
78-93-3 2-Butanone (MEK)ND 2.5 1.3 ug/l
104-51-8 n-Butylbenzene ND 0.50 0.13 ug/l
135-98-8 sec-Butylbenzene ND 0.50 0.13 ug/l
98-06-6 tert-Butylbenzene ND 0.50 0.13 ug/l
56-23-5 Carbon Tetrachloride ND 0.50 0.13 ug/l
108-90-7 Chlorobenzene ND 0.50 0.13 ug/l
75-00-3 Chloroethane ND 0.50 0.20 ug/l
67-66-3 Chloroform ND 0.50 0.13 ug/l
95-49-8 o-Chlorotoluene ND 0.50 0.13 ug/l
106-43-4 p-Chlorotoluene ND 0.50 0.13 ug/l
124-48-1 Dibromochloromethane ND 0.50 0.13 ug/l
106-93-4 1,2-Dibromoethane ND 0.50 0.13 ug/l
75-71-8 Dichlorodifluoromethane ND 0.50 0.20 ug/l
95-50-1 1,2-Dichlorobenzene ND 0.50 0.13 ug/l
541-73-1 1,3-Dichlorobenzene ND 0.50 0.13 ug/l
106-46-7 1,4-Dichlorobenzene ND 0.50 0.13 ug/l
75-34-3 1,1-Dichloroethane ND 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane ND 0.50 0.13 ug/l
75-35-4 1,1-Dichloroethylene ND 0.50 0.13 ug/l
156-59-2 cis-1,2-Dichloroethylene ND 0.50 0.13 ug/l
156-60-5 trans-1,2-Dichloroethylene ND 0.50 0.13 ug/l
78-87-5 1,2-Dichloropropane ND 0.50 0.13 ug/l
142-28-9 1,3-Dichloropropane ND 0.50 0.13 ug/l
594-20-7 2,2-Dichloropropane ND 0.50 0.13 ug/l
563-58-6 1,1-Dichloropropene ND 0.50 0.13 ug/l
10061-01-5 cis-1,3-Dichloropropene ND 0.50 0.13 ug/l
10061-02-6 trans-1,3-Dichloropropene ND 0.50 0.13 ug/l
108-20-3 Di-Isopropyl Ether ND 0.50 0.13 ug/l
64-17-5 Ethyl Alcohol ND 100 65 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
37 of 81
FA8455655.1.2
Method Blank Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2878-MB A0225851.D 1 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
CAS No.Compound Result RL MDL Units Q
591-78-6 2-Hexanone ND 5.0 1.0 ug/l
98-82-8 Isopropylbenzene ND 0.50 0.13 ug/l
99-87-6 p-Isopropyltoluene ND 0.50 0.13 ug/l
74-83-9 Methyl Bromide ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride ND 2.0 1.0 ug/l
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 0.50 0.13 ug/l
91-20-3 Naphthalene ND 0.50 0.13 ug/l
103-65-1 n-Propylbenzene ND 0.50 0.13 ug/l
100-42-5 Styrene ND 0.50 0.13 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 0.50 0.13 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 0.50 0.13 ug/l
127-18-4 Tetrachloroethylene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 0.50 0.13 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 0.50 0.13 ug/l
71-55-6 1,1,1-Trichloroethane ND 0.50 0.13 ug/l
79-00-5 1,1,2-Trichloroethane ND 0.50 0.13 ug/l
79-01-6 Trichloroethylene ND 0.50 0.13 ug/l
75-69-4 Trichlorofluoromethane ND 0.50 0.20 ug/l
96-18-4 1,2,3-Trichloropropane ND 0.50 0.13 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 0.50 0.13 ug/l
108-67-8 1,3,5-Trimethylbenzene ND 0.50 0.13 ug/l
108-05-4 Vinyl Acetate ND 5.0 1.0 ug/l
75-01-4 Vinyl Chloride ND 0.50 0.13 ug/l
m,p-Xylene ND 1.0 0.13 ug/l
95-47-6 o-Xylene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
CAS No.Surrogate Recoveries Limits
1868-53-7 Dibromofluoromethane 101%70-130%
17060-07-0 1,2-Dichloroethane-D4 102%70-130%
2037-26-5 Toluene-D8 100%70-130%
38 of 81
FA8455655.1.2
Method Blank Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2878-MB A0225851.D 1 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 99%70-130%
39 of 81
FA8455655.1.2
Method Blank Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2879-MB A0225882.D 1 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone ND 10 2.0 ug/l
71-43-2 Benzene ND 0.50 0.13 ug/l
108-86-1 Bromobenzene ND 0.50 0.13 ug/l
74-97-5 Bromochloromethane ND 0.50 0.13 ug/l
75-27-4 Bromodichloromethane ND 0.50 0.13 ug/l
75-25-2 Bromoform ND 0.50 0.13 ug/l
78-93-3 2-Butanone (MEK)ND 2.5 1.3 ug/l
104-51-8 n-Butylbenzene ND 0.50 0.13 ug/l
135-98-8 sec-Butylbenzene ND 0.50 0.13 ug/l
98-06-6 tert-Butylbenzene ND 0.50 0.13 ug/l
56-23-5 Carbon Tetrachloride ND 0.50 0.13 ug/l
108-90-7 Chlorobenzene ND 0.50 0.13 ug/l
75-00-3 Chloroethane ND 0.50 0.20 ug/l
67-66-3 Chloroform ND 0.50 0.13 ug/l
95-49-8 o-Chlorotoluene ND 0.50 0.13 ug/l
106-43-4 p-Chlorotoluene ND 0.50 0.13 ug/l
124-48-1 Dibromochloromethane ND 0.50 0.13 ug/l
106-93-4 1,2-Dibromoethane ND 0.50 0.13 ug/l
75-71-8 Dichlorodifluoromethane ND 0.50 0.20 ug/l
95-50-1 1,2-Dichlorobenzene ND 0.50 0.13 ug/l
541-73-1 1,3-Dichlorobenzene ND 0.50 0.13 ug/l
106-46-7 1,4-Dichlorobenzene ND 0.50 0.13 ug/l
75-34-3 1,1-Dichloroethane ND 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane ND 0.50 0.13 ug/l
75-35-4 1,1-Dichloroethylene ND 0.50 0.13 ug/l
156-59-2 cis-1,2-Dichloroethylene ND 0.50 0.13 ug/l
156-60-5 trans-1,2-Dichloroethylene ND 0.50 0.13 ug/l
78-87-5 1,2-Dichloropropane ND 0.50 0.13 ug/l
142-28-9 1,3-Dichloropropane ND 0.50 0.13 ug/l
594-20-7 2,2-Dichloropropane ND 0.50 0.13 ug/l
563-58-6 1,1-Dichloropropene ND 0.50 0.13 ug/l
10061-01-5 cis-1,3-Dichloropropene ND 0.50 0.13 ug/l
10061-02-6 trans-1,3-Dichloropropene ND 0.50 0.13 ug/l
108-20-3 Di-Isopropyl Ether ND 0.50 0.13 ug/l
64-17-5 Ethyl Alcohol ND 100 65 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
40 of 81
FA8455655.1.3
Method Blank Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2879-MB A0225882.D 1 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
CAS No.Compound Result RL MDL Units Q
591-78-6 2-Hexanone ND 5.0 1.0 ug/l
98-82-8 Isopropylbenzene ND 0.50 0.13 ug/l
99-87-6 p-Isopropyltoluene ND 0.50 0.13 ug/l
74-83-9 Methyl Bromide ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride ND 2.0 1.0 ug/l
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 0.50 0.13 ug/l
91-20-3 Naphthalene ND 0.50 0.13 ug/l
103-65-1 n-Propylbenzene ND 0.50 0.13 ug/l
100-42-5 Styrene ND 0.50 0.13 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 0.50 0.13 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 0.50 0.13 ug/l
127-18-4 Tetrachloroethylene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 0.50 0.13 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 0.50 0.13 ug/l
71-55-6 1,1,1-Trichloroethane ND 0.50 0.13 ug/l
79-00-5 1,1,2-Trichloroethane ND 0.50 0.13 ug/l
79-01-6 Trichloroethylene ND 0.50 0.13 ug/l
75-69-4 Trichlorofluoromethane ND 0.50 0.20 ug/l
96-18-4 1,2,3-Trichloropropane ND 0.50 0.13 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 0.50 0.13 ug/l
108-67-8 1,3,5-Trimethylbenzene ND 0.50 0.13 ug/l
108-05-4 Vinyl Acetate ND 5.0 1.0 ug/l
75-01-4 Vinyl Chloride ND 0.50 0.13 ug/l
m,p-Xylene ND 1.0 0.13 ug/l
95-47-6 o-Xylene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
CAS No.Surrogate Recoveries Limits
1868-53-7 Dibromofluoromethane 100%70-130%
17060-07-0 1,2-Dichloroethane-D4 106%70-130%
2037-26-5 Toluene-D8 99%70-130%
41 of 81
FA8455655.1.3
Method Blank Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2879-MB A0225882.D 1 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 98%70-130%
42 of 81
FA8455655.1.3
Blank Spike Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VE2454-BS E106523.D 1 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
67-64-1 Acetone 50 59.0 118 70-130
71-43-2 Benzene 10 11.0 110 70-130
108-86-1 Bromobenzene 10 10.5 105 70-130
74-97-5 Bromochloromethane 10 10.4 104 70-130
75-27-4 Bromodichloromethane 10 11.1 111 70-130
75-25-2 Bromoform 10 10.0 100 70-130
78-93-3 2-Butanone (MEK)50 51.1 102 70-130
104-51-8 n-Butylbenzene 10 10.8 108 70-130
135-98-8 sec-Butylbenzene 10 11.4 114 70-130
98-06-6 tert-Butylbenzene 10 10.9 109 70-130
56-23-5 Carbon Tetrachloride 10 12.2 122 70-130
108-90-7 Chlorobenzene 10 10.5 105 70-130
75-00-3 Chloroethane 10 10.4 104 60-140
67-66-3 Chloroform 10 10.9 109 70-130
95-49-8 o-Chlorotoluene 10 10.6 106 70-130
106-43-4 p-Chlorotoluene 10 10.6 106 70-130
124-48-1 Dibromochloromethane 10 10.5 105 70-130
106-93-4 1,2-Dibromoethane 10 10.1 101 70-130
75-71-8 Dichlorodifluoromethane 10 8.8 88 60-140
95-50-1 1,2-Dichlorobenzene 10 10.4 104 70-130
541-73-1 1,3-Dichlorobenzene 10 10.8 108 70-130
106-46-7 1,4-Dichlorobenzene 10 10.4 104 70-130
75-34-3 1,1-Dichloroethane 10 11.8 118 70-130
107-06-2 1,2-Dichloroethane 10 10.5 105 70-130
75-35-4 1,1-Dichloroethylene 10 12.5 125 70-130
156-59-2 cis-1,2-Dichloroethylene 10 11.0 110 70-130
156-60-5 trans-1,2-Dichloroethylene 10 11.7 117 70-130
78-87-5 1,2-Dichloropropane 10 10.6 106 70-130
142-28-9 1,3-Dichloropropane 10 10.1 101 70-130
594-20-7 2,2-Dichloropropane 10 11.9 119 70-130
563-58-6 1,1-Dichloropropene 10 11.0 110 70-130
10061-01-5 cis-1,3-Dichloropropene 10 10.1 101 70-130
10061-02-6 trans-1,3-Dichloropropene 10 10.7 107 70-130
108-20-3 Di-Isopropyl Ether 10 10.5 105 70-130
64-17-5 Ethyl Alcohol 500 614 123 70-130
100-41-4 Ethylbenzene 10 11.0 110 70-130
* = Outside of Control Limits.
43 of 81
FA8455655.2.1
Blank Spike Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VE2454-BS E106523.D 1 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
591-78-6 2-Hexanone 50 50.4 101 70-130
98-82-8 Isopropylbenzene 10 11.0 110 70-130
99-87-6 p-Isopropyltoluene 10 11.2 112 70-130
74-83-9 Methyl Bromide 10 10.8 108 60-140
74-87-3 Methyl Chloride 10 9.4 94 60-140
75-09-2 Methylene Chloride 10 9.3 93 70-130
108-10-1 4-Methyl-2-pentanone (MIBK)50 52.1 104 70-130
1634-04-4 Methyl Tert Butyl Ether 10 10.5 105 70-130
91-20-3 Naphthalene 10 10.5 105 70-130
103-65-1 n-Propylbenzene 10 10.9 109 70-130
100-42-5 Styrene 10 10.5 105 70-130
630-20-6 1,1,1,2-Tetrachloroethane 10 10.8 108 70-130
79-34-5 1,1,2,2-Tetrachloroethane 10 10.0 100 70-130
127-18-4 Tetrachloroethylene 10 11.5 115 70-130
108-88-3 Toluene 10 10.7 107 70-130
87-61-6 1,2,3-Trichlorobenzene 10 10.5 105 70-130
120-82-1 1,2,4-Trichlorobenzene 10 10.6 106 70-130
71-55-6 1,1,1-Trichloroethane 10 11.6 116 70-130
79-00-5 1,1,2-Trichloroethane 10 10.5 105 70-130
79-01-6 Trichloroethylene 10 10.7 107 70-130
75-69-4 Trichlorofluoromethane 10 11.0 110 60-140
96-18-4 1,2,3-Trichloropropane 10 10.3 103 70-130
95-63-6 1,2,4-Trimethylbenzene 10 10.4 104 70-130
108-67-8 1,3,5-Trimethylbenzene 10 11.0 110 70-130
108-05-4 Vinyl Acetate 50 46.2 92 70-130
75-01-4 Vinyl Chloride 10 10.1 101 60-140
m,p-Xylene 20 22.0 110 70-130
95-47-6 o-Xylene 10 10.5 105 70-130
1330-20-7 Xylene (total)30 32.5 108 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 101%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%70-130%
2037-26-5 Toluene-D8 100%70-130%
* = Outside of Control Limits.
44 of 81
FA8455655.2.1
Blank Spike Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VE2454-BS E106523.D 1 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 99%70-130%
* = Outside of Control Limits.
45 of 81
FA8455655.2.1
Blank Spike Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2878-BS A0225849.D 1 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
67-64-1 Acetone 50 58.2 116 70-130
71-43-2 Benzene 10 11.4 114 70-130
108-86-1 Bromobenzene 10 11.3 113 70-130
74-97-5 Bromochloromethane 10 11.0 110 70-130
75-27-4 Bromodichloromethane 10 11.9 119 70-130
75-25-2 Bromoform 10 11.9 119 70-130
78-93-3 2-Butanone (MEK)50 53.9 108 70-130
104-51-8 n-Butylbenzene 10 11.2 112 70-130
135-98-8 sec-Butylbenzene 10 11.9 119 70-130
98-06-6 tert-Butylbenzene 10 11.4 114 70-130
56-23-5 Carbon Tetrachloride 10 12.7 127 70-130
108-90-7 Chlorobenzene 10 11.1 111 70-130
75-00-3 Chloroethane 10 11.5 115 60-140
67-66-3 Chloroform 10 11.2 112 70-130
95-49-8 o-Chlorotoluene 10 11.1 111 70-130
106-43-4 p-Chlorotoluene 10 11.1 111 70-130
124-48-1 Dibromochloromethane 10 11.6 116 70-130
106-93-4 1,2-Dibromoethane 10 10.9 109 70-130
75-71-8 Dichlorodifluoromethane 10 9.4 94 60-140
95-50-1 1,2-Dichlorobenzene 10 11.1 111 70-130
541-73-1 1,3-Dichlorobenzene 10 11.3 113 70-130
106-46-7 1,4-Dichlorobenzene 10 10.9 109 70-130
75-34-3 1,1-Dichloroethane 10 12.1 121 70-130
107-06-2 1,2-Dichloroethane 10 11.1 111 70-130
75-35-4 1,1-Dichloroethylene 10 12.2 122 70-130
156-59-2 cis-1,2-Dichloroethylene 10 11.6 116 70-130
156-60-5 trans-1,2-Dichloroethylene 10 12.0 120 70-130
78-87-5 1,2-Dichloropropane 10 10.9 109 70-130
142-28-9 1,3-Dichloropropane 10 10.8 108 70-130
594-20-7 2,2-Dichloropropane 10 11.8 118 70-130
563-58-6 1,1-Dichloropropene 10 11.6 116 70-130
10061-01-5 cis-1,3-Dichloropropene 10 10.7 107 70-130
10061-02-6 trans-1,3-Dichloropropene 10 11.6 116 70-130
108-20-3 Di-Isopropyl Ether 10 10.7 107 70-130
64-17-5 Ethyl Alcohol 500 1020 204*70-130
100-41-4 Ethylbenzene 10 11.3 113 70-130
* = Outside of Control Limits.
46 of 81
FA8455655.2.2
Blank Spike Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2878-BS A0225849.D 1 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
591-78-6 2-Hexanone 50 57.5 115 70-130
98-82-8 Isopropylbenzene 10 11.5 115 70-130
99-87-6 p-Isopropyltoluene 10 11.8 118 70-130
74-83-9 Methyl Bromide 10 10.7 107 60-140
74-87-3 Methyl Chloride 10 10.8 108 60-140
75-09-2 Methylene Chloride 10 11.2 112 70-130
108-10-1 4-Methyl-2-pentanone (MIBK)50 51.4 103 70-130
1634-04-4 Methyl Tert Butyl Ether 10 10.7 107 70-130
91-20-3 Naphthalene 10 11.6 116 70-130
103-65-1 n-Propylbenzene 10 11.4 114 70-130
100-42-5 Styrene 10 11.0 110 70-130
630-20-6 1,1,1,2-Tetrachloroethane 10 11.2 112 70-130
79-34-5 1,1,2,2-Tetrachloroethane 10 10.8 108 70-130
127-18-4 Tetrachloroethylene 10 12.4 124 70-130
108-88-3 Toluene 10 11.3 113 70-130
87-61-6 1,2,3-Trichlorobenzene 10 11.4 114 70-130
120-82-1 1,2,4-Trichlorobenzene 10 11.3 113 70-130
71-55-6 1,1,1-Trichloroethane 10 12.1 121 70-130
79-00-5 1,1,2-Trichloroethane 10 11.1 111 70-130
79-01-6 Trichloroethylene 10 11.6 116 70-130
75-69-4 Trichlorofluoromethane 10 11.5 115 60-140
96-18-4 1,2,3-Trichloropropane 10 10.9 109 70-130
95-63-6 1,2,4-Trimethylbenzene 10 10.9 109 70-130
108-67-8 1,3,5-Trimethylbenzene 10 11.5 115 70-130
108-05-4 Vinyl Acetate 50 44.0 88 70-130
75-01-4 Vinyl Chloride 10 10.9 109 60-140
m,p-Xylene 20 22.9 115 70-130
95-47-6 o-Xylene 10 11.1 111 70-130
1330-20-7 Xylene (total)30 33.9 113 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 100%70-130%
17060-07-0 1,2-Dichloroethane-D4 100%70-130%
2037-26-5 Toluene-D8 100%70-130%
* = Outside of Control Limits.
47 of 81
FA8455655.2.2
Blank Spike Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2878-BS A0225849.D 1 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 99%70-130%
* = Outside of Control Limits.
48 of 81
FA8455655.2.2
Blank Spike Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2879-BS A0225880.D 1 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
67-64-1 Acetone 50 60.9 122 70-130
71-43-2 Benzene 10 12.5 125 70-130
108-86-1 Bromobenzene 10 12.2 122 70-130
74-97-5 Bromochloromethane 10 12.1 121 70-130
75-27-4 Bromodichloromethane 10 12.8 128 70-130
75-25-2 Bromoform 10 12.1 121 70-130
78-93-3 2-Butanone (MEK)50 56.5 113 70-130
104-51-8 n-Butylbenzene 10 12.0 120 70-130
135-98-8 sec-Butylbenzene 10 12.7 127 70-130
98-06-6 tert-Butylbenzene 10 12.1 121 70-130
56-23-5 Carbon Tetrachloride 10 13.5 135*70-130
108-90-7 Chlorobenzene 10 12.0 120 70-130
75-00-3 Chloroethane 10 12.8 128 60-140
67-66-3 Chloroform 10 12.5 125 70-130
95-49-8 o-Chlorotoluene 10 12.0 120 70-130
106-43-4 p-Chlorotoluene 10 11.8 118 70-130
124-48-1 Dibromochloromethane 10 12.0 120 70-130
106-93-4 1,2-Dibromoethane 10 11.5 115 70-130
75-71-8 Dichlorodifluoromethane 10 10.2 102 60-140
95-50-1 1,2-Dichlorobenzene 10 11.9 119 70-130
541-73-1 1,3-Dichlorobenzene 10 12.2 122 70-130
106-46-7 1,4-Dichlorobenzene 10 11.9 119 70-130
75-34-3 1,1-Dichloroethane 10 13.3 133*70-130
107-06-2 1,2-Dichloroethane 10 12.2 122 70-130
75-35-4 1,1-Dichloroethylene 10 13.5 135*70-130
156-59-2 cis-1,2-Dichloroethylene 10 12.8 128 70-130
156-60-5 trans-1,2-Dichloroethylene 10 13.3 133*70-130
78-87-5 1,2-Dichloropropane 10 11.9 119 70-130
142-28-9 1,3-Dichloropropane 10 11.5 115 70-130
594-20-7 2,2-Dichloropropane 10 12.9 129 70-130
563-58-6 1,1-Dichloropropene 10 12.7 127 70-130
10061-01-5 cis-1,3-Dichloropropene 10 11.3 113 70-130
10061-02-6 trans-1,3-Dichloropropene 10 12.0 120 70-130
108-20-3 Di-Isopropyl Ether 10 11.7 117 70-130
64-17-5 Ethyl Alcohol 500 827 165*70-130
100-41-4 Ethylbenzene 10 12.3 123 70-130
* = Outside of Control Limits.
49 of 81
FA8455655.2.3
Blank Spike Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2879-BS A0225880.D 1 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
591-78-6 2-Hexanone 50 60.3 121 70-130
98-82-8 Isopropylbenzene 10 12.4 124 70-130
99-87-6 p-Isopropyltoluene 10 12.6 126 70-130
74-83-9 Methyl Bromide 10 12.4 124 60-140
74-87-3 Methyl Chloride 10 11.9 119 60-140
75-09-2 Methylene Chloride 10 12.3 123 70-130
108-10-1 4-Methyl-2-pentanone (MIBK)50 54.4 109 70-130
1634-04-4 Methyl Tert Butyl Ether 10 11.0 110 70-130
91-20-3 Naphthalene 10 11.4 114 70-130
103-65-1 n-Propylbenzene 10 12.2 122 70-130
100-42-5 Styrene 10 11.7 117 70-130
630-20-6 1,1,1,2-Tetrachloroethane 10 11.9 119 70-130
79-34-5 1,1,2,2-Tetrachloroethane 10 11.4 114 70-130
127-18-4 Tetrachloroethylene 10 13.4 134*70-130
108-88-3 Toluene 10 12.1 121 70-130
87-61-6 1,2,3-Trichlorobenzene 10 11.9 119 70-130
120-82-1 1,2,4-Trichlorobenzene 10 11.9 119 70-130
71-55-6 1,1,1-Trichloroethane 10 12.9 129 70-130
79-00-5 1,1,2-Trichloroethane 10 11.9 119 70-130
79-01-6 Trichloroethylene 10 12.7 127 70-130
75-69-4 Trichlorofluoromethane 10 12.9 129 60-140
96-18-4 1,2,3-Trichloropropane 10 11.5 115 70-130
95-63-6 1,2,4-Trimethylbenzene 10 11.6 116 70-130
108-67-8 1,3,5-Trimethylbenzene 10 12.2 122 70-130
108-05-4 Vinyl Acetate 50 47.0 94 70-130
75-01-4 Vinyl Chloride 10 11.8 118 60-140
m,p-Xylene 20 24.6 123 70-130
95-47-6 o-Xylene 10 11.9 119 70-130
1330-20-7 Xylene (total)30 36.4 121 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 102%70-130%
17060-07-0 1,2-Dichloroethane-D4 102%70-130%
2037-26-5 Toluene-D8 99%70-130%
* = Outside of Control Limits.
50 of 81
FA8455655.2.3
Blank Spike Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA2879-BS A0225880.D 1 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 96%70-130%
* = Outside of Control Limits.
51 of 81
FA8455655.2.3
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84556-4MS E106536.D 250 04/14/21 LR n/a n/a VE2454
FA84556-4MSD E106537.D 250 04/14/21 LR n/a n/a VE2454
FA84556-4 E106529.D 250 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
FA84556-4 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
67-64-1 Acetone ND 12500 12500 100 12500 12400 99 1 70-130/20
71-43-2 Benzene 7380 2500 9970 104 2500 9820 98 2 70-130/20
108-86-1 Bromobenzene ND 2500 2280 91 2500 2400 96 5 70-130/20
74-97-5 Bromochloromethane ND 2500 2270 91 2500 2330 93 3 70-130/20
75-27-4 Bromodichloromethane ND 2500 2390 96 2500 2490 100 4 70-130/20
75-25-2 Bromoform ND 2500 2030 81 2500 2110 84 4 70-130/20
78-93-3 2-Butanone (MEK)ND 12500 10900 87 12500 10800 86 1 70-130/20
104-51-8 n-Butylbenzene ND 2500 2360 94 2500 2430 97 3 70-130/20
135-98-8 sec-Butylbenzene ND 2500 2530 101 2500 2580 103 2 70-130/20
98-06-6 tert-Butylbenzene ND 2500 2380 95 2500 2460 98 3 70-130/20
56-23-5 Carbon Tetrachloride ND 2500 2550 102 2500 2650 106 4 70-130/20
108-90-7 Chlorobenzene ND 2500 2350 94 2500 2420 97 3 70-130/20
75-00-3 Chloroethane ND 2500 2340 94 2500 2640 106 12 60-140/20
67-66-3 Chloroform ND 2500 2450 98 2500 2520 101 3 70-130/20
95-49-8 o-Chlorotoluene ND 2500 2370 95 2500 2460 98 4 70-130/20
106-43-4 p-Chlorotoluene ND 2500 2270 91 2500 2380 95 5 70-130/20
124-48-1 Dibromochloromethane ND 2500 2200 88 2500 2270 91 3 70-130/20
106-93-4 1,2-Dibromoethane 49.5 J 2500 2220 87 2500 2270 89 2 70-130/20
75-71-8 Dichlorodifluoromethane ND 2500 1880 75 2500 2180 87 15 60-140/20
95-50-1 1,2-Dichlorobenzene ND 2500 2300 92 2500 2340 94 2 70-130/20
541-73-1 1,3-Dichlorobenzene ND 2500 2340 94 2500 2420 97 3 70-130/20
106-46-7 1,4-Dichlorobenzene ND 2500 2270 91 2500 2360 94 4 70-130/20
75-34-3 1,1-Dichloroethane ND 2500 2650 106 2500 2750 110 4 70-130/20
107-06-2 1,2-Dichloroethane 267 2500 2590 93 2500 2630 95 2 70-130/20
75-35-4 1,1-Dichloroethylene ND 2500 2780 111 2500 2890 116 4 70-130/20
156-59-2 cis-1,2-Dichloroethylene ND 2500 2450 98 2500 2520 101 3 70-130/20
156-60-5 trans-1,2-Dichloroethylene ND 2500 2610 104 2500 2690 108 3 70-130/20
78-87-5 1,2-Dichloropropane ND 2500 2280 91 2500 2410 96 6 70-130/20
142-28-9 1,3-Dichloropropane ND 2500 2150 86 2500 2230 89 4 70-130/20
594-20-7 2,2-Dichloropropane ND 2500 2470 99 2500 2560 102 4 70-130/20
563-58-6 1,1-Dichloropropene ND 2500 2430 97 2500 2540 102 4 70-130/20
10061-01-5 cis-1,3-Dichloropropene ND 2500 2080 83 2500 2210 88 6 70-130/20
10061-02-6 trans-1,3-Dichloropropene ND 2500 2180 87 2500 2320 93 6 70-130/20
108-20-3 Di-Isopropyl Ether ND 2500 2290 92 2500 2370 95 3 70-130/20
64-17-5 Ethyl Alcohol ND 125000 154000 123 125000 135000 108 13 70-130/20
100-41-4 Ethylbenzene 1710 2500 4210 100 2500 4230 101 0 70-130/20
* = Outside of Control Limits.
52 of 81
FA8455655.3.1
Matrix Spike/Matrix Spike Duplicate Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84556-4MS E106536.D 250 04/14/21 LR n/a n/a VE2454
FA84556-4MSD E106537.D 250 04/14/21 LR n/a n/a VE2454
FA84556-4 E106529.D 250 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
FA84556-4 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
591-78-6 2-Hexanone 822 J 12500 11500 85 12500 11500 85 0 70-130/20
98-82-8 Isopropylbenzene 148 2500 2600 98 2500 2670 101 3 70-130/20
99-87-6 p-Isopropyltoluene ND 2500 2440 98 2500 2570 103 5 70-130/20
74-83-9 Methyl Bromide ND 2500 2410 96 2500 2780 111 14 60-140/20
74-87-3 Methyl Chloride ND 2500 2170 87 2500 2380 95 9 60-140/20
75-09-2 Methylene Chloride ND 2500 2170 87 2500 2220 89 2 70-130/20
108-10-1 4-Methyl-2-pentanone (MIBK)404 J 12500 11700 90 12500 11600 90 1 70-130/20
1634-04-4 Methyl Tert Butyl Ether ND 2500 2330 93 2500 2410 96 3 70-130/20
91-20-3 Naphthalene 243 2500 2480 89 2500 2570 93 4 70-130/20
103-65-1 n-Propylbenzene 208 2500 2610 96 2500 2690 99 3 70-130/20
100-42-5 Styrene ND 2500 2240 90 2500 2310 92 3 70-130/20
630-20-6 1,1,1,2-Tetrachloroethane ND 2500 2340 94 2500 2410 96 3 70-130/20
79-34-5 1,1,2,2-Tetrachloroethane ND 2500 2150 86 2500 2240 90 4 70-130/20
127-18-4 Tetrachloroethylene ND 2500 2550 102 2500 2620 105 3 70-130/20
108-88-3 Toluene 11600 2500 14100 100 2500 13800 88 2 70-130/20
87-61-6 1,2,3-Trichlorobenzene ND 2500 2270 91 2500 2350 94 3 70-130/20
120-82-1 1,2,4-Trichlorobenzene ND 2500 2350 94 2500 2390 96 2 70-130/20
71-55-6 1,1,1-Trichloroethane ND 2500 2550 102 2500 2630 105 3 70-130/20
79-00-5 1,1,2-Trichloroethane ND 2500 2250 90 2500 2340 94 4 70-130/20
79-01-6 Trichloroethylene ND 2500 2370 95 2500 2430 97 3 70-130/20
75-69-4 Trichlorofluoromethane ND 2500 2440 98 2500 2830 113 15 60-140/20
96-18-4 1,2,3-Trichloropropane ND 2500 2150 86 2500 2260 90 5 70-130/20
95-63-6 1,2,4-Trimethylbenzene 1550 2500 3950 96 2500 3970 97 1 70-130/20
108-67-8 1,3,5-Trimethylbenzene 410 2500 2870 98 2500 2920 100 2 70-130/20
108-05-4 Vinyl Acetate ND 12500 9850 79 12500 9860 79 0 70-130/20
75-01-4 Vinyl Chloride ND 2500 2080 83 2500 2470 99 17 60-140/20
m,p-Xylene 6190 5000 11300 102 5000 11300 102 0 70-130/20
95-47-6 o-Xylene 2190 2500 4610 97 2500 4610 97 0 70-130/20
1330-20-7 Xylene (total)8380 7500 15900 100 7500 15900 100 0 70-130/20
CAS No.Surrogate Recoveries MS MSD FA84556-4 Limits
1868-53-7 Dibromofluoromethane 101%101%98%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%103%102%70-130%
2037-26-5 Toluene-D8 101%101%100%70-130%
* = Outside of Control Limits.
53 of 81
FA8455655.3.1
Matrix Spike/Matrix Spike Duplicate Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84556-4MS E106536.D 250 04/14/21 LR n/a n/a VE2454
FA84556-4MSD E106537.D 250 04/14/21 LR n/a n/a VE2454
FA84556-4 E106529.D 250 04/14/21 LR n/a n/a VE2454
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-4
CAS No.Surrogate Recoveries MS MSD FA84556-4 Limits
460-00-4 4-Bromofluorobenzene 96%97%99%70-130%
* = Outside of Control Limits.
54 of 81
FA8455655.3.1
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84483-13MS A0225862.D 200 04/14/21 LR n/a n/a VA2878
FA84483-13MSD A0225863.D 200 04/14/21 LR n/a n/a VA2878
FA84483-13 A0225854.D 200 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
FA84483-13 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
67-64-1 Acetone ND 10000 9110 91 10000 9700 97 6 70-130/20
71-43-2 Benzene 947 2000 3230 114 2000 3320 119 3 70-130/20
108-86-1 Bromobenzene ND 2000 2100 105 2000 2190 110 4 70-130/20
74-97-5 Bromochloromethane ND 2000 2070 104 2000 2180 109 5 70-130/20
75-27-4 Bromodichloromethane ND 2000 2220 111 2000 2360 118 6 70-130/20
75-25-2 Bromoform ND 2000 2060 103 2000 2190 110 6 70-130/20
78-93-3 2-Butanone (MEK)ND 10000 8940 89 10000 9480 95 6 70-130/20
104-51-8 n-Butylbenzene ND 2000 2010 101 2000 2140 107 6 70-130/20
135-98-8 sec-Butylbenzene ND 2000 2160 108 2000 2300 115 6 70-130/20
98-06-6 tert-Butylbenzene ND 2000 2110 106 2000 2200 110 4 70-130/20
56-23-5 Carbon Tetrachloride ND 2000 2300 115 2000 2450 123 6 70-130/20
108-90-7 Chlorobenzene ND 2000 2090 105 2000 2190 110 5 70-130/20
75-00-3 Chloroethane ND 2000 2220 111 2000 2380 119 7 60-140/20
67-66-3 Chloroform ND 2000 2160 108 2000 2270 114 5 70-130/20
95-49-8 o-Chlorotoluene ND 2000 2170 109 2000 2250 113 4 70-130/20
106-43-4 p-Chlorotoluene ND 2000 2000 100 2000 2110 106 5 70-130/20
124-48-1 Dibromochloromethane ND 2000 2090 105 2000 2180 109 4 70-130/20
106-93-4 1,2-Dibromoethane ND 2000 1980 99 2000 2070 104 4 70-130/20
75-71-8 Dichlorodifluoromethane ND 2000 1810 91 2000 1930 97 6 60-140/20
95-50-1 1,2-Dichlorobenzene ND 2000 2050 103 2000 2140 107 4 70-130/20
541-73-1 1,3-Dichlorobenzene ND 2000 2090 105 2000 2210 111 6 70-130/20
106-46-7 1,4-Dichlorobenzene ND 2000 2020 101 2000 2120 106 5 70-130/20
75-34-3 1,1-Dichloroethane ND 2000 2300 115 2000 2410 121 5 70-130/20
107-06-2 1,2-Dichloroethane ND 2000 2050 103 2000 2180 109 6 70-130/20
75-35-4 1,1-Dichloroethylene ND 2000 2310 116 2000 2430 122 5 70-130/20
156-59-2 cis-1,2-Dichloroethylene ND 2000 2200 110 2000 2330 117 6 70-130/20
156-60-5 trans-1,2-Dichloroethylene ND 2000 2280 114 2000 2420 121 6 70-130/20
78-87-5 1,2-Dichloropropane ND 2000 2060 103 2000 2160 108 5 70-130/20
142-28-9 1,3-Dichloropropane ND 2000 1950 98 2000 2060 103 5 70-130/20
594-20-7 2,2-Dichloropropane ND 2000 2140 107 2000 2210 111 3 70-130/20
563-58-6 1,1-Dichloropropene ND 2000 2180 109 2000 2320 116 6 70-130/20
10061-01-5 cis-1,3-Dichloropropene ND 2000 1940 97 2000 2050 103 6 70-130/20
10061-02-6 trans-1,3-Dichloropropene ND 2000 2050 103 2000 2150 108 5 70-130/20
108-20-3 Di-Isopropyl Ether ND 2000 2030 102 2000 2150 108 6 70-130/20
64-17-5 Ethyl Alcohol ND 100000 90700 91 100000 110000 110 19 70-130/20
100-41-4 Ethylbenzene 1340 2000 3680 117 2000 3690 118 0 70-130/20
* = Outside of Control Limits.
55 of 81
FA8455655.3.2
Matrix Spike/Matrix Spike Duplicate Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84483-13MS A0225862.D 200 04/14/21 LR n/a n/a VA2878
FA84483-13MSD A0225863.D 200 04/14/21 LR n/a n/a VA2878
FA84483-13 A0225854.D 200 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
FA84483-13 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
591-78-6 2-Hexanone ND 10000 9900 99 10000 10600 106 7 70-130/20
98-82-8 Isopropylbenzene 68.4 J 2000 2210 107 2000 2310 112 4 70-130/20
99-87-6 p-Isopropyltoluene ND 2000 2160 108 2000 2280 114 5 70-130/20
74-83-9 Methyl Bromide ND 2000 2640 132 2000 2690 135 2 60-140/20
74-87-3 Methyl Chloride ND 2000 2170 109 2000 2310 116 6 60-140/20
75-09-2 Methylene Chloride ND 2000 2160 108 2000 2280 114 5 70-130/20
108-10-1 4-Methyl-2-pentanone (MIBK)ND 10000 9140 91 10000 9800 98 7 70-130/20
1634-04-4 Methyl Tert Butyl Ether ND 2000 1940 97 2000 2040 102 5 70-130/20
91-20-3 Naphthalene 596 2000 2680 104 2000 2730 107 2 70-130/20
103-65-1 n-Propylbenzene 190 2000 2310 106 2000 2410 111 4 70-130/20
100-42-5 Styrene ND 2000 2050 103 2000 2160 108 5 70-130/20
630-20-6 1,1,1,2-Tetrachloroethane ND 2000 2090 105 2000 2170 109 4 70-130/20
79-34-5 1,1,2,2-Tetrachloroethane ND 2000 1950 98 2000 2030 102 4 70-130/20
127-18-4 Tetrachloroethylene ND 2000 2290 115 2000 2410 121 5 70-130/20
108-88-3 Toluene 5600 2000 8520 146* a 2000 8320 136* a 2 70-130/20
87-61-6 1,2,3-Trichlorobenzene ND 2000 2040 102 2000 2130 107 4 70-130/20
120-82-1 1,2,4-Trichlorobenzene ND 2000 2040 102 2000 2140 107 5 70-130/20
71-55-6 1,1,1-Trichloroethane ND 2000 2230 112 2000 2360 118 6 70-130/20
79-00-5 1,1,2-Trichloroethane ND 2000 2050 103 2000 2160 108 5 70-130/20
79-01-6 Trichloroethylene ND 2000 2200 110 2000 2310 116 5 70-130/20
75-69-4 Trichlorofluoromethane ND 2000 2230 112 2000 2400 120 7 60-140/20
96-18-4 1,2,3-Trichloropropane ND 2000 1970 99 2000 2020 101 3 70-130/20
95-63-6 1,2,4-Trimethylbenzene 2660 2000 5000 117 2000 4990 117 0 70-130/20
108-67-8 1,3,5-Trimethylbenzene 787 2000 2990 110 2000 3060 114 2 70-130/20
108-05-4 Vinyl Acetate ND 10000 7960 80 10000 8530 85 7 70-130/20
75-01-4 Vinyl Chloride ND 2000 2110 106 2000 2250 113 6 60-140/20
m,p-Xylene 5860 4000 11100 131*4000 11000 129 1 70-130/20
95-47-6 o-Xylene 3170 2000 5680 126 2000 5640 124 1 70-130/20
1330-20-7 Xylene (total)9030 6000 16800 130 6000 16600 126 1 70-130/20
CAS No.Surrogate Recoveries MS MSD FA84483-13 Limits
1868-53-7 Dibromofluoromethane 102%102%99%70-130%
17060-07-0 1,2-Dichloroethane-D4 100%101%101%70-130%
2037-26-5 Toluene-D8 101%100%99%70-130%
* = Outside of Control Limits.
56 of 81
FA8455655.3.2
Matrix Spike/Matrix Spike Duplicate Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84483-13MS A0225862.D 200 04/14/21 LR n/a n/a VA2878
FA84483-13MSD A0225863.D 200 04/14/21 LR n/a n/a VA2878
FA84483-13 A0225854.D 200 04/14/21 LR n/a n/a VA2878
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-1, FA84556-2
CAS No.Surrogate Recoveries MS MSD FA84483-13 Limits
460-00-4 4-Bromofluorobenzene 97%96%98%70-130%
(a) Outside control limits due to high level in sample relative to spike amount.
* = Outside of Control Limits.
57 of 81
FA8455655.3.2
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84560-7MS A0225893.D 20 04/15/21 LR n/a n/a VA2879
FA84560-7MSD A0225894.D 20 04/15/21 LR n/a n/a VA2879
FA84560-7 A0225888.D 20 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
FA84560-7 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
67-64-1 Acetone ND 1000 656 66*1000 803 80 20 70-130/20
71-43-2 Benzene 110 200 327 109 200 372 131*13 70-130/20
108-86-1 Bromobenzene ND 200 197 99 200 229 115 15 70-130/20
74-97-5 Bromochloromethane ND 200 201 101 200 227 114 12 70-130/20
75-27-4 Bromodichloromethane ND 200 214 107 200 243 122 13 70-130/20
75-25-2 Bromoform ND 200 191 96 200 223 112 15 70-130/20
78-93-3 2-Butanone (MEK)ND 1000 813 81 1000 1000 100 21*70-130/20
104-51-8 n-Butylbenzene 9.1 J 200 206 98 200 240 115 15 70-130/20
135-98-8 sec-Butylbenzene 5.2 J 200 214 104 200 249 122 15 70-130/20
98-06-6 tert-Butylbenzene ND 200 200 100 200 233 117 15 70-130/20
56-23-5 Carbon Tetrachloride ND 200 218 109 200 251 126 14 70-130/20
108-90-7 Chlorobenzene ND 200 202 101 200 235 118 15 70-130/20
75-00-3 Chloroethane ND 200 243 122 200 244 122 0 60-140/20
67-66-3 Chloroform ND 200 217 109 200 247 124 13 70-130/20
95-49-8 o-Chlorotoluene ND 200 225 113 200 261 131*15 70-130/20
106-43-4 p-Chlorotoluene ND 200 192 96 200 223 112 15 70-130/20
124-48-1 Dibromochloromethane ND 200 196 98 200 226 113 14 70-130/20
106-93-4 1,2-Dibromoethane ND 200 186 93 200 215 108 14 70-130/20
75-71-8 Dichlorodifluoromethane ND 200 200 100 200 198 99 1 60-140/20
95-50-1 1,2-Dichlorobenzene ND 200 196 98 200 226 113 14 70-130/20
541-73-1 1,3-Dichlorobenzene ND 200 198 99 200 231 116 15 70-130/20
106-46-7 1,4-Dichlorobenzene ND 200 194 97 200 225 113 15 70-130/20
75-34-3 1,1-Dichloroethane ND 200 226 113 200 256 128 12 70-130/20
107-06-2 1,2-Dichloroethane ND 200 201 101 200 229 115 13 70-130/20
75-35-4 1,1-Dichloroethylene ND 200 227 114 200 259 130 13 70-130/20
156-59-2 cis-1,2-Dichloroethylene ND 200 210 105 200 243 122 15 70-130/20
156-60-5 trans-1,2-Dichloroethylene ND 200 223 112 200 255 128 13 70-130/20
78-87-5 1,2-Dichloropropane ND 200 202 101 200 228 114 12 70-130/20
142-28-9 1,3-Dichloropropane ND 200 185 93 200 216 108 15 70-130/20
594-20-7 2,2-Dichloropropane ND 200 203 102 200 227 114 11 70-130/20
563-58-6 1,1-Dichloropropene ND 200 213 107 200 243 122 13 70-130/20
10061-01-5 cis-1,3-Dichloropropene ND 200 185 93 200 214 107 15 70-130/20
10061-02-6 trans-1,3-Dichloropropene ND 200 195 98 200 223 112 13 70-130/20
108-20-3 Di-Isopropyl Ether ND 200 197 99 200 226 113 14 70-130/20
64-17-5 Ethyl Alcohol ND 10000 8250 83 10000 12900 129 44*70-130/20
100-41-4 Ethylbenzene 522 200 761 120 200 867 173* a 13 70-130/20
* = Outside of Control Limits.
58 of 81
FA8455655.3.3
Matrix Spike/Matrix Spike Duplicate Summary Page 2 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84560-7MS A0225893.D 20 04/15/21 LR n/a n/a VA2879
FA84560-7MSD A0225894.D 20 04/15/21 LR n/a n/a VA2879
FA84560-7 A0225888.D 20 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
FA84560-7 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
591-78-6 2-Hexanone ND 1000 898 90 1000 1070 107 17 70-130/20
98-82-8 Isopropylbenzene 31.5 200 236 102 200 275 122 15 70-130/20
99-87-6 p-Isopropyltoluene 3.9 J 200 209 103 200 244 120 15 70-130/20
74-83-9 Methyl Bromide ND 200 281 141*200 256 128 9 60-140/20
74-87-3 Methyl Chloride ND 200 230 115 200 241 121 5 60-140/20
75-09-2 Methylene Chloride ND 200 210 105 200 241 121 14 70-130/20
108-10-1 4-Methyl-2-pentanone (MIBK)ND 1000 835 84 1000 1000 100 18 70-130/20
1634-04-4 Methyl Tert Butyl Ether ND 200 179 90 200 207 104 15 70-130/20
91-20-3 Naphthalene 367 200 545 89 200 619 126 13 70-130/20
103-65-1 n-Propylbenzene 118 200 328 105 200 375 129 13 70-130/20
100-42-5 Styrene 3.0 J 200 195 96 200 226 112 15 70-130/20
630-20-6 1,1,1,2-Tetrachloroethane ND 200 195 98 200 224 112 14 70-130/20
79-34-5 1,1,2,2-Tetrachloroethane ND 200 188 94 200 217 109 14 70-130/20
127-18-4 Tetrachloroethylene ND 200 216 108 200 251 126 15 70-130/20
108-88-3 Toluene 136 200 345 105 200 395 130 14 70-130/20
87-61-6 1,2,3-Trichlorobenzene ND 200 206 103 200 237 119 14 70-130/20
120-82-1 1,2,4-Trichlorobenzene ND 200 204 102 200 235 118 14 70-130/20
71-55-6 1,1,1-Trichloroethane ND 200 215 108 200 244 122 13 70-130/20
79-00-5 1,1,2-Trichloroethane ND 200 201 101 200 234 117 15 70-130/20
79-01-6 Trichloroethylene ND 200 213 107 200 243 122 13 70-130/20
75-69-4 Trichlorofluoromethane ND 200 247 124 200 252 126 2 60-140/20
96-18-4 1,2,3-Trichloropropane ND 200 186 93 200 215 108 14 70-130/20
95-63-6 1,2,4-Trimethylbenzene 724 200 958 117 200 1090 183* a 13 70-130/20
108-67-8 1,3,5-Trimethylbenzene 229 200 444 108 200 510 141*14 70-130/20
108-05-4 Vinyl Acetate ND 1000 730 73 1000 875 88 18 70-130/20
75-01-4 Vinyl Chloride ND 200 226 113 200 234 117 3 60-140/20
m,p-Xylene 551 400 1010 115 400 1150 150*13 70-130/20
95-47-6 o-Xylene 200 200 413 107 200 474 137*14 70-130/20
1330-20-7 Xylene (total)751 600 1420 112 600 1620 145*13 70-130/20
CAS No.Surrogate Recoveries MS MSD FA84560-7 Limits
1868-53-7 Dibromofluoromethane 101%101%100%70-130%
17060-07-0 1,2-Dichloroethane-D4 102%101%105%70-130%
2037-26-5 Toluene-D8 98%99%98%70-130%
* = Outside of Control Limits.
59 of 81
FA8455655.3.3
Matrix Spike/Matrix Spike Duplicate Summary Page 3 of 3
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84560-7MS A0225893.D 20 04/15/21 LR n/a n/a VA2879
FA84560-7MSD A0225894.D 20 04/15/21 LR n/a n/a VA2879
FA84560-7 A0225888.D 20 04/15/21 LR n/a n/a VA2879
The QC reported here applies to the following samples:Method: SM 6200B
FA84556-3
CAS No.Surrogate Recoveries MS MSD FA84560-7 Limits
460-00-4 4-Bromofluorobenzene 96%95%96%70-130%
(a) Outside control limits due to high level in sample relative to spike amount.
* = Outside of Control Limits.
60 of 81
FA8455655.3.3
SGS North America Inc.
GC Volatiles
QC Data Summaries
Includes the following where applicable:
• Method Blank Summaries
• Blank Spike Summaries
• Matrix Spike and Duplicate Summaries
Orlando, FL
Section 6
61 of 81
FA845566
Method Blank Summary Page 1 of 1
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
G1S209-MB 1S6146.D 1 04/19/21 BJ n/a n/a G1S209
The QC reported here applies to the following samples:Method: MADEP VPH REV 2.1
FA84556-1, FA84556-2, FA84556-3, FA84556-4
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 1.0 1.0 ug/l
100-41-4 Ethylbenzene ND 2.0 1.0 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 2.0 1.0 ug/l
91-20-3 Naphthalene ND 5.0 3.0 ug/l
108-88-3 Toluene ND 2.0 1.0 ug/l
m,p-Xylene ND 4.0 2.0 ug/l
95-47-6 o-Xylene ND 2.0 1.0 ug/l
C5- C8 Aliphatics (Unadj.)ND 100 35 ug/l
C9- C12 Aliphatics (Unadj.)ND 100 35 ug/l
C9- C10 Aromatics (Unadj.)ND 100 35 ug/l
C5- C8 Aliphatics ND 100 35 ug/l
C9- C12 Aliphatics ND 100 35 ug/l
C9- C10 Aromatics ND 100 35 ug/l
CAS No.Surrogate Recoveries Limits
460-00-4 BFB 98%70-130%
460-00-4 BFB 101%70-130%
62 of 81
FA8455666.1.1
Blank Spike/Blank Spike Duplicate Summary Page 1 of 1
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
G1S209-BS 1S6144.D 1 04/19/21 BJ n/a n/a G1S209
G1S209-BSD 1S6145.D 1 04/19/21 BJ n/a n/a G1S209
The QC reported here applies to the following samples:Method: MADEP VPH REV 2.1
FA84556-1, FA84556-2, FA84556-3, FA84556-4
Spike BSP BSP BSD BSD Limits
CAS No.Compound ug/l ug/l %ug/l %RPD Rec/RPD
71-43-2 Benzene 80 70.4 88 78.1 98 10 70-130/25
100-41-4 Ethylbenzene 80 70.9 89 79.8 100 12 70-130/25
1634-04-4 Methyl Tert Butyl Ether 80 75.9 95 85.2 107 12 70-130/25
91-20-3 Naphthalene 80 71.1 89 80.2 100 12 70-130/25
108-88-3 Toluene 80 68.9 86 77.1 96 11 70-130/25
m,p-Xylene 160 142 89 160 100 12 70-130/25
95-47-6 o-Xylene 80 72.1 90 80.3 100 11 70-130/25
C5- C8 Aliphatics (Unadj.)240 192 80 211 88 9 70-130/25
C9- C12 Aliphatics (Unadj.)160 142 89 155 97 9 70-130/25
C9- C10 Aromatics (Unadj.)80 74.9 94 76.7 96 2 70-130/25
C9- C10 Aromatics 80 74.9 94 76.7 96 2 70-130/25
CAS No.Surrogate Recoveries BSP BSD Limits
460-00-4 BFB 103%108%70-130%
460-00-4 BFB 107%114%70-130%
* = Outside of Control Limits.
63 of 81
FA8455666.2.1
Matrix Spike Summary Page 1 of 1
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84556-2MS 1S6152.D 1 04/19/21 BJ n/a n/a G1S209
FA84556-2 1S6147.D 1 04/19/21 BJ n/a n/a G1S209
The QC reported here applies to the following samples:Method: MADEP VPH REV 2.1
FA84556-1, FA84556-2, FA84556-3, FA84556-4
FA84556-2 Spike MS MS
CAS No.Compound ug/l Q ug/l ug/l %Limits
71-43-2 Benzene ND 80 85.7 107 70-130
100-41-4 Ethylbenzene ND 80 86.3 108 70-130
1634-04-4 Methyl Tert Butyl Ether 2.1 80 86.3 105 70-130
91-20-3 Naphthalene ND 80 77.0 96 70-130
108-88-3 Toluene ND 80 84.6 106 70-130
m,p-Xylene ND 160 172 108 70-130
95-47-6 o-Xylene ND 80 85.7 107 70-130
C5- C8 Aliphatics (Unadj.)ND 480 550 115 70-130
C9- C12 Aliphatics (Unadj.)ND 400 409 102 70-130
C9- C10 Aromatics (Unadj.)ND 240 243 101 70-130
C9- C10 Aromatics ND 240 243 101 70-130
CAS No.Surrogate Recoveries MS FA84556-2 Limits
460-00-4 BFB 101%100%70-130%
460-00-4 BFB 106%104%70-130%
* = Outside of Control Limits.
64 of 81
FA8455666.3.1
Duplicate Summary Page 1 of 1
Job Number:FA84556
Account:RENCM Resolve Environmental
Project:Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA84556-2DUP 1S6148.D 1 04/19/21 BJ n/a n/a G1S209
FA84556-2 1S6147.D 1 04/19/21 BJ n/a n/a G1S209
The QC reported here applies to the following samples:Method: MADEP VPH REV 2.1
FA84556-1, FA84556-2, FA84556-3, FA84556-4
FA84556-2 DUP
CAS No.Compound ug/l Q ug/l Q RPD Limits
71-43-2 Benzene ND ND nc 50
100-41-4 Ethylbenzene ND ND nc 50
1634-04-4 Methyl Tert Butyl Ether 2.1 2.1 0 50
91-20-3 Naphthalene ND ND nc 50
108-88-3 Toluene ND ND nc 50
m,p-Xylene ND ND nc 50
95-47-6 o-Xylene ND ND nc 50
C5- C8 Aliphatics (Unadj.)ND ND nc 50
C9- C12 Aliphatics (Unadj.)ND ND nc 50
C9- C10 Aromatics (Unadj.)ND ND nc 50
C5- C8 Aliphatics ND ND nc 50
C9- C12 Aliphatics ND ND nc 50
C9- C10 Aromatics ND ND nc 50
CAS No.Surrogate Recoveries DUP FA84556-2 Limits
460-00-4 BFB 105%100%70-130%
460-00-4 BFB 110%104%70-130%
* = Outside of Control Limits.
65 of 81
FA8455666.4.1
SGS North America Inc.
Metals Analysis
QC Data Summaries
Includes the following where applicable:
• Method Blank Summaries
• Matrix Spike and Duplicate Summaries
• Blank Spike and Lab Control Sample Summaries
• Serial Dilution Summaries
Orlando, FL
Section 7
66 of 81
FA845567
BLANK RESULTS SUMMARY
Part 2 - Method Blanks
Login Number: FA84556
Account: RENCM - Resolve Environmental
Project: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
QC Batch ID: MP38791 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 04/12/21
MB
Metal RL IDL MDL raw final
Aluminum 200 14 14
Antimony 6.0 1 1
Arsenic 10 1.3 1.3
Barium 200 1 1
Beryllium 4.0 .2 .2
Cadmium 5.0 .2 .2
Calcium 1000 50 50
Chromium 10 1 1
Cobalt 50 .2 .2
Copper 25 1 1
Iron 300 17 17
Lead 5.0 1 1.1 0.20 <5.0
Magnesium 5000 35 35
Manganese 15 .5 1
Molybdenum 50 .3 .3
Nickel 40 .4 .4
Potassium 10000 200 200
Selenium 10 2.4 2.9
Silver 10 .7 .7
Sodium 10000 500 500
Strontium 10 .5 .5
Thallium 10 1.1 1.4
Tin 50 .9 1
Titanium 10 .5 1
Vanadium 50 .5 .6
Zinc 20 3 4.4
Associated samples MP38791: FA84556-1, FA84556-2, FA84556-3, FA84556-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
_________________________________________________________________________________________________________
Page 1
67 of 81
FA8455677.1.1
MATRIX SPIKE AND DUPLICATE RESULTS SUMMARY
Login Number: FA84556
Account: RENCM - Resolve Environmental
Project: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
QC Batch ID: MP38791 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 04/12/21 04/12/21
FA84556-1 QC FA84556-1 Spikelot QC
Metal Original DUP RPD Limits Original MS MPFLICP2 % Rec Limits
Aluminum
Antimony
Arsenic anr
Barium anr
Beryllium
Cadmium anr
Calcium
Chromium anr
Cobalt
Copper
Iron
Lead 1.2 0.0 200.0(a) 0-20 1.2 486 500 97.0 80-120
Magnesium
Manganese
Molybdenum
Nickel
Potassium
Selenium anr
Silver anr
Sodium
Strontium
Thallium
Tin
Titanium
Vanadium
Zinc anr
Associated samples MP38791: FA84556-1, FA84556-2, FA84556-3, FA84556-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(N) Matrix Spike Rec. outside of QC limits
(anr) Analyte not requested
(a) RPD acceptable due to low duplicate and sample concentrations.
_________________________________________________________________________________________________________
Page 1
68 of 81
FA8455677.1.2
MATRIX SPIKE AND DUPLICATE RESULTS SUMMARY
Login Number: FA84556
Account: RENCM - Resolve Environmental
Project: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
QC Batch ID: MP38791 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 04/12/21
FA84556-1 Spikelot MSD QC
Metal Original MSD MPFLICP2 % Rec RPD Limit
Aluminum
Antimony
Arsenic anr
Barium anr
Beryllium
Cadmium anr
Calcium
Chromium anr
Cobalt
Copper
Iron
Lead 1.2 481 500 96.0 1.0 20
Magnesium
Manganese
Molybdenum
Nickel
Potassium
Selenium anr
Silver anr
Sodium
Strontium
Thallium
Tin
Titanium
Vanadium
Zinc anr
Associated samples MP38791: FA84556-1, FA84556-2, FA84556-3, FA84556-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(N) Matrix Spike Rec. outside of QC limits
(anr) Analyte not requested
_________________________________________________________________________________________________________
Page 2
69 of 81
FA8455677.1.2
SPIKE BLANK AND LAB CONTROL SAMPLE SUMMARY
Login Number: FA84556
Account: RENCM - Resolve Environmental
Project: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
QC Batch ID: MP38791 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 04/12/21
BSP Spikelot QC
Metal Result MPFLICP2 % Rec Limits
Aluminum
Antimony
Arsenic anr
Barium anr
Beryllium
Cadmium anr
Calcium
Chromium anr
Cobalt
Copper
Iron
Lead 483 500 96.6 80-120
Magnesium
Manganese
Molybdenum
Nickel
Potassium
Selenium anr
Silver anr
Sodium
Strontium
Thallium
Tin
Titanium
Vanadium
Zinc anr
Associated samples MP38791: FA84556-1, FA84556-2, FA84556-3, FA84556-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
_________________________________________________________________________________________________________
Page 1
70 of 81
FA8455677.1.3
SERIAL DILUTION RESULTS SUMMARY
Login Number: FA84556
Account: RENCM - Resolve Environmental
Project: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
QC Batch ID: MP38791 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 04/12/21
FA84556-1 QC
Metal Original SDL 1:5 %DIF Limits
Aluminum
Antimony
Arsenic anr
Barium anr
Beryllium
Cadmium anr
Calcium
Chromium anr
Cobalt
Copper
Iron
Lead 1.20 0.00 100.0(a) 0-10
Magnesium
Manganese
Molybdenum
Nickel
Potassium
Selenium anr
Silver anr
Sodium
Strontium
Thallium
Tin
Titanium
Vanadium
Zinc anr
Associated samples MP38791: FA84556-1, FA84556-2, FA84556-3, FA84556-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
(a) Percent difference acceptable due to low initial sample concentration (< 50 times IDL).
_________________________________________________________________________________________________________
Page 1
71 of 81
FA8455677.1.4
POST DIGESTATE SPIKE SUMMARY
Login Number: FA84556
Account: RENCM - Resolve Environmental
Project: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
QC Batch ID: MP38791 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 04/12/21
Sample Final FA84556-1 PS Spike Spike Spike QC
Metal ml ml Raw Corr.** ug/l ml ug/ml ug/l % Rec Limits
Aluminum
Antimony
Arsenic
Barium
Beryllium
Cadmium
Calcium
Chromium
Cobalt
Copper
Iron
Lead 9.8 10 1.2 1.176 44.6 0.2 2.5 50 86.8 80-120
Magnesium
Manganese
Molybdenum
Nickel
Potassium
Selenium
Silver
Sodium
Strontium
Thallium
Tin
Titanium
Vanadium
Zinc
Associated samples MP38791: FA84556-1, FA84556-2, FA84556-3, FA84556-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(**) Corr. sample result = Raw * (sample volume / final volume)
(anr) Analyte not requested
_________________________________________________________________________________________________________
Page 1
72 of 81
FA8455677.1.5
SGS North America Inc.
Misc. Forms
Custody Documents and Other Forms
(SGS Scott, LA)
Includes the following where applicable:
• Chain of Custody
Orlando, FL
Section 8
73 of 81
FA845568
FA84556: Chain of Custody
Page 1 of 3
SGS Scott, LA
74 of 81
FA8455688.1
FA84556: Chain of Custody
Page 2 of 3
75 of 81
FA8455688.1
SGS Sample Receipt Summary
Job Number:FA84556 Client:SGS NORTH AMERICA (FL)
Date / Time Received:4/10/2021 9:25:00 AM Delivery Method:FedEx
Project:KWICK MART
4. No. Coolers:1
Airbill #'s:5061 4506 4663
Cooler Security
1. Custody Seals Present:
Y or N
2. Custody Seals Intact:
3. COC Present:
4. Smpl Dates/Time OK
2. Thermometer ID:
Cooler Temperature Y or N
1. Temp criteria achieved:
3. Cooler media:
DV462;
Ice (direct contact)
Quality Control Preservation Y or N N/A
1. Trip Blank present / cooler:
2. Trip Blank listed on COC:
3. Samples preserved properly:
4. VOCs headspace free:
Sample Integrity - Documentation Y or N
1. Sample labels present on bottles:
2. Container labeling complete:
3. Sample container label / COC agree:
Sample Integrity - Condition Y or N
1. Sample recvd within HT:
3. Condition of sample:
2. All containers accounted for:
Sample Integrity - Instructions
1. Analysis requested is clear:
2. Bottles received for unspecified tests
3. Sufficient volume recvd for analysis:
4. Compositing instructions clear:
5. Filtering instructions clear:
Intact
Y or N
Comments
Y or N N/A
Cooler Temps (Initial/Adjusted):#1: (4.9/4.9); DV462
FA84556: Chain of Custody
Page 3 of 3
76 of 81
FA8455688.1
SGS North America Inc.
GC Volatiles
QC Data Summaries
(SGS Scott, LA)
Includes the following where applicable:
• Method Blank Summaries
• Blank Spike Summaries
• Matrix Spike and Duplicate Summaries
Orlando, FL
Section 9
77 of 81
FA845569
Method Blank Summary Page 1 of 1
Job Number:FA84556
Account:ALSE SGS Orlando, FL
Project:RENCM: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP18400-MB LI132619.D 1 04/12/21 AA 04/12/21 OP18400 GLI1085
The QC reported here applies to the following samples:Method: EPA 504.1
FA84556-1, FA84556-2, FA84556-3
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.020 0.0038 ug/l
CAS No.Surrogate Recoveries Limits
348-51-6 1-Chloro-2-fluorobenzene 102%70-130%
78 of 81
FA8455699.1.1
Method Blank Summary Page 1 of 1
Job Number:FA84556
Account:ALSE SGS Orlando, FL
Project:RENCM: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP18409-MB LI132650.D 1 04/14/21 PC 04/14/21 OP18409 GLI1086
The QC reported here applies to the following samples:Method: EPA 504.1
FA84556-4
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.020 0.0038 ug/l
CAS No.Surrogate Recoveries Limits
348-51-6 1-Chloro-2-fluorobenzene 101%70-130%
79 of 81
FA8455699.1.2
Blank Spike/Blank Spike Duplicate Summary Page 1 of 1
Job Number:FA84556
Account:ALSE SGS Orlando, FL
Project:RENCM: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP18400-BS LI132620.D 1 04/12/21 AA 04/12/21 OP18400 GLI1085
OP18400-BSD LI132621.D 1 04/12/21 AA 04/12/21 OP18400 GLI1085
The QC reported here applies to the following samples:Method: EPA 504.1
FA84556-1, FA84556-2, FA84556-3
Spike BSP BSP BSD BSD Limits
CAS No.Compound ug/l ug/l %ug/l %RPD Rec/RPD
106-93-4 1,2-Dibromoethane 0.251 0.24 95 0.24 95 0 70-130/20
CAS No.Surrogate Recoveries BSP BSD Limits
348-51-6 1-Chloro-2-fluorobenzene 100%103%70-130%
* = Outside of Control Limits.
80 of 81
FA8455699.2.1
Blank Spike/Blank Spike Duplicate Summary Page 1 of 1
Job Number:FA84556
Account:ALSE SGS Orlando, FL
Project:RENCM: Kwick Mart; 10308 Albemarle Rd, Mint Hill, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP18409-BS LI132651.D 1 04/14/21 PC 04/14/21 OP18409 GLI1086
OP18409-BSD LI132652.D 1 04/14/21 PC 04/14/21 OP18409 GLI1086
The QC reported here applies to the following samples:Method: EPA 504.1
FA84556-4
Spike BSP BSP BSD BSD Limits
CAS No.Compound ug/l ug/l %ug/l %RPD Rec/RPD
106-93-4 1,2-Dibromoethane 0.251 0.26 103 0.25 99 4 70-130/20
CAS No.Surrogate Recoveries BSP BSD Limits
348-51-6 1-Chloro-2-fluorobenzene 102%98%70-130%
* = Outside of Control Limits.
81 of 81
FA8455699.2.2