MO-4625_15635_CA_MRP_20230113

2725 E. Millbrook Road, Suite 121
Raleigh, NC 27604
Telephone [phone]
www.atcgroupservices.com

January 13, 2023

Mr. Dan Bowser
North Carolina Department of Environmental Quality
Division of Waste Management – Underground Storage Tank Section
610 East Center Avenue, Suite 301
Mooresville, North Carolina 28115

Subject: Active Remediation Monitoring Report
Former Star-Brite Laundry Facility
Phillips 66 RM No. 0528
5639 Statesville Road
Charlotte, North Carolina 28269
ATC Project No. P660528016

Dear Mr. Bowser:

ATC Associates of North Carolina, P.C., on behalf of Phillips 66 Company, is submitting this Active Remediation
Monitoring Report for Phillips 66 Risk Management Site No. 0528, former Star-Brite Laundry Facility. This
report includes information regarding the groundwater monitoring results and site activities for the period of July
2022 through December 2022.

If you have any questions or require additional information, please contact our office at
[phone].

Sincerely,
ATC Associates of North Carolina, P.C.

Brian Buchanan Gabriel Araos, P.E.
Project Scientist Branch Manager
Direct Line: 919-573-1203 Direct Line: 919-573-1205
Email: [e-mail] Email: [e-mail]

Attachments:
1. Active Remediation Monitoring Report

cc: Mr. Ed Kuhn– Contract Program Manager for Phillips 66 Company

Prepared for:

Phillips 66 Company
222 S Church Street, Suite 400
Charlotte, North Carolina 28202

ACTIVE REMEDIATION MONITORING REPORT
FORMER STAR-BRITE LAUNDRY FACILITY
PHILLIPS 66 RM SITE No. 0528
5639 STATESVILLE ROAD
CHARLOTTE, MECKLENBURG COUNTY, NORTH CAROLINA

ATC Project No. P660528016

Prepared by:

ATC Associates of North Carolina, P.C.
2725 E. Millbrook Road, Suite 121
Raleigh, North Carolina 27604
Telephone [phone]

Brian Buchanan
Project Scientist
Direct Line: 919-573-1203
Email: [e-mail]

Gabriel Araos, P.E.
Branch Manager
Direct Line: 919-573-1205
Email: [e-mail]

January 13, 2023

Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
NORTH CAROLINA DEPARTMENT OF ENVIRONMENAL QUALITY
Division of Waste Management, Underground Storage Tank Section
GROUNDWATER PUMP & TREAT REMEDIATION SITE DATA SHEET

PART A
(To be completed with each submission)

Background

Site Name: Former Star-Brite Laundry Facility Incident No.: 15635 Date: 1/13/2023
Location: 5639 Statesville Road, Charlotte, North Carolina 28269
Region: Mooresville County: Mecklenburg Date Release Identified: 11/1995
Responsible Party: Phillips 66 Company
Date CAP Completed: 06/1998 with New Technology Cleanup Plan submitted 11/2012

PART B
(To be completed for initial report or to update information previously provided)

Hydrogeology

Description of Aquifer Lithology: Clayey silts & clay to 70 ft bls
Is bedrock aquifer/fractured saprolite impacted? Describe: Yes. There is current impact to the bedrock
aquifer, with MTBE and 1,2-DCA exceeding 2L standards.

Average Hydraulic Conductivity (ft./day): 1.55 Average Groundwater Gradient (%): 1.6%
How were above determined? Slug tests, water levels, and pumping test
Major Pumping Influences which may Affect GW flow: Nearby WSWs servicing greenhouse and residential
WSWs
Distance from Site: WSWs 110’ to 300’ in various directions Pumping Rate: WSWs uncertain

Location and Distance from site of Nearest Supply Well(s): WSW-1 and WSW-2 (Oakdale Greenhouse
LLC) 200’ east, WSW-3 230’ northeast, WSW-4 200’ northwest, WSW-5 110’ west, WSW-6 110’ northwest,
and WSW-7 300’ west.

Description of Release

Type of Product: Petroleum Estimated Volume Released: Unknown
Average Plume Dimensions (ft.)--Width: 80 Length: 100 Depth Interval: 20' –135’
Ranges of Concentrations from CSA: Maximum benzene conc.=32,000 ppb; max MTBE=53,800 ppb; max
1,2-DCA=200 ppb; Current max benzene concentration = 0.19 J µg/L; max MTBE = 52.7 µg/L; max 1,2-
DCA = 1.6 µg/L

Emergency Response/Initial Remedial Actions

Date Source Removed/Repaired: November 1995 - Tank Closure
Free Product Recovered (gal.): N/A
Soil Excavation (tons): 600 Average Contaminant Concentration (mg/kg): >120,000
Type of Treatment or Disposal: Off-site treatment by bioremediation at licensed facility/recycling for use in
asphalt manufacturing.

Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
Remediation

Goals of Remediation: Groundwater extraction

Description of Treatment System: Low profile air stripper and particle filters.

Pilot test conducted? (Type) Slug test and step test
Date: June 13, 2012 and April 30 to May 1, 2014, respectively
Method of System Effluent Disposal: NPDES Permit No. NCG 510000
No. of Monitoring Wells: 12 (current monitoring wells)
Monitoring Schedule: Semi-annual
Date GW System Started: 7/31/14
No. of Recovery Wells: 3 (wells RW-1 and RW-3 are active, well RW-2 is inactive)

Are any other remediation systems used in conjunction with Pump & Treat? No Describe: NA.

PART C
SYSTEM PERFORMANCE MONITORING
(To be completed with each submission)

PERIOD OF OPERATION

Report
for

07

/

01

/

22

to

12

/

31

/

22
Days of Operation this
Period:

183 (approx).

SYSTEM DOWNTIME SUMMARY (current reporting period only)

Month Reason

July - December 2022

Routine scheduled maintenance during bi-weekly O&M visits.

FREE PRODUCT RECOVERY

Total Gallons Recovered Since Last Report: 0 gallons

Total Gallons Recovered to Date: 0
Well I.D.: N/A

Air Sparge and Soil Vapor Extraction remedial system in operation between February 2000 and November
2011. System decommissioned and a New Technology Cleanup Plan was submitted November 2012.
Pump and treat system was started July 31, 2014.
Recovery Well Flowrate
(GPM)
Drawdown
(ft.)
Radius of Influence
(ft.)
Pump
Type/Capacity

RW-1

3

40

75
Centrifugal/20
gpm

RW-3

3

40

Not established
Centrifugal/20
gpm
Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
INFLUENT & EFFLUENT CONCENTRATION DATA - TREATMENT SYSTEM

Gallons Treated Since Last Report: 528,800 (06/21/2022 – 12/20/2022)

Total Gallons Treated To Date: 9,500,231 (12/20/2022)

Parameter/Units:
Influent MTBE (RW/1/RW-3: 20.1 µg/L /43.3 µg/L) sampled 07/18/22; Influent MTBE (RW/1/RW-3: <0.13
µg/L /45.7 µg/L) sampled 10/25/22; Effluent MTBE (<0.13 µg/L) sampled 07/18/22; Effluent MTBE (<0.13
µg/L) sampled 10/25/22.

Attach additional sheet(s) as needed:

COMMENTS:
Influent and Effluent samples are collected on a quarterly basis.

Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023
Page i

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
Table of Contents
1.0 SITE IDENTIFICATION .......................................................................................................................... 1
2.0 EXECUTIVE SUMMARY ........................................................................................................................ 1
3.0 INTRODUCTION ..................................................................................................................................... 1
4.0 SITE BACKGROUND ............................................................................................................................ 1
5.0 GROUNDWATER CHARACTERIZATION ........................................................................................... 2
5.1 GROUNDWATER LEVELS...................................................................................................................................... 2
5.2 GROUNDWATER QUALITY ................................................................................................................................... 3
5.3 WATER SUPPLY WELLS ....................................................................................................................................... 3
6.0 REMEDIATION SYSTEM OPERATIONS AND MAINTENANCE ...................................................... 4
6.1 REMEDIAL SYSTEM ............................................................................................................................................ 4
6.2 SYSTEM SAMPLING ............................................................................................................................................ 4
7.0 PLAN AND SCHEDULE ........................................................................................................................ 4
7.1 SITE ACTIVITIES ................................................................................................................................................. 4
8.0 SUMMARY, CONCLUSIONS, AND RECOMMENDATIONS ............................................................. 5
9.0 REPORT LIMITATIONS ......................................................................................................................... 5

TABLES:
Table 1 - Well Construction Details
Table 2 - Groundwater Elevation Data
Table 3 - Current Groundwater Analytical Results
Table 4 - Historical Groundwater Analytical Results
Table 5 - Water Supply Well Information
Table 6 - Water Supply Well Analytical Results
Table 7 - Remedial System Sampling

FIGURES:
Figure 1 - Site Location Map
Figure 2 - Site Map
Figure 3a - Shallow Groundwater Elevation Contour Map – October 25, 2022
Figure 3b - Deep Groundwater Elevation Contour Map – October 25, 2022
Figure 4 - Dissolved Methyl Tertiary Butyl Ether Isoconcentration Map
Figure 5 - Dissolved 1,2-DCA Isoconcentration Map
Figure 6 - Water Supply Well Location Map

GRAPHS:
Graph 1 - MTBE Influent Concentration Trend Graph – RW-3

APPENDICES:
Appendix A - Laboratory Analytical Reports (Monitoring and Supply Well Sampling)
Appendix B - Laboratory Analytical Reports (NPDES System Sampling)

Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023
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Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
2.0 EXECUTIVE SUMMARY

ATC Associates of North Carolina, P.C. (ATC) has completed an Active Remediation Monitoring Report for
Former Star-Brite Laundry Facility. This report documents groundwater monitoring results and site activities
for the period of July 2022 through December 2022.

The former Star-Brite Laundry Facility is located at 5639 Statesville Road, Charlotte, North Carolina. The
site consists of a single-story Ice-cream store with parking and landscaped areas. The site remediation
system is located to the west of the existing single-story building. The property is currently owned by Mr.
Johnny Keziah and Ms. Frances Keziah and occupied by Pelican’s Snoballs.

ATC performed a semi-annual groundwater sampling event in October 2022 that consisted of the collection
of groundwater samples from site monitoring and recovery wells, and from vicinity water supply wells. The
collected data indicated that groundwater samples from monitoring wells MW-1A, MW-4D, MW-9A, MW-
10D, and recovery wells RW-1 and RW-3 contained dissolved concentrations that exceeded the
corresponding 2L Standards for at least one or more constituent(s). No constituents were detected above
North Carolina GCLs during the October 2022 sampling event.

Chloroform was detected in the samples from water supply wells WSW-1, WSW-2, and WSW-3 at levels
consistent with prior detections.

Influent samples for RW-1/RW-3 and effluent samples were collected in July and October 2022. No
constituents from either of the quarterly effluent samples collected during the reporting period exceeded
their allowable limits by the NPDES permit.

ATC is currently performing bi-weekly O&M visits at the site to ensure proper remedial system operation.
The P&T system continues to be effective in the removal of petroleum-impacted groundwater.

Based on the October 2022 groundwater monitoring event, ATC recommends continued operation of the
P&T system combined with semiannual groundwater monitoring and quarterly system influent and effluent
sampling. The next semi-annual groundwater monitoring event is scheduled for April 2023.

3.0 INTRODUCTION

Phillips 66 Company (Phillips 66) retained ATC Associates of North Carolina, P.C. (ATC) to provide
environmental consulting services for the former Star-Brite Laundry Facility. The site is located at 5639
Statesville Road, Charlotte, North Carolina. The property consists of a single-story Ice-cream store with
parking and landscaped areas. Most of the eastern part of the site is covered by asphalt pavement, while
most of the western part is covered with landscaped and grass-covered areas. The site remediation system
is located to the west of the existing single-story building. Figure 1 shows the site location on a topographic
map, and a site map showing the locations of the monitoring wells and remediation wells is included as
Figure 2.

The site is situated in a residential and commercial area within the city limits of Charlotte, North Carolina.
The Oakdale Greenhouse facility is located on an adjacent property to the east across Statesville Road.
The remaining vicinity land usage is primarily residential.

4.0 SITE BACKGROUND

In November 1995, seven underground storage tanks (USTs) were removed from the site. The USTs
consisted of three gasoline tanks, one diesel fuel tank, one kerosene tank, one heating oil tank, and one
used oil tank. During the UST closure, approximately 600 tons of impacted soil was removed and disposed.
The petroleum release was reported to the North Carolina Department of Environment and Natural
Resources (NCDENR, currently the North Carolina Department of Environmental Quality [NCDEQ]) in
November 1995.
Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023
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ATC Project No. P660528014 Phillips 66 Company
In August 1997, Rust Environment and Infrastructure (Rust) completed a Comprehensive Site Assessment
(CSA). The CSA indicated that soil and groundwater contamination was confined to the site. In February
1998, the NCDEQ required a Corrective Action Plan (CAP), which was submitted by Rust in June 1998.
The CAP identified air sparging (AS) and soil vapor extraction (SVE) as the most feasible technologies to
remediate the petroleum-impacted soil and groundwater on-site. In February 2000, the AS/SVE system
was started. Enhancements to the AS/SVE system and remediation wells were completed between 2000
and 2003, and a new AS compressor was installed in early 2006. The system provided treatment of on-site
constituents from its activation in 2000 until November 2011, when failure of the SVE equipment occurred.
Because remaining impact was limited to deep overburden and upper bedrock zones beyond the influence
of the remedial system, the NCDEQ UST Section allowed development of a New Technology Cleanup Plan
(NTCP) to address the remaining impact. Additionally, a road-widening project required abandonment of
monitoring and remedial system wells, which would have also disrupted remedial operations.

On November 6, 2012, the NTCP was submitted to the NCDEQ. The NTCP specified a Pump and Treat
(P&T) system to extract and treat groundwater from the deep saprolite and upper bedrock zones with
discharge into a storm drain via a National Pollutant Discharge Elimination System (NPDES) permit. The
NPDES permit for the new P&T system was approved on February 21, 2014. Completion of a stormwater
drop inlet that receives the treated water occurred in June 2014, and the building permit was approved by
Mecklenburg County in July 2014. System start-up occurred on July 31, 2014, with virtually continual
operation thereafter.

In April 2015, ATC supervised the abandonment of vapor extraction wells VE-6 through VE-10 that were
associated with the former AS/SVE system, and monitoring well MW-1R, due to a blockage in the casing.
Following the well abandonments, ATC supervised the installation of site monitoring wells MW-1A, MW-2A,
MW-5A, MW-8A, MW-9A, and MW-11DA. Well MW-1A is a replacement well for well MW-1R, and wells
MW-2A, MW-5A, MW-8A, MW-9A, and MW-11DA are replacement wells for wells that were previously
abandoned for road widening construction along Statesville Road. The road-widening project was
completed during the summer of 2015.

On March 28, 2018, ATC supervised the installation of recovery well RW-3. The boring location was cleared
to 5.5 feet below ground surface (bgs) using air-knife technology and drilled to 68 feet bgs using a hollow
stem auger drill rig. Drilling was stopped at 68 feet bgs due to auger refusal. Recovery well RW-3 was
installed to a total depth of 68 feet bgs, with a 35-foot length of 0.010-inch slotted, 4-inch diameter PVC
well screen extending from 33 to 68 feet bgs, and solid PVC riser casing to the ground surface. The well
was completed at ground surface using a flush-mount, traffic-rated 2-foot by 2-foot well vault secured in
concrete to match existing grade.

On April 25 and 26, 2018, ATC removed the pump from recovery well RW-2 and subsequently
decontaminated the pump prior to installing it in newly installed well RW-3. Recovery well RW-2 was not
abandoned and is used as a groundwater monitoring point during groundwater monitoring events.

The treatment system continues to recover impacted groundwater. Groundwater is recovered from two
recovery wells equipped with electric submersible pumps and is then treated using an air stripper and bag
filters, prior to discharge. The groundwater is discharged in accordance with NPDES General Permit No.
NCG510000.

5.0 GROUNDWATER CHARACTERIZATION

5.1 GROUNDWATER LEVELS

On October 25, 2022, groundwater levels were measured in the site monitoring well network. LNAPL was
not detected in any site wells. Depths were measured from the top of the well casings, which are referenced
to an arbitrary benchmark of 100.00 feet. The October 25, 2022, groundwater contour map for the shallow
saprolite aquifer shows that shallow groundwater flow delineated by wells MW-1A, MW-2A, MW-5A, MW-
6R, and MW-9A has an overall groundwater flow direction to the east-southeast. The groundwater contour
Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023
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ATC Project No. P660528014 Phillips 66 Company
map for the deep fractured rock aquifer shows that deep groundwater flow delineated by wells MW-4D,
MW-10D, MW-11DA, and MW-12D has an overall groundwater flow direction to the west.

Well construction details for the monitoring wells are summarized in Table 1. The locations of the monitoring
wells are shown in Figure 2, and the groundwater elevation data is summarized in Table 2. A groundwater
elevation contour map for the shallow saprolite and deep fractured rock aquifers based on the October
2022 gauging data are included as Figures 3a and 3b.

5.2 GROUNDWATER QUALITY

On October 25, 2022, ATC personnel conducted a groundwater monitoring event of the site well network,
including recovery wells, RW-1, RW-2, and RW-3. The groundwater samples were transported on ice and
under chain-of-custody documentation to North Carolina-accredited SGS-Accutest laboratory located in
Orlando, Florida (North Carolina Lab Certification No. 573). The laboratory could not locate the sample
bottles for MW-9A in the sample cooler; therefore, MW-9A was resampled on November 7, 2022. The
samples were analyzed for volatile organic compounds (VOCs), including benzene, toluene, ethylbenzene,
total xylenes (BTEX), methyl tertiary butyl ether (MTBE), isopropyl ether (IPE), and naphthalene by EPA
Method 6200B and low-level ethylene dibromide (EDB) by EPA Method 504.1. The laboratory report for the
April 2022 sampling event is included in Appendix A.

Groundwater quality results exceeded the NCDEQ Groundwater Quality 2L Standards for the following
constituents and monitoring well locations:
 MTBE (2L Standard of 20 µg/L) in well RW-1 (29.1 µg/L) and RW-3 (38.8 µg/L);
 Naphthalene (2L Standard of 6 µg/L) in well MW-1A (21.2 µg/L) and RW-3 (7.3 µg/L);
 1,2-Dichloroethane (1,2-DCA; 2L Standard of 0.4 µg/L) in wells MW-4D (0.43 µg/L), RW-1 (1.2
µg/L), and RW-3 (2.2 µg/L), and;
 1,2-Dibromoethane (EDB; 2L Standard of 0.02 µg/L) in wells MW-4D (0.077 µg/L), MW-9A (0.043
µg/L), and MW-10D (0.030 µg/L).

None of the detected constituents exceeded their respective GCLs in the site monitoring or recovery wells.
Groundwater analytical results for the October 2022 sampling event are summarized in Table 3, and
historical groundwater analytical results are summarized in Table 4. Isoconcentration maps are provided
for the following constituents: MTBE (Figure 4); and 1,2-DCA (Figure 5).

5.3 WATER SUPPLY WELLS

Correspondence from the NCDEQ, dated April 23, 2003, stated that water supply wells within 500 feet of
the site should be sampled. Information for each property is summarized in Table 5, and the locations of
the properties with water supply wells are shown on Figure 6.

On October 25, 2022, samples were collected from water supply wells, WSW-1 and WSW-2, located at the
Oakdale Nursery property (5626 Statesville Road), and WSW-6 at the Wallace property (6325 Burmith
Avenue). Samples could not be collected at WSW-3, WSW-4, WSW-5, and WSW-7 due to lack of power
at each respective well pump. Each of the properties that contain WSW-3, WSW-4, WSW-5, and WSW-7
are connected to municipal water provided by the City of Charlotte.

The water supply well samples were transported on ice and under chain-of-custody to SGS-Accutest
laboratory located in Orlando, Florida. The water supply well samples were analyzed for VOCs including
BTEX, MTBE, IPE and naphthalene by EPA Method 6200B. Each sample was additionally analyzed for low
level EDB by EPA Method 504.1. The laboratory report is included in Appendix A, and laboratory results
are summarized in Table 6.

Chloroform was detected in water supply wells WSW-1 and WSW-2 at concentrations that did not exceed
the 2L Standard and at levels consistent with prior detections. Chloroform was also detected in water supply
Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023
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ATC Project No. P660528014 Phillips 66 Company
well WSW-6 at a concentration below the 2L Standard and at a level consistent with previous events when
chloroform has been detected.

6.0 REMEDIATION SYSTEM OPERATIONS AND MAINTENANCE

6.1 REMEDIAL SYSTEM

Historically, an air sparge and soil vapor extraction (AS/SVE) system operated on site from February 2000
until 2012. In November 2012, a New Technology Cleanup Plan (NTCP) specifying pump and treat (P&T)
technology was completed and approved by NCDEQ. The remediation wells associated with the AS/SVE
system were abandoned in August 2013, and April 2015. The AS/SVE system was decommissioned and
removed from the site in August 2013.

The new P&T system was delivered to the site in February 2014, following approval of the NPDES permit
on February 21, 2014. Trenching of the discharge line to the drop inlet that now serves as the point of
discharge took place in April 2014. The drop inlet was completed in June 2014 by a third-party road
construction contractor. Following permit approval by Mecklenburg County, the P&T system was started on
July 31, 2014. Bi-weekly O&Ms have been conducted since remedial system startup to ensure proper
system operation.

Recovery well RW-3 was installed at the site to remove petroleum-impacted groundwater and has replaced
recovery well RW-2 as an active recovery well. Recovery well RW-2 will continue to be used as a
groundwater monitoring point. A new submersible pump was installed at RW-3 during the 2019 reporting
period due to pump failure.

From July 1, 2022, through December 31, 2022, the remedial system operated for approximately 183 days
out of a possible 184 days. Minimal system shutdown resulted from routine scheduled maintenance
throughout the reporting period. The average dissolved VOC mass removal during the reporting period
was estimated as 0.23 grams/day.

6.2 SYSTEM SAMPLING

Influent samples for RW-1/RW-3 and effluent samples were collected in July and October 2022. The
samples were sent to SGS Acutest in Orlando, Florida for analysis. Each sample was analyzed by EPA
Method 6200B for VOCs, EPA Method 6010C for lead, and EPA Method SM-20, 2540D for TSS, and tested
for pH as required by the NPDES permit.

No constituents from either of the quarterly effluent samples collected during the reporting period exceeded
their allowable limits by the NPDES permit. The laboratory results for remedial system sampling are
summarized in Table 7 and included in Appendix B, with a Graph following Table 7 showing the trend of
MTBE concentrations vs Time in active recovery well RW-3.

7.0 PLAN AND SCHEDULE

7.1 SITE ACTIVITIES

The next semi-annual sampling event is proposed for April 2023. Monitoring well and water supply well
samples will be analyzed for VOCs (including BTEX, MTBE, IPE, and naphthalene) by EPA Method 6200B
and low level EDB by EPA Method 504.1.

Quarterly treatment system effluent sampling will be conducted in January and April 2023. Each effluent
sample will be analyzed for benzene, ethylbenzene, toluene, total xylenes, 1,2-dichloroethane, MTBE, and
naphthalene by EPA Method 6200B, lead by EPA Method 6010C, and TSS by EPA Method SM-20, 2540D
Former Star-Brite Laundry Facility (RM No. 0528)
January 13, 2023
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ATC Project No. P660528014 Phillips 66 Company
in accordance with the NPDES permit. Active Remediation Monitoring Reports will be submitted semi-
annually. Operation and maintenance for the P&T system will continue to occur on a bi-weekly basis.

8.0 SUMMARY, CONCLUSIONS, AND RECOMMENDATIONS

During this reporting period, bi-weekly maintenance of the P&T remedial system was conducted. ATC
performed a semi-annual groundwater-sampling event in October 2022 that consisted of the collection of
groundwater samples from site monitoring and recovery wells, and from vicinity water supply wells. The
collected data indicated that groundwater samples from monitoring wells MW-1A, MW-4D, MW-9A, MW-
10D, and recovery wells RW-1 and RW-3 contained dissolved concentrations that exceeded the
corresponding 2L Standards for at least one or more constituent(s). No constituents were detected above
North Carolina GCLs during the October 2022 sampling event. Chloroform was detected in the samples
from water supply wells WSW-1, WSW-2, and WSW-3 at levels consistent with prior detections.

MTBE is the primary contaminant of concern. The highest MTBE concentrations are typically present in the
eastern portion of the site in an area defined by wells RW-1, RW-3, and MW-9A. MTBE concentrations in
well RW-2 have been below the 2L Standard since the April 2016 groundwater monitoring event. The
highest MTBE concentrations have been detected in the groundwater samples collected from recovery well
RW-3, which is an active recovery well with the current remedial system.

The P&T system continues to be effective in the removal of petroleum-impacted groundwater. Based on
the October 2022 groundwater monitoring event, ATC recommends continued operation of the P&T system
combined with semiannual groundwater monitoring and quarterly system influent and effluent sampling.
The next semi-annual groundwater monitoring event is scheduled for April 2023.

9.0 REPORT LIMITATIONS

This investigation is intended to be a non-biased assessment of on-site environmental conditions proximate
to the location of the former and/or current UST system. Subsurface investigative and remedial
methodologies were performed in general accordance with applicable state and federal regulatory
requirements. The information presented in this report is based upon site-specific observations, generally
accepted geological and environmental consulting practices, and analytical results for environmental
samples collected at the time the field investigation was performed. The data presented in this report are
believed to represent subsurface conditions at the facility; however, data may not be completely
representative of subsurface conditions at every location. ATC assumes no liability arising from
environmental impact to, or from, the site, regardless of the date of impact occurrence or findings.

Former Star-Brite Laundry Facility (RM No. 0528)

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
TABLES
TABLE 1
WELL CONSTRUCTION DETAILS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Well Total Well Screen TOC
Monitoring Construction Abandonment Diameter Depth Interval Elevation
Well Date Date (inches)(feet)(feet)(feet)
MW-1R Mar. 2001 April 2015 2 35 15-35 99.26
MW-1A April 2015 ---2 35 15-35 99.73
MW-2R Mar. 2001 Nov. 2012 2 35 15-35 99.48
MW-2A April 2015 ---2 35 15-35 100.11
MW-3R Mar. 2001 ---2 35 15-35 99.82
MW-4D June 1997 ---2 81 76-81 99.42
MW-5R Mar. 2001 Nov. 2012 2 35 15-35 99.02
MW-5A April 2015 ---2 35 15-35 99.78
MW-6R Feb. 2002 ---2 35 15-35 99.36
MW-7 June 1997 ---2 25 10-25 99.05
MW-8 June 1997 Nov. 2012 2 25 10-25 98.63
MW-8A April 2015 ---2 35 15-35 99.30
MW-9R Mar. 2001 Nov. 2012 2 35 15-35 99.27
MW-9A April 2015 ---2 35 15-35 99.33
MW-10D Aug. 2007 ---2 115 105-115 99.29
MW-11D Aug. 2007 Nov. 2012 2 91 81-91 100.01
MW-11DA April 2015 ---2 90 80-90 99.68
MW-12D Aug. 2007 ---2 128 118-128 99.78
Well Total Well Screen TOC
Recovery Construction Abandonment Diameter Depth Interval Elevation
Well Date Date (inches)(feet)(feet)(feet)
RW-1 4/3/2013 ---4 85 65-85 ---
RW-2 4/8/2013 ---4 130 110-130 ---
RW-3 3/28/2018 ---4 68 33-68 ---
Notes:
TOC = Top of Casing
Elevations are referenced to an arbitrary on-site benchmark of 100.00 feet
Page 1 of 1
TABLE 2
GROUNDWATER ELEVATION DATA
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No: 15635
RM No: 0528
05/02/08 19.89 79.37
10/08/08 21.41 77.85
04/07/09 23.86 75.40
10/12/09 24.12 75.14
04/20/10 13.49 85.77
10/06/10 27.94 71.32
04/26/11 20.99 78.27
10/14/11 25.07 74.19
04/16/12 23.55 75.71
10/19/12 27.36 71.90
05/02/13 14.19 85.07
10/15/13 NS NS
05/19/14 NS NS
10/06/14 NS NS
05/19/15
05/19/15 24.76 74.97
10/07/15 29.89 69.84
04/12/16 24.12 75.61
10/18/16 29.35 70.38
04/05/17 28.8 70.93
10/18/17 29.98 69.75
04/05/18 28.18 71.55
10/16/18 28.78 70.95
04/22/19 17.94 81.79
10/28/19 22.37 77.36
05/20/20 15.50 84.23
11/19/20 19.00 80.73
04/15/21 11.95 87.78
10/28/21 22.85 76.88
04/28/22 20.69 79.04
10/25/22 28.32 71.41
05/02/08 18.99 80.49
10/08/08 21.45 78.03
04/07/09 31.81 67.67
10/12/09 24.15 75.33
04/19/10 13.56 85.92
10/06/10 32.55 66.93
04/26/11 21.06 78.42
10/14/11 24.98 74.50
04/16/12 21.10 78.38
10/19/12 27.29 72.19
05/02/13
05/19/15 24.14 75.97
10/07/15 29.68 70.43
04/12/16 23.41 76.70
10/18/16 28.44 71.67
04/05/17 28.30 71.81
10/18/17 29.49 70.62
04/05/18 27.48 72.63
10/16/18 28.15 71.96
04/22/19 16.91 83.20
10/28/19 22.00 78.11
05/20/20 14.45 85.66
11/19/20 18.24 81.87
04/15/21 11.10 89.01
10/28/21 23.20 76.91
04/28/22 20.93 79.18
10/25/22 27.83 72.28
100.11
99.73
Well Abandoned
MW-1A
MW-2A
99.26
99.48
Groundwater
Elevation
(feet)
Monitoring Well Sample Date
Depth To
Groundwater
(feet)
TOC Elevation
(feet)
Well Abandoned
MW-2R
MW-1R
Page 1 of 7
TABLE 2
GROUNDWATER ELEVATION DATA
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No: 15635
RM No: 0528
Groundwater
Elevation
(feet)
Monitoring Well Sample Date
Depth To
Groundwater
(feet)
TOC Elevation
(feet)
05/02/08 19.08 80.74
10/08/08 21.35 78.47
04/07/09 28.18 71.64
10/12/09 24.50 75.32
04/19/10 13.61 86.21
10/06/10 28.79 71.03
04/26/11 21.06 78.76
10/14/11 24.88 74.94
04/16/12 24.80 75.02
10/19/12 27.09 72.73
05/02/13 23.85 75.97
10/15/13 23.57 76.25
05/19/14 16.40 83.42
10/06/14 24.52 75.30
05/19/15 23.58 76.24
10/07/15 29.12 70.70
04/12/16 22.80 77.02
10/18/16 28.19 71.63
04/05/17 27.37 72.45
10/18/17 28.99 70.83
04/05/18 27.16 72.66
10/16/18 27.28 72.54
04/22/19 15.81 84.01
10/28/19 21.74 78.08
05/05/20 13.70 86.12
11/19/20 16.93 82.89
04/15/21 10.48 89.34
10/28/21 23.03 76.79
04/28/22 20.19 79.63
10/25/22 27.51 72.31
05/05/08 19.55 79.87
10/14/08 22.74 76.68
04/07/09 20.75 78.67
10/12/09 23.57 75.85
04/20/10 15.08 84.34
10/06/10 22.67 76.75
04/26/11 21.89 77.53
10/14/11 26.18 73.24
04/16/12 22.84 76.58
10/19/12 27.98 71.44
05/02/13 24.99 74.43
10/15/13 25.57 73.85
05/19/14 17.60 81.82
10/06/14 27.59 71.83
05/19/15 26.41 73.01
10/07/15 31.22 68.20
04/11/16 25.77 73.65
10/18/16 29.53 69.89
04/05/17 29.65 69.77
10/18/17 31.01 68.41
04/05/18 28.98 70.44
10/16/18 29.76 69.66
04/22/19 20.48 78.94
10/28/19 25.42 74.00
05/20/20 19.68 79.74
11/19/20 22.00 77.42
04/15/21 10.84 88.58
10/28/21 23.62 75.80
04/28/22 19.95 79.47
10/25/22 28.66 70.76
MW-4D
MW-3R 99.82
99.42
Page 2 of 7
TABLE 2
GROUNDWATER ELEVATION DATA
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No: 15635
RM No: 0528
Groundwater
Elevation
(feet)
Monitoring Well Sample Date
Depth To
Groundwater
(feet)
TOC Elevation
(feet)
05/02/08 18.41 80.61
10/10/08 21.07 77.95
04/07/09 19.37 79.65
10/13/09 22.91 76.11
04/19/10 12.63 86.39
10/06/10 22.17 76.85
04/26/11 20.11 78.91
04/16/12 20.85 78.17
10/19/12 26.99 72.03
05/02/13
05/19/15 24.74 75.04
10/07/15 30.01 69.77
04/11/16 24.00 75.78
10/18/16 29.40 70.38
04/05/17 28.83 70.95
10/18/17 29.96 69.82
04/05/18 28.10 71.68
10/16/18 28.58 71.20
04/22/19 17.33 82.45
10/28/19 22.14 77.64
05/20/20 15.21 84.57
11/19/20 18.61 81.17
04/15/21 11.54 88.24
10/28/21 23.35 76.43
04/28/22 21.10 78.68
10/25/22 28.09 71.69
05/02/08 18.33 81.03
10/10/08 21.10 78.26
04/06/09 16.85 82.51
10/12/09 23.20 76.16
04/19/10 11.56 87.80
10/06/10 20.96 78.40
04/26/11 20.29 79.07
04/16/12 20.97 78.39
10/19/12 24.66 74.70
05/02/13 23.18 76.18
10/15/13 23.82 75.54
05/19/14 15.45 83.91
10/06/14 23.74 75.62
05/19/15 22.03 77.33
10/07/15 28.68 70.68
04/11/16 20.64 78.72
10/18/16 27.23 72.13
04/05/17 ----
10/19/17 29.12 70.24
04/05/18 25.40 73.96
10/16/18 25.95 73.41
04/22/19 12.96 86.40
10/28/19 21.12 78.24
05/20/20 12.02 87.34
11/19/20 14.24 85.12
04/15/21 9.01 90.35
10/28/21 22.22 77.14
04/28/22 17.75 81.61
10/25/22 26.46 72.90
99.36
Well Abandoned
MW-5A
MW-6R
MW-5R 99.02
99.78
Page 3 of 7
TABLE 2
GROUNDWATER ELEVATION DATA
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No: 15635
RM No: 0528
Groundwater
Elevation
(feet)
Monitoring Well Sample Date
Depth To
Groundwater
(feet)
TOC Elevation
(feet)
05/02/08 19.82 79.23
10/10/08 21.20 77.85
04/06/09 17.34 81.71
10/12/09 23.40 75.65
04/19/10 12.37 86.68
10/06/10 21.27 77.78
04/26/11 21.64 77.41
10/14/11 24.22 74.83
04/16/12 21.34 77.71
10/19/12 24.28 74.77
05/02/13 23.85 75.20
10/15/13 23.88 75.17
05/19/14 15.52 83.53
10/06/14 24.24 74.81
05/19/15 23.55 75.50
10/07/15 24.21 74.84
04/11/16 22.71 76.34
10/18/16 24.39 74.66
04/05/17 DRY ---
10/19/17 DRY ---
04/05/18 DRY ---
10/16/18 DRY ---
04/22/19 15.57 83.48
10/28/19 22.07 76.98
05/20/20 13.55 85.50
11/19/20 17.02 82.03
04/15/21 10.75 88.30
10/28/21 23.80 75.25
04/28/22 21.15 77.90
10/25/22 DRY ---
05/02/08 DRY ---
10/10/08 25.00 73.63
04/06/09 23.12 75.51
10/13/09 23.90 74.73
04/20/10 19.54 79.09
10/06/10 23.86 74.77
04/26/11 DRY DRY
10/14/11 24.71 73.92
04/16/12 24.41 74.22
10/19/12 DRY DRY
05/02/13
05/19/15 24.63 74.67
10/07/15 29.19 70.11
04/11/16 22.54 76.76
10/18/16 28.68 70.62
04/05/17 27.98 71.32
10/18/17 28.31 70.99
04/05/18 26.50 72.80
10/16/18 27.77 71.53
04/22/19 13.92 85.38
10/28/19 23.88 75.42
05/20/20 12.97 86.33
11/19/20 19.43 79.87
04/15/21 9.95 89.35
10/28/21 23.13 76.17
04/28/22 19.85 79.45
10/25/22 27.32 71.98
99.30
99.05MW-7
98.63MW-8
Well Abandoned
MW-8A
Page 4 of 7
TABLE 2
GROUNDWATER ELEVATION DATA
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No: 15635
RM No: 0528
Groundwater
Elevation
(feet)
Monitoring Well Sample Date
Depth To
Groundwater
(feet)
TOC Elevation
(feet)
05/02/08 23.70 75.57
10/10/08 26.31 72.96
04/06/09 23.41 75.86
10/13/09 26.77 72.50
04/20/10 19.38 79.89
10/06/10 25.73 73.54
04/26/11 25.81 73.46
10/14/11 29.66 69.61
04/16/12 25.78 73.49
10/19/12 30.77 68.50
05/02/13
05/19/15 24.79 74.54
10/07/15 29.57 69.76
04/11/16 23.82 75.51
10/18/16 26.68 72.65
04/05/17 28.36 70.97
10/18/17 29.58 69.75
04/05/18 27.49 71.84
10/16/18 28.09 71.24
04/22/19 14.98 84.35
10/28/19 22.97 76.36
05/20/20 13.90 85.43
11/19/20 19.38 79.95
04/15/21 10.19 89.14
10/28/21 22.71 76.62
04/28/22 19.97 79.36
10/25/22 28.03 71.30
05/05/08 19.99 79.30
10/14/08 22.74 76.55
04/07/09 19.49 79.80
10/12/09 24.36 74.93
04/19/10 13.58 85.71
10/06/10 22.90 76.39
04/26/11 21.81 77.48
10/14/11 26.40 72.89
04/16/12 22.12 77.17
10/19/12 28.52 70.77
05/02/13 24.70 74.59
10/15/13 25.51 73.78
05/19/14 17.49 81.80
10/06/14 27.38 71.91
05/19/15 26.32 72.97
10/07/15 31.04 68.25
04/11/16 25.35 73.94
10/18/16 29.82 69.47
04/05/17 29.42 69.87
10/18/17 30.79 68.50
04/05/18 28.77 70.52
10/16/18 28.87 70.42
04/22/19 17.21 82.08
10/28/19 22.97 76.32
05/20/20 15.91 83.38
11/19/20 18.84 80.45
04/15/21 10.93 88.36
10/28/21 23.23 76.06
04/28/22 19.82 79.47
10/25/22 27.80 71.49
99.29
99.33MW-9A
MW-10D
MW-9R
Well Abandoned
99.27
Page 5 of 7
TABLE 2
GROUNDWATER ELEVATION DATA
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No: 15635
RM No: 0528
Groundwater
Elevation
(feet)
Monitoring Well Sample Date
Depth To
Groundwater
(feet)
TOC Elevation
(feet)
05/05/08 19.97 80.04
10/13/08 21.90 78.11
04/07/09 18.75 81.26
10/13/09 23.45 76.56
04/19/10 12.81 87.20
10/06/10 22.23 77.78
04/26/11 21.05 78.96
10/14/11 25.68 74.33
04/16/12 21.10 78.91
10/19/12 27.57 72.44
05/02/13
05/19/15 25.54 74.14
10/07/15 30.68 69.00
04/11/16 24.73 74.95
10/18/16 29.56 70.12
04/05/17 27.91 71.77
10/18/17 30.45 69.23
04/05/18 28.23 71.45
10/16/18 28.67 71.01
04/22/19 16.95 82.73
10/28/19 22.10 77.58
05/20/20 15.58 84.10
11/19/20 18.40 81.28
04/15/21 10.56 89.12
10/28/21 22.85 76.83
04/28/22 19.70 79.98
10/25/22 27.41 72.27
05/05/08 19.34 80.44
10/13/08 22.45 77.33
04/07/09 19.00 80.78
10/12/09 24.03 75.75
04/19/10 13.37 86.41
10/06/10 22.58 77.20
04/26/11 21.85 77.93
10/14/11 26.17 73.61
04/16/12 21.89 77.89
10/19/12 28.53 71.25
05/02/13 24.41 75.37
10/15/13 24.50 75.28
05/19/14 17.88 81.90
10/06/14 26.77 73.01
05/19/15 25.75 74.03
10/07/15 30.27 69.51
04/11/16 24.92 74.86
10/18/16 29.14 70.64
04/05/17 27.3 72.48
10/18/17 30.25 69.53
04/05/18 28.22 71.56
10/16/18 28.29 71.49
04/22/19 16.63 83.15
10/28/19 22.65 77.13
05/20/20 15.38 84.4
11/19/20 18.29 81.49
04/15/21 11.01 88.77
10/28/21 22.90 76.88
04/28/22 19.86 79.92
10/25/22 27.46 72.32
99.68
99.78
MW-11DA
MW-12D
100.01
Well Abandoned
MW-11D
Page 6 of 7
TABLE 2
GROUNDWATER ELEVATION DATA
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No: 15635
RM No: 0528
Groundwater
Elevation
(feet)
Monitoring Well Sample Date
Depth To
Groundwater
(feet)
TOC Elevation
(feet)
10/18/16 66.12 NS
10/16/18 74.73 NS
04/22/19 NA NS
10/28/19 22.44 NS
05/20/20 54.30 NS
11/19/20 51.40 NS
04/15/21 44.63 NS
10/28/21 22.80 NS
04/28/22 20.25 NS
10/25/22 28.00 NS
10/18/16 28.71 NS
10/16/18 28.10 NS
04/22/19 16.93 NS
10/28/19 23.32 NS
05/20/20 14.32 NS
11/19/20 18.10 NS
04/15/21 10.15 NS
10/28/21 22.70 NS
04/28/22 18.77 NS
10/25/22 27.20 NS
04/05/18 28.18 NS
10/16/18 32.85 NS
04/22/19 NA NS
10/28/19 44.01 NS
05/20/20 41.74 NS
11/19/20 40.48 NS
04/15/21 32.45 NS
10/28/21 22.30 NS
04/28/22 21.63 NS
10/25/22 28.35 NS
Notes:
TOC elevations referenced to an arbitrary onsite benchmark of 100.00 feet
NS = Not surveyed
RW-2
RW-3 NS
NS
NSRW-1
All data expressed in feet
Depth to groundwater measured from top of casing
TOC = Top of casing
Page 7 of 7
TABLE 3
CURRENT GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No: 15635
RM No: 0528
504.1
Monitoring
Well
Sampling
Date
Benzene Toluene Ethylbenzene Total Xylenes Total BTEX MTBE Naphthalene n-Butylbenzene sec-Butylbenzene tert-Butylbenzene Chloroethane Chloroform o-Chlorotoluene p-Chlorotoluene 1,2-Dichloroethane Di-Isopropyl Ether 2-Hexanone Isopropylbenzene p-Isopropyltoluene Methyl Bromide Methyl Chloride Methylene Chloride 2-Butanone n-Propylbenzene 1,1,2,2-Tetrachloroethane 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene Acetone 1,2-Dibromoethane (EDB)1 600 600 500 NE 20 6 70 70 70 3,000 70 100 24 0.4 70 400 70 25 10 3 5 4,000 70 0.2 400 400 6,000 0.02
5,000 260,000 80,000 50,000 NE 20,000 6,000 5,900 8,800 14,750 NE 70,000 NE 24,000 400 70,000 40,000 30,500 11,700 10,000 3,000 400,000 4,000,000 26,100 200 28,500 24,100 6,000,000 50
MW-1A 10/25/2022 <0.13 <0.13 1.1 <0.25 1.1 <0.13 21.2 0.40 J 0.24 J <0.13 0.25 J <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 0.46 J <0.13 <0.20 <0.20 <1.0 <1.3 1.5 <0.13 0.14 J 0.20 J 4.4 J <0.0095
MW-2A 11/7/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0096
MW-3R 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 0.40 J <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 0.27 J 2.1 J <0.0096
MW-4D 10/25/2022 0.17 J <0.13 <0.13 <0.25 0.17 J 0.63 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 0.43 J <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 0.077
MW-5A 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0094
MW-6R 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0095
MW-7 10/25/2022
MW-8A 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0097
MW-9A 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 0.34 J <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 2.5 J 0.043
MW-10D 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 0.20 J <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 0.030
MW-11DA 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0095
MW-12D 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0095
RW-1 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND 29.1 0.34 J <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 1.2 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0097
RW-2 10/25/2022 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0097
RW-3 10/25/2022 <0.25 <0.25 <0.25 <0.50 ND 38.8 7.3 <0.25 <0.25 <0.25 <0.40 <0.25 <0.25 <0.25 2.2 <0.25 <2.0 <0.25 <0.25 <0.40 <0.40 4.5 B <2.5 <0.25 <0.25 <0.25 <0.25 5.4 J <0.0097
Notes:
1. "<" or ND = Not detected at or above the method detection limit
2. Concentrations are reported in micrograms per liter (ug/l) or parts per billion (ppb) equivalents
3. 2L Standard = Title 15A NCAC 2L .0202 Groundwater Standard.
4. Values in BOLD indicate levels above 2L Groundwater Standards.
5. BTEX = Benzene, Toluene, Ethylbenzene, and Total Xylenes
6. MTBE = Methyl Tertiary Butyl Ether
7. GCL = Gross Contaminant Level established by NCDEQ.
8. J = Estimated Value
9. B = Indicates analyte found in associated method blank
10. NE = Not Established
GCL
2L Standard
Sample Method EPA 6200B
Not Sampled - Well Dry
Page 1 of 1
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
06/01/96 28,000 31,600 2,150 13,900 75,650 53,800 NA NS 560 NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 29,222 34,000 2,200 11,600 77,022 26,000 NA 320 380 NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 31,000 34,000 1,900 10,100 77,000 34,000 NA 300 330 NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 32,000 35,000 2,000 10,400 79,400 25,000 NA 210 NS NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 32,000 33,000 1,700 9,900 76,600 28,000 NA 320 ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 3,100 3,400 260 1,400 8,160 9,000 NA 70 ND NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 11,000 11,000 530 1,900 24,430 17,000 NA 110 ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/01 870 830 44 239 1983 3,900 NA 22 ND NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 ND ND ND ND NA 6,300 NA 3 ND NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 ND ND ND ND NA 8,500 NA ND ND NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 290 ND ND ND 290 3,000 NA 11 ND NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 720 <100 <100 <200 720 11,000 NA <20 <100 NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 <2 <3 <3 <3 ---7,800 7 <4 <4 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04 32 22 4 28 86 3,900 38 <1 12 NA NA NA NA NA NA NA NA NA NA NA NA
04/18/05 110 5 31 8 154 14,000 55 <1 36 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05 31 13 43 47 134 2,600 <1 5.600 830 NA NA NA NA NA NA NA NA NA NA NA NA
03/29/06 <1 <5 <5 <5 ---640 <5 <1 <5 NA NA 13 NA <1 <1 <2 NA NA NA NA NA
10/05/06 <5 <5 <5 <5 ---1,000 <5 <5 <5 NA NA 15 NA <5 <5 <5 NA NA NA NA NA
03/21/07 <1 <1 <2 <2 ---2,900 3 <2 <2 NA NA <2 NA <2 <2 <4 NA NA NA NA NA
09/27/07 10 <0.7 <0.8 1 11 1,000 1 <1 6 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 17 <50 <50 <100 17 1,200 <50 <0.02 <50 NA NA 35 NA NA NA NA NA NA NA NA NA
10/08/08 1 J <0.7 <0.8 <0.8 1 380 <0.8 0.07 <1 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 35 18 <10 <10 53 2,000 <10 2 <100 NA NA NA NA NA NA NA NA NA NA NA NA
10/12/09 <1 <1 <1 <1 ---1,400 <1 <0.024 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/20/10 4 <2 <2 <4 4 2,200 3 <0.022 <2 NA NA NA NA NA NA NA NA NA NA NA NA
10/20/10 <0.2 <0.2 <0.1 <0.2 ---330 0.22 <0.022 <0.1 <0.1 <0.1 4.0 <0.2 <0.1 <50 <0.2 NA NA <0.1 <0.1 <0.1
04/26/11 <0.1 <0.1 <0.1 <0.1 ---600 0.8 <0.023 <0.1 <0.1 <0.1 8.5 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
10/14/11 <1 <1 <1 <1 ---88 <1 <0.029 <1 <1 <1 <1 <1 <1 <1 <1.6 <0.029 <1 <1 <1 <1
04/16/12 <0.5 <0.5 <0.5 <0.5 ---56 <0.5 <0.029 <0.5 <0.5 <0.5 0.6 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12 <0.1 <0.1 <0.1 <0.5 ---13 <0.1 <0.0097 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.0097 <0.1 <0.1 <0.1 <0.1
05/02/13 <0.5 <0.5 <0.5 <0.5 ---2.9 <0.5 <0.5 <0.5 2.9 1.0 J <0.5 <0.5 <0.5 <0.5 <1.0 <2.5 0.7 J 1 J <0.5 <0.5
10/16/13
05/19/14
10/06/14
05/19/15
2L Standard
GCL
MW-1
MW-1R
NS - Due to blockage in well
NS - Well Dry
NS - Blockage at 15 feet
Well Abandoned
Page 1 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
05/19/15 <0.1 0.8 <0.1 <0.2 0.8 6.1 <0.1 0.015 J <0.1 <0.1 <0.1 0.1 J <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 0.8 <0.1 0.1 J 0.11 J 9.8 <0.1 <0.0096 0.6 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/12/16 0.1 J 0.8 <0.1 0.2 J 1.1 J 3.8 <0.1 0.019 J 1.6 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 0.2 J <0.1
10/19/16 0.17 J 1.4 1.1 10 12.67 23.3 <0.13 0.028 5.0 <0.13 <0.13 0.68 <0.13 <0.13 <0.13 <1.0 <0.13 <0.5 <0.13 1.7 0.93
04/05/17 0.26 J 1.6 2.2 15.8 19.86 23.0 <0.13 0.021 7.9 <0.13 <0.13 <0.13 0.15 J <0.13 <0.13 <0.13 <0.13 <0.13 0.16 J 2.8 1.6
10/18/17 0.24 J 1.2 11.4 94.9 107.74 25.9 <0.13 <0.13 23.3 <0.13 <0.13 <0.13 1.1 <0.13 <0.13 <1.0 NA <0.13 1.7 36.0 16.7
04/05/18 0.18 J 1.2 6.7 49.5 57.58 14.5 <0.13 <0.0090 11.1 <0.13 <0.13 0.22 J 0.70 <0.13 <0.13 <1.0 NA <0.13 1.1 13.0 7.8
10/16/18 0.23 J 1.1 9.7 56.7 67.5 12.4 <0.13 <0.0093 16.8 <0.13 0.13 J 0.31 J 1.30 <0.13 <0.13 <0.20 <0.13 0.17 J 1.9 25.3 16
04/23/19 <0.13 0.81 3.1 18.8 ---3 <0.13 <0.0093 7.2 <0.13 <0.13 <0.13 0.41 J <0.13 <0.13 <1.0 NA <0.13 0.74 14.6 6.9
10/29/19 0.25 J 2.7 17.1 49.6 69.4 3.6 <0.13 <0.13 46.5 0.74 0.69 <0.13 3.0 <0.13 <0.13 <1.0 NA 0.78 6.8 45.2 38.4
05/20/20 <0.13 1.3 2.4 9.8 13.5 1.2 <0.13 <0.0096 37.8 0.86 0.37 J <0.13 0.41 J <0.13 <0.13 <1.0 NA 0.39 J 0.96 15.5 8.4
11/19/20 0.17 J 2.2 4.1 24.8 31.27 0.63 <0.13 <0.13 31.2 2.0 0.75 <0.13 0.75 <0.13 <0.13 <1.0 NA 0.81 2.0 29.3 16.4
04/15/21 0.16 J 0.54 5.1 13.1 18.9 <0.13 <0.13 <0.0038 29.8 1.5 0.68 <0.13 1.2 <0.13 <0.13 <1.0 NA 0.79 3.5 23.5 13.2
10/29/21 0.15 J 0.46 J 3.8 11.9 16.31 <0.13 <0.13 <0.0038 14.1 1.1 0.48 J <0.13 0.73 <0.13 <0.13 <1.0 NA 0.48 J 1.9 14.8 9.2
04/29/22 0.19 J <0.13 2.0 9.6 11.79 <0.13 <0.13 <0.0094 22.3 2.4 0.76 <0.13 0.40 J <0.13 <0.13 <1.0 NA 0.77 1.1 16.7 7.8
10/25/22 <0.13 <0.13 1.1 <0.25 1.1 <0.13 <0.13 <0.0095 21.2 0.40 J 0.24 J <0.13 0.46 J <0.13 <0.13 <1.0 NA <0.13 1.5 0.14 J 0.20 J
06/01/96 NS NS NS NS ---NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 26,000 3,200 1,900 96,000 127,100 7,700 NA 290 410 NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 30,000 36,000 2,100 10,900 79,000 10,000 NA 300 390 NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 32,000 38,000 2,500 13,000 85,500 7,300 NA 210 NS NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 7,700 32,000 2,000 11,600 53,300 ND NA ND ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 140 16 11 30 197 94 NA ND 6 NA NA NA NA NA NA NA NA NA NA NA NA
MW-2
MW-1A
Page 2 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
03/01/01 93 99 13 43 248 530 NA 22 7 NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 430 670 94 430 1,624 690 NA 36 40 NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 ND ND ND 6 6 620 NA ND ND NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 260 22 17 95 394 720 NA 3 ND NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 <5 <5 <5 <10 ---870 NA <0.5 <5 NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 <0.5 <0.7 <0.8 1 1 340 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04 13 <10 <10 37 50 290 <10 <1 <100 NA NA NA NA NA NA NA NA NA NA NA NA
04/18/05 <1 2 <1 14 16 210 <1 <1 32 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05 2 8 33 234 278 130 <1 8.700 310 NA NA NA NA NA NA NA NA NA NA NA NA
03/29/06 <1 <5 <5 <5 ---53 <5 <1 <5 NA NA 3 NA <1 <1 <2 NA NA NA NA NA
10/05/06 <5 <5 <5 <5 ---140 <5 <5 <5 NA NA <5 NA <5 <5 <5 NA NA NA NA NA
03/21/07 <0.5 <0.7 <0.8 <0.8 ---9 <0.8 <1 <1 NA NA <1 NA <1 <0.8 <2 NA NA NA NA NA
09/27/07 6 <0.7 <0.8 <0.8 6 3 <0.8 <1 2 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 <1 1 <5 <10 1 17 <5 <0.02 <5 NA NA <5.0 NA NA <5.0 NA NA NA NA NA NA
10/08/08 <0.5 <0.7 <0.8 <0.8 ---1 J <0.8 <0.0096 <1 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 <1 <1 <1 <1 ---<8 <1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
10/12/09 <1 <1 <1 <1 ---<8 <1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/19/10 <0.1 <0.1 <0.1 <0.2 ---0 <0.1 <0.02 <0.1 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 <0.2 <0.2 <0.1 <0.2 ---<0.2 <0.1 <0.022 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
04/26/11 <0.1 <0.1 <0.1 <0.1 ---1.5 <0.1 <0.021 1.7 B <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
10/14/11 <0.5 0.1 J <0.5 <0.5 0.1 0.4 J <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 0.1 J <0.5 <0.5 <0.8 0.039 <0.5 <0.5 <0.5 <0.5
04/16/12 <0.5 <0.5 <0.5 <0.5 ---0.1 J <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12 <0.1 <0.1 <0.1 <0.1 ---0.7 <0.1 <0.0095 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.0095 <0.1 <0.1 <0.1 <0.1
05/02/13
05/19/15 <0.1 0.2 J <0.1 0.1 J 0.3 J 6.7 <0.1 0.035 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 0.1 J 0.6
10/07/15 <0.2 0.9 J <0.2 <0.2 0.15 J 3.7 <0.2 <0.0096 0.3 J <0.2 <0.2 <0.2 <0.2 <0.2 <0.2 <0.4 1 <0.2 <0.2 <0.2 <0.2
04/12/16 <0.1 0.2 J <0.1 0.4 J 0.6 J 1.7 <0.1 0.012 J 0.2 J <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 1.0 4.4
10/18/16 <0.13 1.4 <0.13 <2.0 1.4 3.1 <0.13 <0.0095 0.15 J <0.13 <0.13 0.25 J <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/05/17 <0.13 1 <0.13 0.14 J 1.14 3.9 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13
10/18/17 <0.13 0.38 J <0.13 <0.25 0.38 5.0 <0.13 <0.13 0.97 <0.13 <0.13 0.20 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.15 J <0.13
04/05/18 <0.13 0.15 J <0.13 0.61 J 1.2 8.5 <0.13 <0.0089 1.6 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.49 J 0.25 J
10/16/18 <0.13 <0.13 <0.13 1.3 J 1.3 4.9 <0.0093 <0.13 0.42 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 0.6 0.25 J
04/22/19 <0.13 <0.13 0.29 J 5.3 5.3 1.5 <0.0093 <0.13 7.8 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 0.34 J 3 0.23 J
10/28/19 <0.13 <0.13 0.19 1.1 1.29 <0.13 <0.13 <0.13 3.4 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 0.14 1.0 <0.13
05/20/20 <0.13 <0.13 <0.13 0.19 J 0.19 J <0.13 <0.13 <0.0095 0.28 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.34 J <0.13
11/20/20 <0.13 <0.13 0.18 J 0.62 J 0.80 0.18 J <0.13 <0.13 4.9 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 0.37 J 2.6 <0.13
04/15/21 <0.13 <0.13 <0.13 0.62 J 0.62 <0.13 <0.13 <0.0037 2.2 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 0.16 J 2.00 0.18 J
10/28/21 <0.13 <0.13 0.15 J <0.25 0.15 <0.13 <0.13 <0.0038 4.9 0.15 J <0.13 <0.13 0.14 J <0.13 <0.13 <1.0 NA <0.13 0.46 J 0.22 J 0.22 J
04/28/22 <0.13 <0.13 <0.13 <0.25 <0.25 <0.13 <0.13 <0.0095 3.8 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 0.17 J 0.52 <0.13
11/07/22 <0.13 <0.13 <0.13 <0.25 <0.25 <0.13 <0.13 <0.0096 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 NA <0.13 <0.13 <0.13 <0.13
Well abandoned
MW-2R
MW-2A
Page 3 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
07/01/96 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 24,000 31,000 2,000 10,400 67,400 34,000 NA 270 350 NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 28,000 36,000 2,600 13,200 79,800 25,000 NA 170 NS NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 350 200 270 1,290 2,110 28,000 NA ND 64 NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 26,000 37,000 2,400 14,700 80,100 9,000 NA 290 ND NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 2 ND ND 1 3 17,000 NA ND ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/01 12,000 22,000 1,600 8,700 44,300 3,900 NA 84 ND NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 11,000 17,000 2,400 8,800 39,200 220 NA 74 710 NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 8,600 16,000 1,000 7,200 32,800 400 NA 78 450 NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 13,000 32,000 2,800 19,600 67,400 ND NA 65 4,200 NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 13,000 21,000 1,000 10,000 45,000 11,000 NA 120 <1,000 NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 1,500 9,400 1,200 8,800 20,900 810 10 140 930 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04 1,400 9,500 1,300 10,300 22,500 750 210 <100 690 NA NA NA NA NA NA NA NA NA NA NA NA
04/18/05 3,200 7,300 1,100 9,300 20,900 2,100 40 <50 930 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05 <250 4,700 2,200 14,600 21,500 <250 <250 <250 2,600 NA NA NA NA NA NA NA NA NA NA NA NA
03/29/06 120 140 21 220 501 430 <5 14 <5 NA NA 8 NA <1 <1 <2 NA NA NA NA NA
10/05/06 200 430 130 900 1,660 500 7 10 150 NA NA 9 NA <5 <5 <5 NA NA NA NA NA
03/21/07 5 390 95 530 1,020 100 1 1 30 NA NA <1 NA <1 <0.8 <2 NA NA NA NA NA
09/27/07 4 2 2 21 29 130 1 1 7 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 4 2 2 23 31 170 <5 0.65 <5 NA NA <5.0 NA NA <5.0 NA NA NA NA NA NA
10/08/08 26 100 120 840 1,086 290 3 J 0.92 170 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 <1 2 <1 5 ---120 1 0.42 <10 NA NA NA NA NA NA NA NA NA NA NA NA
10/12/09 <1 <1 <1 <1 ---100 <1 0.12 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/19/10 <0.1 28 42 300 370 32 <0.1 <0.022 22 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 <0.2 <0.2 <0.1 <0.2 ---17 <0.1 <0.022 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 0.23 0.17
04/26/11 0.11 <0.1 <0.1 0.18 0.29 14 <0.1 <0.021 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
10/14/11 0.2 J 0.5 0.3 J 2.80 3.80 36 <0.5 <0.029 0.7 1.3 0.4 J <0.5 0.4 J <0.5 <0.5 <0.8 <0.029 0.3 J 1.2 6.5 3.9
04/16/12 <0.5 <0.5 <0.5 <0.5 ---3.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12 <0.1 <0.1 <0.1 <0.1 ---0.5 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.0096 <0.1 <0.1 <0.1 <0.1
05/02/13 0.7 0.8 0.2 J 1.2 2.9 J 2.7 <0.1 <0.1 0.7 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 0.1 J 0.9 0.3 J
10/16/13 0.3 J 0.4 J 0.4 J 4.3 5.4 7.2 <0.1 <0.0095 0.9 0.3 J 0.1 J <0.1 0.2 J <0.1 <0.1 <0.2 <0.5 <0.1 0.4 J 2.6 1.6
05/19/14 0.2 J 0.5 2.3 30.2 33.2 J 84 0.1 J 0.087 75 3 1.8 0.2 J 2.7 <0.1 <0.1 <0.2 <0.5 1.5 8.1 57 49
10/06/14 0.2 J 0.8 1.4 22.5 24.9 110 <0.1 0.2 100 3.4 1.6 0.2 J 1.6 <0.1 <0.1 <0.2 <0.5 1.4 4.1 37 44
05/19/15 0.2 J 0.4 J 0.4 J 12.7 13.7 J 79 0.1 J 0.13 55 3.4 1.6 0.2 J 0.9 <0.1 <0.1 <0.2 1.7 J 1.5 2.8 22 50
10/07/15 0.2 J 0.4 J 0.7 15.9 17.2 J 64 0.1 J 0.13 65 3.4 1.6 0.2 J 1.1 <0.1 <0.1 <0.2 0.5 1.4 4 26 44
04/12/16 0.1 J 0.3 J 0.2 J 6.3 J 6.9 J 18 <0.1 0.047 66 1.7 0.9 <0.1 0.5 J <0.1 <0.1 <0.2 <0.5 1.0 1.7 20 42
10/18/16 <0.63 0.7 J 0.81 J 12.7 14.21 27.3 <0.63 0.049 129 1.6 J 1.0 J <0.63 0.77 J <0.63 <0.63 <5.0 <0.63 1.0 J 3.8 24.8 54.1
04/06/17 0.15 J 0.37 J 0.32 J 7.8 8.64 18.4 <0.13 0.054 82.2 1.2 0.79 <0.13 0.66 <0.13 <0.13 <0.13 <0.13 0.97 2.7 14.5 40.9
10/18/17 <0.13 0.19 J 1.1 28.5 29.79 19.4 <0.13 <0.13 411 3.9 2.2 <0.13 2.5 <0.13 <0.13 <1.0 NA 2.9 11.4 43.4 134
04/05/18 0.26 J 0.60 0.43 J 12.8 14.09 14.8 <0.13 0.027 147 2.4 1.6 <0.13 1.2 <0.13 <0.13 <1.0 NA 3.0 5.2 19.6 130
10/16/18 0.40 J 0.61 0.38 J 9.6 10.21 6.4 <0.0093 <0.13 149 <0.13 1.3 <0.13 1.2 <0.13 <0.13 <0.20 <0.13 2.2 4.1 17.5 77.4
04/22/19 <0.13 0.32 J 0.17 J 9.6 10.1 18.8 <0.0093 <0.13 15.2 1.1 0.75 <0.13 0.24 J <0.13 <0.13 <1.0 NA 1.5 0.73 8.2 65.3
10/28/19 <0.13 <0.13 <0.13 1.0 1.0 1.5 <0.13 <0.13 6.5 0.48 0.25 <0.13 <0.13 <0.13 <0.13 <1.0 NA 0.4 0.17 J 3.5 11.6
05/20/20 <0.13 <0.13 <0.13 0.83 J 0.83 J 0.93 <0.13 0.048 12.8 0.60 0.37 J <0.13 <0.13 <0.13 <0.13 <1.0 NA 0.41 J 0.38 J 21.2 17.5
11/20/20 <0.13 <0.13 <0.13 0.28 J 0.28 0.75 <0.13 <0.13 2.7 0.21 J <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.70 4.4
04/15/21 <0.13 <0.13 <0.13 <0.25 ND 0.19 J <0.13 0.068 1.2 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 1.0 1.8
10/28/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0038 1.9 0.13 J <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.8 1.9
04/28/22 <0.13 <0.13 <0.13 <0.25 <0.25 0.67 <0.13 <0.0094 0.34 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.14 J 0.58
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0096 0.40 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 0.27 J
MW-3
MW-3R
Page 4 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
07/01/96 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 63 4 ND 34 101 5 NA NA 8 NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 39 ND ND ND 39 11 NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 290 ND ND 30 320 55 NA NA NS NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 240 1 ND 17 258 87 NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/01 230 ND ND ND 230 92 NA NA 12 NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 310 ND ND ND 310 130 NA NA 13 NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 100 <5 <5 <10 100 840 NA NA 30 NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 120 <0.7 <0.8 2 122 1,100 5 <1 25 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04 45 7 4 23 78 1,000 4 <1 31 NA NA NA NA NA NA NA NA NA NA NA NA
04/18/05 <1 <1 <1 <1 0 950 8 <1 1 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05 3 <1 <1 <1 3 960 6 <1 2 NA NA NA NA NA NA NA NA NA NA NA NA
03/29/06 180 <5 <5 <5 180 1,100 <5 <1 <5 NA NA 89 NA <1 <1 <2 NA NA NA NA NA
10/05/06 49 <5 <5 <5 49 1,600 6 <5 35 NA NA 90 NA <5 <5 <5 NA NA NA NA NA
03/21/07 38 <1 <2 2 40 2,400 8 <2 20 NA NA NA NA NA NA NA NA NA NA NA NA
09/27/07 8 <0.7 <0.8 <0.8 8 1,700 8 <1 3 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 13 <100 <100 <200 13 2,300 <100 <0.02 <100 NA NA 110 NA NA <100 NA NA NA NA NA NA
10/08/08 11 J <4 <4 <4 11 1,900 5 J <0.0096 <5 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 12 <10 <10 <10 12 2,500 24 <0.022 <100 NA NA NA NA NA NA NA NA NA NA NA NA
10/12/09 <10 <10 <10 <10 0 3,000 <10 <0.022 <100 NA NA NA NA NA NA NA NA NA NA NA NA
04/20/10 4 0 <0.1 <0.2 4 2,500 5 <0.022 <0.1 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 4 <0.1 <0.1 0.3 4 2,700 4 <0.022 <0.1 <0.1 0.99 77 0.21 <0.2 <0.1 <0.2.NA NA <0.1 0.18 <0.1
04/27/11 4.8 <2 <2 <2 4.8 2,300 4.7 <0.022 <2 <2 <2 70 <4 <2 <2 <4 NA NA <2 <2 <2
10/14/11 5.4 J <10 <10 <10 5.4 2,700 5.4 J <0.049 <10 <10 <10 73 <10 <10 <10 <16 <0.54 <10 <10 <10 <10
04/16/12 2.8 J <10 <10 <10 2.8 J 3,200 5.2 J 0.016 J <10 <10 <10 86 <10 <10 <10 <16 <40 <10 <10 <10 <10
10/19/12 8.7 <1 <1 <1 8.7 2,800 4.0 J <0.0096 <1 <1 <1 71 <1 <1 <1 <2 <0.0096 <1 <1 <1 <1
05/02/13 8.3 J <5.0 <5.0 <5.0 8.3 J 2,800 <5.0 <5.0 <5.0 <5.0 <5.0 78 <5.0 <5.0 <5.0 <10 25 <5.0 <5.0 <5.0 <5.0
10/16/13 3.1 J <2.0 <2.0 <2.0 3.1 J 2,400 4.3 J <0.0096 <2.0 <2.0 <2.0 75 <2.0 <2.0 <2.0 <4.0 <10 <2.0 <2.0 <2.0 <2.0
05/19/14 <2.0 <2.0 <2.0 <4.0 <10.0 1,900 3.6 J <0.014 31 <2.0 <2.0 48 <2.0 <2.0 <2.0 <4.0 <10 <2.0 <2.0 <2.0 <2.0
10/06/14 <1.0 <1.0 <1.0 <2.0 <5.0 1,000 2.0 J <0.0097 <1.0 <1.0 <1.0 28 <1.0 <1.0 <1.0 <2.0 <5.0 <1.0 <1.0 <1.0 <1.0
05/19/15 <2.0 <2.0 <2.0 <4.0 <10.0 1,200 2.1 J <0.15 <2.0 <2.0 <2.0 32 <2.0 <2.0 <2.0 <4.0 <10 <2.0 <2.0 <2.0 <2.0
10/07/15 <2.0 <2.0 <2.0 <4.0 <10.0 2,200 4.4 J <0.0096 <2.0 <2.0 <2.0 52 <2.0 <2.0 <2.0 <4.0 10 <2.0 <2.0 <2.0 <2.0
04/11/16 <1.0 <1.0 <1.0 <2.0 <5.0 1,700 3.4 J <0.0096 <1.0 <1.0 <1.0 43 <1.0 <1.0 <1.0 <2.0 <5.0 <1.0 <1.0 <1.0 <1.0
10/19/16 <6.3 <6.3 <6.3 <100 ---4,240 7 <0.0095 <6.3 <6.3 <6.3 108 <6.3 <6.3 <6.3 <50 <6.3 <6.3 <6.3 <6.3 <6.3
04/06/17 <3.1 <3.1 <3.1 <6.3 ---3,020 4.9 J <3.1 <3.1 <3.1 <3.1 77.5 <3.1 <3.1 <3.1 <25 NA <3.1 <3.1 <3.1 <3.1
10/18/17 <1.3 1.3 J <1.3 <2.5 1.3 1,400 3.5 J <1.3 <1.3 <1.3 <1.3 41.4 <1.3 <1.3 <1.3 <10 NA <1.3 <1.3 <1.3 <1.3
04/05/18 <1.3 <1.3 <1.3 <2.5 ND 959 3.9 J <0.0093 <1.3 <1.3 <1.3 40.8 <1.3 <1.3 <1.3 <10 NA <1.3 <1.3 <1.3 <1.3
10/16/18 <0.13 <0.13 <0.13 <1.3 NE 876 <0.13 <0.0093 <1.3 <0.13 <0.13 34 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/23/19 <0.63 <0.63 <0.63 <1.3 ND 200 <0.63 <0.0093 2.5 <0.63 <0.63 4.3 <0.63 <0.63 <0.63 <5.0 NA <0.63 <0.63 <0.63 0.74 J
10/29/19 <0.13 <0.13 <0.13 <0.25 ND 31.4 <0.13 <0.13 <0.13 <0.13 <0.13 1.1 <0.13 <0.13 <0.13 <5.0 NA <0.13 <0.13 <0.13 <0.13
05/21/20 <0.13 <0.13 <0.13 <0.25 ND 4.3 <0.13 <0.0095 <0.13 <0.13 <0.13 0.47 J <0.13 <0.13 0.16 J <5.0 NA <0.13 <0.13 <0.13 <0.13
11/19/20 <0.13 <0.13 <0.13 <0.25 ND 2.1 <0.13 <0.13 <0.13 <0.13 <0.13 0.18 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/15/21 <0.13 <0.13 <0.13 <0.25 ND 1.4 <0.13 0.093 <0.13 <0.13 <0.13 0.18 J <0.13 <0.13 0.14 J <1.0 NA <0.13 <0.13 <0.13 <0.13
10/29/21 <0.13 <0.13 <0.13 <0.25 ND 1.2 <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.14 J <1.0 NA <0.13 <0.13 <0.13 <0.13
04/29/22 <0.13 <0.13 <0.13 <0.25 <0.25 1.3 <0.13 <0.0095 0.18 J <0.13 <0.13 0.14 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 0.17 J <0.13 <0.13 <0.25 0.17 J 0.63 <0.13 0.077 <0.13 <0.13 <0.13 0.43 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-4D
Page 5 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
07/01/96 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 ND ND ND ND ---ND NA NA NS NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 2 0.6 ND 1.1 3.7 ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/01 110 19 11 679 819 ND NA NA 150 NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 2 ND ND 4 6 2 NA NA 15 NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04 <1 <1 <1 5.1 5 <8 <1 <1 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/18/05 <1 <1 <1 <1 ---<1 <1 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05 <1 <1 <1 <1 ---<1 <1 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
03/29/06 <1 <5 <5 <5 ---<5 <5 <1 <5 NA NA NA NA NA NA NA NA NA NA NA NA
10/05/06 <5 <5 <5 <5 ---<5 <5 <5 <5 NA NA NA NA NA NA NA NA NA NA NA NA
03/21/07 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/27/07 2 <0.7 <0.8 <0.8 2 <0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 <1 <5 <5 <10 ---<5 <5 <0.02 <5 NA NA NA NA NA NA NA NA NA NA NA NA
10/08/08 <0.5 <0.8 <0.7 <0.8 ---2 J <0.8 <0.0095 <1 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 <1 <1 <1 <1 ---<8 <1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
10/13/09 <1 <1 <1 <1 ---<8 <1 <0.023 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/19/10 <0.1 <0.1 <0.1 <0.2 ---<0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 <0.1 <0.1 <0.1 <0.2 ---<0.2 <0.1 <0.022 <0.1 <0.1 <0.1 <0.2 <0.2 <0.2 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
04/27/11 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.1 <0.022 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
10/14/11
04/16/12
04/16/12 <0.5 <0.5 <0.5 <0.5 ---0.1 J <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12 <0.1 <0.1 <0.1 <0.1 ---<0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.0096 <0.1 <0.1 <0.1 <0.1
05/02/13
05/19/15 <0.1 <0.1 <0.1 <0.2 <0.5 0.3 J <0.1 <0.0095 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.5 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 <0.1 <0.1 <0.2 <0.5 0.3 J <0.1 <0.0096 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/11/16 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0095 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/18/16 <0.13 <0.13 <0.13 <0.31 ---<0.13 <0.13 <0.0098 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/05/17 <0.13 <0.13 <0.13 <0.25 ---<0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 NA <0.13 <0.13 <0.13 <0.13
10/18/17 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0092 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/16/18 <0.13 <0.13 <0.13 <1.3 NE <0.13 <0.13 <0.0092 0.17 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/22/19 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0092 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/28/19 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
05/20/20 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0093 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
11/20/20 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/15/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0037 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/28/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/28/22 <0.13 <0.13 <0.13 <0.25 <0.25 <0.13 <0.13 <0.0094 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0094 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-5A
MW-5
Well not located
Well abandoned
MW-5R
Well abandoned
Page 6 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
07/01/96 NS NS NS NS ---NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 4 0.7 ND ND 4.7 3 NA NA 2 NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 ND ND ND 1.2 1.2 ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/01 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 ND ND ND ND NA ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 ND ND ND ND NA ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04 <1 <1 <1 <1 ---<8 <1 <1 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/18/05 <1 <1 <1 <1 ---<1 <1 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05 <1 <1 <1 <1 ---<1 <1 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
03/29/06 <1 <5 <5 <5 ---<5 <5 <1 <5 NA NA <1 NA <1 <1 <2 NA NA NA NA NA
10/05/06 <5 <5 <5 <5 ---<5 <5 <5 <5 NA NA <5 NA <5 <5 <5 NA NA NA NA NA
03/21/07 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA <1 NA <1 <0.8 <2 NA NA NA NA NA
09/27/07 4 <0.7 <0.8 <0.8 4 <0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 <1 <5 <5 <10 ---<5 <5 <0.02 <5 NA NA <5.0 NA NA <5.0 NA NA NA NA NA NA
10/08/08 <0.5 <0.8 <0.7 <0.8 ---<0.5 <0.8 <0.0097 <1 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 <1 <1 <1 <1 ---<8 <1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
10/12/09 <1 <1 <1 <1 ---<8 <1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/19/10 <0.1 <0.1 <0.1 <0.2 ---<0.2 <0.1 <0.021 <0.1 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 <0.1 <0.1 <0.1 <0.2 ---<0.2 <0.1 <0.021 <0.1 <0.1 <0.1 1.0 <0.2 <0.2 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
04/27/11 <0.1 <0.1 <0.1 <0.1 ---<0.2 <0.1 <0.022 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
10/14/11
04/16/12 <0.5 <0.5 <0.5 <0.5 ---<0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12 <0.1 <0.1 <0.1 <0.1 ---<0.1 <0.1 <0.0095 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.0095 <0.1 <0.1 <0.1 <0.1
05/02/13 <0.1 <0.1 <0.1 <0.1 ND <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/16/13 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0097 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
05/19/14 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/06/14 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
05/19/15 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0094 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.5 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0095 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/11/16 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0097 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/18/16 <0.13 <0.13 <0.13 <0.31 ---<0.13 <0.13 <0.0098 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/06/17
10/19/17 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0092 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/16/18 <0.13 <0.13 <0.13 <1.3 NE <0.13 <0.13 <0.0092 <1.3 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/23/19 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0092 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/28/19 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
05/21/20 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0094 <0.13 <0.13 <0.13 <0.13 <0.13 1.4 4.7 <1.0 NA <0.13 <0.13 <0.13 <0.13
11/19/20 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.72 2.4 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/15/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0037 <0.13 <0.13 <0.13 <0.13 <0.13 0.39 J 1.5 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/28/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 1.5 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/29/22 <0.13 <0.13 <0.13 <0.25 <0.25 <0.13 <0.13 <0.0094 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.34 J <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-6R
Well not located
Not Sampled - Could Not Find Well
MW-6
Page 7 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
07/01/96 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 ND ND ND ND ---ND NA NA NS NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/01 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04 <1 <1 <1 <1 ---<8 <1 <1 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/18/05 <1 <1 <1 <1 ---<1 <1 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05
03/29/06 <1 <5 <5 <5 ---<5 <5 <1 <5 NA NA <1 NA <1 <1 <2 NA NA NA NA NA
10/05/06 <5 <5 <5 <5 ---<5 <5 <5 <5 NA NA <5 NA <5 <5 <5 NA NA NA NA NA
03/21/07 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA <1 NA <1 <0.8 <2<NA NA NA NA NA
09/27/07 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 <1 <5 <5 <10 ---<5 <5 <0.02 <5 NA NA <5.0 NA NA <5.0 NA NA NA NA NA NA
10/08/08 <0.5 <0.8 <0.7 <0.8 ---<0.5 <0.8 <0.0096 <1 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 <1 <1 <1 <1 ---<8 <1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
10/12/09 <1 <1 <1 <1 ---<8 <1 <0.022 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/19/10 <0.1 <0.1 <0.1 0.14 ---<0.2 <0.1 <0.021 <0.1 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 <0.1 <0.2 <0.1 <0.2 ---<0.2 <0.1 <0.021 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
04/27/11 <0.1 <0.1 <0.1 <0.1 ---<0.2 <0.1 <0.023 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
10/14/11 <0.5 <0.5 <0.5 <0.5 ---<0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.8 <0.029 <0.5 <0.5 <0.5 <0.5
04/16/12 <0.5 <0.5 <0.5 <0.5 ---<0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12 <0.1 <0.1 <0.1 <0.1 ---<0.1 <0.1 NA <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 NA <0.1 <0.1 <0.1 <0.1
05/02/13 <0.1 <0.1 <0.1 <0.1 ND <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/16/13 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0097 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
05/19/14 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/06/14 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0097 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
05/19/15 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0094 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.5 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/11/16 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0095 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/18/16
04/05/17
10/19/17
04/05/18
10/16/18
04/23/19 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0093 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.20 J <1.0 NA <0.13 <0.13 <0.13 <0.13
10/28/19 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.22 J <1.0 NA <0.13 <0.13 <0.13 <0.13
05/21/20 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0094 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.33 J <1.0 NA <0.13 <0.13 <0.13 <0.13
11/19/20 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.34 J <1.0 NA <0.13 <0.13 <0.13 <0.13
04/15/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0037 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.21 J <1.0 NA <0.13 <0.13 <0.13 <0.13
10/28/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.22 J <1.0 NA <0.13 <0.13 <0.13 <0.13
04/29/22 <0.13 <0.13 <0.13 <0.25 <0.25 <0.13 <0.13 <0.0094 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22
MW-7
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Page 8 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
07/01/96 NS NS NS NS NA NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 ND ND ND ND ---ND NA NA NS NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/01 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 <0.5 <0.7 <0.8 <0.8 ND <0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04
04/18/05 <1 <1 <1 <1 ---<1 <1 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05
03/29/06 <1 <5 <5 <5 ---<5 <5 <1 <5 NA NA <1 NA <1 <1 <2 NA NA NA NA NA
10/05/06 <5 <5 <5 <5 ---<5 <5 <5 <5 NA NA <5 NA <5 <5 <5 NA NA NA NA NA
03/21/07 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA <1 NA <1 <0.8 <2 NA NA NA NA NA
09/27/07 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08
10/08/08
04/09/09 <1 <1 <1 <1 ---<8 <1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
10/13/09
04/20/10 <0.1 <0.1 <0.1 <0.2 ---<0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 <0.2 <0.2 <0.1 <0.2 ---<0.2 <0.1 <0.022 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
04/26/11
10/14/11
04/16/12 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12
05/02/13
05/19/15 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0098 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.5 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.0095 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/11/16 <0.1 <0.1 <0.1 <0.2 <0.5 0.2 J <0.1 <0.0097 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/19/16 <0.13 <0.13 <0.13 <0.31 ---<0.13 <0.13 <0.0097 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/05/17 <0.13 <0.13 <0.13 <0.25 ---<0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 NA <0.13 <0.13 <0.13 <0.13
10/18/17 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0091 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA 0.26 J <0.13 <0.13 <0.13
10/16/18 <0.13 <0.13 <0.13 <1.3 NE <0.13 <0.13 <0.0092 <1.3 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 0.16 J <0.13 <0.13 <1.3
04/23/19 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0092 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/29/19 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
05/21/20 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
11/19/20 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/15/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/29/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/29/22 <0.13 <0.13 <0.13 <0.25 <0.25 <0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.21 J <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0097 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-8A
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
Not Sampled - Well Dry
MW-8
Well abandoned
Page 9 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
07/01/96 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
07/01/97 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
11/01/97 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
03/01/99 ND ND ND ND ---ND NA NA NS NA NA NA NA NA NA NA NA NA NA NA NA
12/01/99 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/00 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
09/01/00 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/01/01 ND 0.5 ND ND 0.5 0.7 NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
09/01/01 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
02/01/02 ND ND ND ND ---0.5 NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
09/02/02 NS NS NS NS NS NS NS NS NS NA NA NA NA NA NA NA NA NA NA NA NA
03/03/03 ND ND ND ND ---ND NA NA ND NA NA NA NA NA NA NA NA NA NA NA NA
09/03/03 NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA NA
03/17/04 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/22/04 <1 <1 <1 <1 ---<8 <1 <1 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/18/05 <1 <1 <1 <1 ---<1 <1 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
09/14/05 <1 <1 <1 <1 ---<1 <1 <1 <1 NA NA NA NA NA NA NA NA NA NA NA NA
03/29/06 <1 <5 <5 <5 ---<5 <5 <1 <5 NA NA <1 NA <1 <1 <2 NA NA NA NA NA
10/05/06 <5 <5 <5 <5 ---<5 <5 <5 <5 NA NA <5 NA <5 <5 <5 NA NA NA NA NA
03/21/07 <0.5 <0.7 <0.8 <0.8 ---<0.5 <0.8 <1 <1 NA NA <1 NA <1 <0.8 <2 NA NA NA NA NA
09/27/07
05/08/08 <1 0.74 <5 <10 0.74 3.4 <5 <0.02 <5 NA NA <5.0 NA NA <5.0 NA NA NA NA NA NA
10/08/08 <0.5 <0.8 <0.7 <0.8 ---9 <0.8 <0.0096 <1 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 <1 <1 <1 <1 ---<8 <1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
10/13/09 <1 <1 <1 <1 ---10 <1 <0.022 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/20/10 <0.1 <0.1 <0.1 <0.2 ---<0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 <0.2 <0.2 <0.1 <0.2 ---5.9 <0.1 <0.022 <0.1 <0.1 <0.1 <0.2 <0.2 <0.2 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
04/26/11 <0.1 <0.1 <0.1 <0.1 ---6.4 <0.1 <0.022 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.1 <0.2 NA NA <0.1 <0.1 <0.1
10/14/11 <0.5 0.1 J <0.5 0.2 J 0.3 13 <0.5 <0.029 <0.5 <0.5 <0.5 0.3 J <0.5 <0.5 <0.5 <0.8 <0.029 <0.5 <0.5 <0.5 <0.5
04/16/12 <0.5 <0.5 <0.5 <0.5 ---0.7 <0.5 <0.029 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12 <0.1 <0.1 <0.1 <0.1 ---0.5 <0.1 <0.0097 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.0097 <0.1 <0.1 <0.1 <0.1
05/02/13
MW-9R
Well abandoned
MW-9
Not Sampled - Well Dry
Page 10 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
05/19/15 5.0 J <2.0 <2.0 <4.0 5.0 J 2,500 11 0.013 J <2.0 <2.0 <2.0 110 <2.0 <2.0 <2.0 <4.0 <10 <2.0 <2.0 <2.0 <2.0
10/07/15 23 <2.0 <2.0 <4.0 31 2,200 9.2 J <0.0096 <2.0 <2.0 <2.0 73 <2.0 <2.0 <2.0 <4.0 10 <2.0 <2.0 <2.0 <2.0
04/11/16 5.9 <1.0 <1.0 <2.0 5.9 1,100 3.4 J 0.018 J <1.0 <1.0 <1.0 34 <1.0 <1.0 <1.0 <2.0 <5.0 <1.0 <1.0 <1.0 <1.0
10/19/16 3.4 <0.13 <0.13 <0.31 3.4 640 <0.13 0.029 0.42 J <0.13 <0.13 18.2 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/05/17 10.7 J <3.1 <3.1 <6.3 10.7 J 746 <3.1 0.059 <3.1 <3.1 <3.1 21.4 <3.1 <3.1 <3.1 <25 NA <3.1 <3.1 <3.1 <3.1
10/18/17 36.4 <1.3 <1.3 <2.5 36.4 974 3.3 J <1.3 1.7 J <1.3 <1.3 36.2 <1.3 <1.3 <1.3 <10 NA <1.3 <1.3 <1.3 <1.3
04/05/18 4.4 J <1.3 <1.3 <2.5 4.4 J 532 1.6 J <0.0091 <1.3 <1.3 <1.3 14.8 <1.3 <1.3 <1.3 <10 NA <1.3 <1.3 <1.3 <1.3
10/16/18 18.1 <0.13 <0.13 <1.3 18.1 753 <0.13 <0.0092 <1.3 <0.13 <0.13 19.6 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/23/19 42.8 <2.5 <2.5 <5.0 42.8 628 <2.5 <0.0092 5.3 J <2.5 <2.5 27.6 <2.5 <2.5 <2.5 <20 NA <2.5 <2.5 <2.5 <2.5
10/29/19 1.6 <0.63 <0.63 <1.3 1.6 190 <0.63 <0.63 0.79 <0.63 <0.63 5.9 <0.63 <0.63 <0.63 6.4 NA <0.63 <0.63 <0.63 <0.63
05/21/20 <0.31 <0.31 <0.31 <0.63 ND 82.7 <0.31 0.017 J 0.79 J <0.31 <0.31 2.3 J <0.31 <0.31 <0.31 <2.5 NA <0.31 <0.31 <0.31 <0.31
11/19/20 <0.13 <0.13 <0.13 <0.25 ND 46.3 <0.13 0.48 <0.13 <0.13 <0.13 2.1 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/15/21 <0.13 <0.13 <0.13 <0.25 ND 2.7 <0.13 <0.0037 <0.13 <0.13 <0.13 0.16 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/29/21 <0.13 <0.13 <0.13 <0.25 ND 50.0 <0.13 0.036 <0.13 <0.13 <0.13 1.8 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/29/22 <0.13 <0.13 <0.13 <0.25 <0.25 16.0 <0.13 <0.0094 <0.13 <0.13 <0.13 0.54 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 0.043 <0.13 <0.13 <0.13 0.34 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
09/27/07 460 <0.7 <0.8 15 475 330 4 <1 13 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 670 <50 <50 <100 670 1,100 <50 0.01 <50 NA NA 63 NA NA <50 NA NA NA NA NA NA
10/08/08 470 <0.8 <0.7 10 480 680 2 J 0.02 33 NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 390 <1 <1 7.1 397 810 3.3 <0.021 22 NA NA NA NA NA NA NA NA NA NA NA NA
10/12/09 69 <1 <1 <1 69 860 <1 <0.022 <10 NA NA NA NA NA NA NA NA NA NA NA NA
04/19/10 45 <0.1 <0.1 <0.2 45 1,000 2.8 <0.022 17 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 110 1,100 440 1,870 3,520 980 3.4 <0.022 61 27 <1 30 39 <2 <1 <2 NA NA 110 670 220
04/27/11 17 <0.1 <0.1 0.12 17.12 700 2 <0.022 2.3 <0.1 <0.1 20 <0.2 0.21 0.56 <0.2 NA NA <0.1 <0.1 <0.1
10/14/11 6.5 <5 <5 1 J 7.50 610 <5 0.031 <5 <5 <5 24 <5 <5 <5 <8 <0.029 <5 <5 <5 <5
04/16/12 10 <2.5 <2.5 <2.5 10 740 2.3 J <0.029 1.6 J <2.5 <2.5 22 0.6 J <2.5 <2.5 <4 <10 <2.5 <2.5 0.8 J <2.5
10/19/12 0.2 J <0.1 <0.1 <0.1 0.2 J 2.1 <0.1 <0.0097 <0.1 <0.1 <0.1 0.4 J <0.1 <0.1 <0.1 <0.2 <0.0097 <0.1 <0.1 <0.1 <0.1
05/02/13 1.1 <0.1 <0.1 <0.1 1.1 66.0 <0.1 <0.1 0.2 J <0.1 <0.1 2.8 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/16/13 <0.1 <0.1 <0.1 <0.1 <0.1 1.6 <0.1 <0.0096 <0.1 <0.1 <0.1 0.2 J <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
05/19/14 3.3 J <1.0 <1.0 <2.0 3.3 J 800 2.1 J <0.0096 <1.0 <1.0 <1.0 14 <1.0 <1.0 <1.0 <2.0 <5.0 <1.0 <1.0 <1.0 <1.0
10/06/14 1.4 J <0.5 <0.5 <1.0 1.4 J 360 0.7 J <0.0097 <0.5 <0.5 <0.5 6.5 <0.5 <0.5 <0.5 <1.0 <2.5 <0.5 <0.5 <0.5 <0.5
05/19/15 0.2 J 0.4 J <0.1 0.4 J 1.0 J 7 <0.1 <0.0094 0.1 J <0.1 <0.1 0.7 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 <0.1 <0.1 <0.2 <0.5 29 0.2 J <0.0095 <0.1 <0.1 <0.1 2.7 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/11/16 1 <0.1 <0.1 <0.2 1 0.5 J <0.1 <0.0095 0.2 J <0.1 <0.1 0.5 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/19/16 <0.13 <0.13 <0.13 <0.31 ---2.1 <0.13 <0.0095 <0.13 <0.13 <0.13 0.52 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/06/17 <0.13 <0.13 <0.13 <0.25 ---0.31 J <0.13 <0.13 <0.13 <0.13 <0.13 0.43 J <0.13 <0.13 <0.13 <0.13 NA <0.13 <0.13 <0.13 <0.13
10/18/17 <0.13 <0.13 <0.13 <0.25 ND 3.7 <0.13 <0.0098 <0.13 <0.13 <0.13 0.45 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 <0.13 <0.13 <0.13 <0.25 ND 0.33 J <0.13 <0.0092 <0.13 <0.13 <0.13 0.53 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/16/18 <0.13 <0.13 <0.13 <1.3 NE 2.5 <0.13 <0.0092 <1.3 <0.13 <0.13 1.4 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/23/19 11 0.6 <0.13 0.61 J 12.21 0.6 <0.13 <0.0092 0.89 <0.13 <0.13 0.33 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.22 J 0.42 J
10/29/19 <0.13 <0.13 <0.13 <0.25 ND 0.25 J <0.13 <0.13 <0.13 <0.13 <0.13 0.16 J <0.13 <0.13 0.16 <1.0 NA <0.13 <0.13 <0.13 <0.13
05/21/20 <0.13 <0.13 <0.13 <0.25 ND 0.19 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.17 J <1.0 NA <0.13 <0.13 <0.13 <0.13
11/19/20 <0.13 <0.13 <0.13 <0.25 ND 0.22 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/16/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0037 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.19 J <1.0 NA <0.13 <0.13 <0.13 <0.13
10/29/21 <0.13 <0.13 <0.13 <0.25 ND 0.21 J <0.13 <0.0037 <0.13 <0.13 <0.13 0.16 J <0.13 <0.13 0.21 J <1.0 NA <0.13 <0.13 <0.13 <0.13
04/29/22 <0.13 <0.13 <0.13 <0.25 <0.25 <0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 0.19 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 0.030 <0.13 <0.13 <0.13 0.20 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-9A
MW-10D
Page 11 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
09/27/07 2,200 <1 <2 67 2,267 2,300 7 <2 98 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 1,800 <50 <50 40 1,840 1,800 <50 0.09 <50 NA NA <50 NA NA <50 NA NA NA NA NA NA
10/08/08 650 <3 <3 6 J 650 2,400 4 J 0.023 J 7 J NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 410 <10 <10 <10 410 2,600 <10 <0.021 <100 NA NA NA NA NA NA NA NA NA NA NA NA
10/13/09 59 <10 <10 <10 59 2,300 <10 <0.022 <100 NA NA NA NA NA NA NA NA NA NA NA NA
04/19/10 71 <0.1 0.11 0.48 72 2,300 5.8 <0.021 4.8 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 17 4.5 <2 <4 22 2,800 4.9 <0.022 <2 <2 <2 50 <4 <2 <2 <4 NA NA <2 <2 <2
04/27/11 5.2 <0.5 <0.5 <0.5 5.2 2,600 3.9 <0.024 <0.5 <0.5 <0.5 51 1 1 1.8 <1 NA NA <0.5 <0.5 <0.5
10/14/11 11 J <25 <25 <25 11 3,200 5.8 J 0.043 <25 <25 <25 62 <25 <25 <25 <40 <0.20 <25 <25 <25 <25
04/16/12 22 <10 <10 <10 22 2,700 4.3 J <0.029 <10 <10 <10 55 <10 <10 <10 <16 <40 <10 <10 <10 <10
10/19/12 8.0 J <5 <5 <5 8.0 J 2,900 <5 <0.0096 <5 <5 <5 52 <5 <5 <5 <10 <0.0096 <5 <5 <5 <5
05/02/13
05/19/15 <0.1 <0.1 <0.1 <0.2 <0.5 3.5 0.3 J <0.0095 <0.1 <0.1 <0.1 2.4 <0.1 <0.1 <0.1 <0.5 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 <0.1 <0.1 <0.2 <0.5 3.9 0.1 J <0.0095 <0.1 <0.1 <0.1 0.7 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/11/16 <0.1 <0.1 <0.1 <0.2 <0.5 0.5 <0.1 <0.0096 <0.1 <0.1 <0.1 0.4 J <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/19/16 <0.13 <0.13 <0.13 <0.31 ----0.49 J <0.13 <0.0096 <0.13 <0.13 <0.13 0.29 J <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/05/17 <0.13 <0.13 <0.13 <0.25 ---<0.13 <0.13 0.014 J <0.13 <0.13 <0.13 0.20 J <0.13 <0.13 <0.13 <0.13 NA <0.13 <0.13 <0.13 <0.13
10/18/17 <0.13 <0.13 <0.13 <0.25 ND 0.50 <0.13 <0.13 <0.13 <0.13 <0.13 0.18 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 <0.13 <0.13 <0.13 <0.25 ND 0.54 <0.13 <0.0092 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/16/18 <0.13 <0.13 <0.13 <1.3 NE 0.51 <0.13 <0.0092 <1.3 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/22/19 <0.13 <0.13 <0.13 <0.25 ND 0.40 J <0.13 <0.0092 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/28/19 <0.13 <0.13 <0.13 <0.25 ND 2.3 <0.13 <0.13 <0.13 <0.13 <0.13 0.26 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
05/20/20 <0.13 <0.13 <0.13 <0.25 ND 0.36 J <0.13 <0.13 <0.13 <0.13 <0.13 0.15 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
11/19/20 <0.13 <0.13 <0.13 <0.25 ND 0.44 J <0.13 <0.13 <0.13 <0.13 <0.13 0.14 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/16/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0037 <0.13 <0.13 <0.13 0.17 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/28/21 <0.13 <0.13 <0.13 <0.25 ND 0.18 J <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/28/22 <0.13 <0.13 <0.13 <0.25 <0.25 0.23 J <0.13 <0.0095 0.22 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-11DA
MW-11D
Well abandoned
Page 12 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
09/27/07 250 <0.7 <0.8 1 251 1,200 3 <1 96 NA NA NA NA NA NA NA NA NA NA NA NA
05/08/08 110 <50 <50 <100 110 1600 <50 <0.02 <50 NA NA 54 NA NA <50 NA NA NA NA NA NA
10/08/08 3 J <2 <1 <2 3 1,000 3 J 0.017 J ND NA NA NA NA NA NA NA NA NA NA NA NA
04/09/09 5 <1 <1 <1 5 1,300 5.1 <0.021 <10 NA NA NA NA NA NA NA NA NA NA NA NA
10/12/09 7.8 <5 <5 <5 7.8 1,300 <5 <0.021 <50 NA NA NA NA NA NA NA NA NA NA NA NA
04/19/10 16 <0.1 <0.1 0.64 16.64 1,000 3.8 <0.022 3.2 NA NA NA NA NA NA NA NA NA NA NA NA
10/10/10 26 160 71 323 580 1,400 3.3 <0.022 12 <1 <1 38 7.0 <2 <1 <2 NA NA 14 100 30
04/27/11 1.4 24 <1 4.4 29.8 1,200 3.2 <0.021 <1 <1 <1 27 <2 <1 <1 2.5 NA NA <1 <1 <1
10/14/11 0.1 J 0.3 J 0.1 J 0.7 1.2 22 3.8 <0.029 <0.5 <0.5 <0.5 26 <0.5 <0.5 <0.5 <0.8 <0.029 <0.5 <0.5 0.2 J <0.5
04/16/12 0.1 J <0.5 <0.5 <0.5 0.1 J 140 3.1 <0.029 <0.5 <0.5 <0.5 22 <0.5 <0.5 <0.5 <0.8 <2.0 <0.5 <0.5 <0.5 <0.5
10/19/12 0.1 J <0.1 <0.1 <0.1 ---150 2.0 <0.0096 <0.1 <0.1 <0.1 24 <0.1 <0.1 <0.1 <0.2 <0.0096 <0.1 <0.1 <0.1 <0.1
05/02/13 <5.0 <5.0 <5.0 <5.0 ND 2,100 5.1 J <5.0 <5.0 <5.0 <5.0 50 <5.0 <5.0 <5.0 <10 <25 <5.0 <5.0 <5.0 <5.0
10/16/13 1.5 J <0.5 <0.5 <0.5 1.5 J 770 2.5 J <0.0096 <0.5 <0.5 <0.5 30 <0.5 <0.5 <0.5 <1.0 <2.5 <0.5 <0.5 <0.5 <0.5
05/19/14 0.6 J <0.5 <0.5 <1.0 0.6 J 660 3.0 <0.0095 <0.5 <0.5 <0.5 27 <0.5 <0.5 <0.5 <1.0 <2.5 <0.5 <0.5 <0.5 <0.5
10/06/14 0.9 J <0.2 <0.2 <0.4 0.9 J 540 1.6 <0.0095 <0.2 <0.2 <0.2 18 <0.2 <0.2 <0.2 <0.4 <1.0 <0.2 <0.2 0.2 J <0.2
05/19/15 <0.1 <0.1 <0.1 <0.2 <0.5 26 0.2 J <0.0093 <0.1 <0.1 <0.1 4.2 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 <0.1 <0.1 <0.2 <0.5 54 0.2 J <0.0094 <0.1 <0.1 <0.1 4 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/11/16 <0.1 <0.1 <0.1 <0.2 <0.5 18 0.1 J <0.0096 <0.1 <0.1 <0.1 3.8 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/19/16 <0.13 <0.13 <0.13 <0.31 ----61.6 0.18J 0.017 <0.13 <0.13 <0.13 3.2 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/05/17 <0.13 <0.13 <0.13 <0.25 ---62.7 0.17 J <0.13 <0.13 <0.13 <0.13 4.0 <0.13 <0.13 <0.13 <0.13 NA <0.13 <0.13 <0.13 <0.13
10/18/17 <0.13 <0.13 <0.13 <0.25 ND 0.43 J <0.13 <0.13 <0.13 <0.13 <0.13 0.78 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 <0.13 <0.13 <0.13 <0.25 ND 5.9 <0.13 <0.0092 <0.13 <0.13 <0.13 1.3 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/16/18 <0.13 <0.13 <0.13 <1.3 NE 32.4 <0.13 <0.0092 <1.3 <0.13 <0.13 2.9 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/23/19 <0.13 <0.13 <0.13 <0.25 ND 1.4 <0.13 <0.0092 <0.13 <0.13 <0.13 0.42 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/29/19 <0.13 <0.13 <0.13 <0.25 ND 3.0 <0.13 <0.13 <0.13 <0.13 <0.13 0.26 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
05/21/20 <0.13 <0.13 <0.13 <0.25 ND 1.7 <0.13 <0.13 <0.13 <0.13 <0.13 0.46 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
11/19/20 <0.13 <0.13 <0.13 <0.25 ND 3.5 <0.13 <0.13 <0.13 <0.13 <0.13 0.37 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/16/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0036 <0.13 <0.13 <0.13 0.19 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/29/21 <0.13 <0.13 <0.13 <0.25 ND 0.34 J <0.13 <0.0037 <0.13 <0.13 <0.13 0.30 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/29/22 <0.13 <0.13 <0.13 <0.25 <0.25 0.44 J <0.13 <0.0094 <0.13 <0.13 <0.13 0.28 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
05/02/13 40 J <20 <20 <20 40 J 18,000 24.0 <20 <20 <20 320 <20 <20 <20 <20 <40 <100 <20 <20 <20 <20
10/16/13 47 J <20 <20 <20 47 J 28,000 30 J <0.0095 <20 <20 <20 450 <20 <20 <20 <40 <100 <20 <20 <20 <20
05/28/14 15 J <10 <10 <20 16 J 15,000 16 J <0.0095 <10 <10 <10 200 <10 <10 <10 <20 <50 <10 <10 <10 <10
10/07/14 67 <2.0 <2.0 <4.0 67 2,600 3.5 J <0.0096 15 <2.0 <2.0 44 4.3 J <2.0 <2.0 <4.0 <10 <2.0 <2.0 5.0 J 4.9 J
05/19/15 3.7 J <1.0 <1.0 <2.0 3.7 J 1,000 1.5 J <0.0094 4.9 J <1.0 <1.0 19 <1.0 <1.0 <1.0 <2.0 <5.0 <1.0 <1.0 <1.0 <1.0
10/07/15 <1.0 <1.0 <1.0 <2.0 <5.0 630 1.0 <0.0094 2.0 J <1.0 <1.0 12 <1.0 <1.0 <1.0 <2.0 <5.0 <1.0 <1.0 <1.0 <1.0
04/12/16 <0.5 <0.5 <0.5 <1.0 <2.5 390 0.6 J <0.0095 1.0 J <0.5 <0.5 7.9 <0.5 <0.5 <0.5 <1.0 <2.5 <0.5 <0.5 <0.5 <0.5
10/18/16 0.16 J <0.13 <0.13 <0.31 ---361 0.46J <0.0097 0.29 J <0.13 <0.13 6.6 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/05/17 <0.13 <0.13 <0.13 <0.25 ---307 0.45 J <0.13 0.25 J <0.13 <0.13 6.2 <0.13 <0.13 <0.13 <0.13 NA <0.13 <0.13 <0.13 <0.13
10/19/17 <0.13 <0.13 <0.13 <0.25 ND 244 0.34 J <0.13 14.5 <0.13 <0.13 4.1 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 <0.13 <0.13 <0.13 <0.25 ND 223 0.33 J <0.0092 0.32 J <0.13 <0.13 3.6 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/16/18 <0.13 <0.13 <0.13 <1.3 NE 123 0.36 J <0.0092 0.22 J <0.13 <0.13 3.4 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/22/19 0.19 J <0.13 <0.13 <0.25 0.19 104 0.24 J <0.0092 0.61 <0.13 <0.13 2.8 0.16 J <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/31/19 <0.13 <0.13 <0.13 <0.25 ND 39.2 0.15 <0.13 <0.13 <0.13 <0.13 1.2 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
05/21/20 0.30 J <0.13 <0.13 <0.25 0.30 J 59.3 0.19 J <0.13 <0.13 <0.13 <0.13 2.0 <0.13 <0.13 0.14 J <1.0 NA <0.13 <0.13 <0.13 <0.13
11/20/20 <0.13 <0.13 <0.13 <0.25 ND 46.0 0.14J <0.13 <0.13 <0.13 <0.13 1.4 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/16/21 0.17 J <0.13 <0.13 <0.25 0.17 50.7 E 0.17 J <0.0037 <0.13 <0.13 <0.13 1.7 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
08/13/21 <0.13 <0.13 <0.13 <0.13 ND 56.5 NA NA NA NA NA 1.7 NA NA NA NA NA NA NA NA NA
10/28/21 <0.13 <0.13 <0.13 <0.25 ND 16.9 <0.13 <0.0038 <0.13 <0.13 <0.13 0.59 <0.13 <0.13 0.18 J <1.0 NA <0.13 <0.13 <0.13 <0.13
04/28/22 <0.13 <0.13 <0.13 <0.25 <0.25 45.7 0.23 J <0.0094 0.47 J <0.13 0.22 J 1.6 0.20 J <0.13 0.18 J <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND 29.1 <0.13 <0.0097 0.34 J <0.13 <0.13 1.2 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-12D
RW-1
Page 13 of 14
TABLE 4
HISTORICAL GROUNDWATER ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Monitoring
Well
Sample
Date Benzene Toluene Ethylbenzene Total Xylenes BTEX MTBE IPE EDB* Naphthalene n-Butylbenzene sec-Butylbenzene 1,2-Dichloroethane Isopropylbenzene Bromodichloromethane Chloroform Methylene Chloride 1,2-dibromo-3-chloropropane* p-Isopropyltoluene n-Propylbenzene 1,2,4-Trimethylbenzene 1,3,5-Trimethylbenzene1 600 600 500 NE 20 70 0.02 6 70 70 0.4 70 0.6 70 5 0.04 25 70 400 400
5,000 260,000 80,000 50,000 NE 20,000 70,000 50 6,000 5,900 8,800 400 30,500 NE 70,000 400,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
05/02/13 <2.0 <2.0 <2.0 <2.0 ND 1,400 2.9 J <2.0 <2.0 <2.0 <2.0 28 <2.0 <2.0 <2.0 <4.0 <10.0 <2.0 <2.0 <2.0 <2.0
10/16/13 0.7 J <0.5 <0.5 <0.5 0.7 J 290 0.6 J <0.0096 <0.5 <0.5 <0.5 6.7 <0.5 <0.5 <0.5 <1.0 <2.5 <0.5 <0.5 <0.5 <0.5
05/27/14 0.1 J <0.1 <0.1 <0.2 0.1 J 37 <0.1 <0.0096 <0.1 <0.1 <0.1 0.8 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/14 <0.5 <0.5 <0.5 <1.0 <2.5 590 1.8 J <0.0096 <0.5 <0.5 <0.5 14 0.5 J <0.5 <0.5 <1.0 <2.5 <0.5 <0.5 <0.5 <0.5
05/19/15 <0.1 <0.1 <0.1 <0.2 <0.5 120 0.7 <0.0095 <0.1 <0.1 <0.1 7.2 0.1 J <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/07/15 <0.1 <0.1 <0.1 <0.2 <0.5 110 0.5 <0.0094 <0.1 <0.1 <0.1 5.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
04/12/16 <0.1 <0.1 <0.1 <0.2 <0.5 8.1 0.2 J <0.0096 <0.1 <0.1 <0.1 4.0 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 <0.1 <0.1 <0.1
10/18/16 <0.13 <0.13 <0.13 <0.31 ---<0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 3.2 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13 <0.13
04/05/17 <0.13 <0.13 <0.13 <0.25 ---2.3 <0.13 <0.13 <0.13 <0.13 <0.13 2.2 <0.13 <0.13 <0.13 <0.13 NA <0.13 <0.13 <0.13 <0.13
10/19/17 <0.13 <0.13 <0.13 <0.25 ND 1.1 <0.13 <0.13 0.26 J <0.13 <0.13 2.6 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 <0.13 <0.13 <0.13 <0.25 ND 1.5 <0.13 <0.0093 <0.13 <0.13 <0.13 2.1 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/16/18 <0.13 <0.13 <0.13 <1.3 NE 9.2 <0.13 <0.0095 <1.3 <0.13 <0.13 0.8 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/23/19 0.45 J 0.18 J <0.13 0.34 J 0.97 <0.13 <0.13 <0.0095 0.79 <0.13 <0.13 0.18 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.16 J 0.29 J
10/31/19
05/21/20 <0.13 <0.13 <0.13 <0.25 ND 2.6 <0.13 <0.13 <0.13 <0.13 <0.13 0.16 J <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
11/20/20 <0.13 <0.13 <0.13 <0.25 ND 0.17 J <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13
04/16/21 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/29/21 <0.13 <0.13 <0.13 <0.25 ND 4.5 <0.13 <0.0038 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 0.15 J <1.0 NA <0.13 <0.13 <0.13 <0.13
04/29/22 <0.13 <0.13 <0.13 <0.25 <0.25 <0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
10/25/22 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.0097 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
04/05/18 8.3 0.17 J 0.24 J 1.2 J ND 2,420 2.5 <0.0093 0.54 <0.13 0.25 J 44.0 1.2 <0.13 <0.13 <1.0 NA <0.13 <0.13 0.39 J 0.13 J
10/16/18 <0.13 <0.13 <0.13 <1.3 NE 3,530 <0.13 <0.0093 <1.3 <0.13 <0.13 74.0 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 <0.13 <1.3
04/22/19 <6.3 <6.3 <6.3 <13 ND 1,280 <6.3 <0.0093 <6.3 <6.3 <6.3 29.9 <6.3 <6.3 <6.3 <50 NA <6.3 <6.3 <6.3 <6.3
10/31/19 <2.5 <2.5 <2.5 <5.0 ND 537 <2.5 <2.5 <2.5 <2.5 <2.5 14.8 <2.5 <2.5 <2.5 21.7 NA <2.5 <2.5 <2.5 <2.5
05/21/20 <1.3 <1.3 <1.3 <1.3 ND 245 <1.3 0.012 J <1.3 <1.3 <1.3 8.3 <1.3 <1.3 <1.3 <10 NA <1.3 <1.3 <1.3 <0.13
11/20/20 <0.13 <0.13 <0.13 <0.25 ND 118 <0.13 <0.13 1.1 J <0.13 <0.13 4.1 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13 <0.13
04/16/21 0.25 J <0.13 <0.13 <0.25 0.25 104 0.38 J <0.0037 2.1 <0.13 <0.13 5.1 0.18 J <0.13 0.16 J <1.0 NA <0.13 <0.13 <0.13 <0.13
07/13/21 <0.25 <0.25 <0.25 <0.25 ND 86.5 NA NA NA NA NA 3.2 NA NA NA NA NA NA NA NA NA
10/28/21 <0.31 <0.31 <0.31 <0.63 ND 81.8 <0.31 <0.0038 0.38 J <0.31 <0.31 3.3 <0.31 <0.31 <0.31 4.8 J NA <0.31 <0.31 <0.31 <0.31
04/28/22 <0.25 <0.25 <0.25 <0.50 <0.50 52.7 <0.25 <0.0093 3.7 <0.25 <0.25 1.6 0.33 J <0.25 0.64 J 4.2 B NA <0.25 <0.25 <0.25 <0.25
10/25/22 <0.25 <0.25 <0.25 <0.50 ND 38.8 <0.25 <0.0097 7.3 <0.25 <0.25 2.2 <0.25 <0.25 <0.25 4.5 B NA <0.25 <0.25 <0.25 <0.25
MW-MW1 05/02/13 1 0.1 J 0.4 J 3.6 5.1 J <0.1 <0.1 <0.1 2.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 <0.1 0.2 J 2.5 0.6
MW-MW2 05/02/13 1.6 <0.1 0.3 J 3.8 5.7 J <0.1 <0.1 <0.1 2.2 0.2 J 0.1 J <0.1 <0.1 <0.1 <0.1 <0.2 <0.5 0.1 J 0.1 J 3.6 1.6
Notes:
1. "<" or ND = Not detected at or above the method detection limit
2. Concentrations are reported in micrograms per liter (ug/l) or parts per billion (ppb) equivalents
3. 2L Standard = Title 15A NCAC 2L .0202 Groundwater Standard.
4. Values in BOLD indicate levels above 2L Groundwater Standards.
5. BTEX = Benzene, Toluene, Ethylbenzene, Total Xylenes
6. MTBE = Methyl Tertiary Butyl Ether
7. IPE = Isopropyl Ether
8. EDB = Ethylene Dibromide (1,2-Dibromoethane)
9. GCL = Gross Contamination Level
10. * = analyzed using EPA Method 504.1, except samples collected in April 2016 which were analyzed for EDB by Method 8011.
11. J = Estimated Value
12. NA / --- = Not available.
13. Lab results for groundwater collected from GW-9A on April 5, 2017 indicated a concentration of Ethyl Alcohol (Ethanol) at 38,500 ug/L, which exceeds the NCAC 2L Groundwater Standard of 4,000 ug/L.
14. NE = Not Established
15. B = Indictes analyte found in associated method blank.
RW-2
RW-3
NS - Not Sampled - Pump Not Operational
Page 14 of 14
TABLE 5
WATER SUPPLY WELL INFORMATION
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Melvin and Dora A. Watkins
2732 Boulder Lane
Charlotte, NC 28213
Yang Her and Yia Thao
2733 Boulder Lane
Charlotte, NC 28269
Keith D. and Cindy P. Williams
2740 Boulder Lane
Charlotte, NC 28269
Kevin and Donna Wallace
2741 Boulder Lane
Charlotte, NC 28213
Paul D. and Carolene B. Robinson
P.O. Box 680894
Charlotte, NC 28216
Barbara M. T. and Carol L. Bridges
6116 Burmith Avenue
Charlotte, NC 28269
James I. and Sue I. Bettis
6117 Burmith Avenue
Charlotte, NC 28269
Cathy McIlwain
6217 Burmith Avenue
Charlotte, NC 28269
Kenneth E. Douglas and
Mary E. Patton-Douglas
6220 Burmith Avenue
Charlotte, NC 28269
Sue H. Picklesimer and
Brenda Godbey
3940 Oakdale Road
Charlotte, NC 28216
Christopher B. Poindexter
5325 Eagle Lake Drive
Charlotte, NC 28217
Joe R. Young (deceased) and
Vera Jeanne Young
6308 Burmith Avenue
Charlotte, NC 28269
Adrienne Wallace
6325 Burmith Avenue
Charlotte, NC 28269
Daryl H. and Michelle M. Starnes
5517 Collins Street
Charlotte, NC 28269
Michael T. and Jennifer M. Bower
5453 Datha Avenue
Charlotte, NC 28269
Lawrence H. Duke, Sr.
12930 Dorman Road
Pineville, NC 28134
Nancy H. Melton
4716 Statesville Road
Charlotte, NC 28269
James E. Harris
P.O. Box 667446
Charlotte, NC 28266
Daniel and Cornelia Moldovan
5505 Milhaven Lane
Charlotte, NC 28269
Leila N. Sadler
5521 Milhaven Lane
Charlotte, NC 28269
Hattie J. and Asante M. and
Diantha D. Caldwell
5715 Milhaven Lane
Charlotte, NC 28269
Property
Address Property Owner Distance from Site
(feet)
Hydraulic
Setting
Well Status/
Comments
2732 Boulder Lane 1,370 Up gradient
2733 Boulder Lane 1,380 Up gradient
2740 Boulder Lane 1,260 Up gradient
Up gradient
6101 Burmith Avenue 1,050 Up gradient
6220 Burmith Avenue
6116 Burmith Avenue 900
6217 Burmith Avenue 470
2741 Boulder Lane 1,270
Up gradient
6117 Burmith Avenue 900 Up gradient
No
No
Up gradient
Up gradient
Upgradient
Up gradient
Up gradient
No
No
Up gradient
Up gradient500
Down gradient
No
No
Yes
1,450
110*
1,430
1,010
5312 Milhaven Lane
5028 Milhaven Lane
5721 Milhaven Lane
5521 Milhaven Lane
5505 Milhaven Lane
1,340
640
1,270
1,330 Up gradient
1,260
Down gradient
6240 Burmith Avenue
WSW-7 300*Up gradient WSW Pump has
no power
WSW Pump has
no powerUp gradient200*
Yes
Yes6249 Burmith Avenue
WSW-4
6325 BurmithAvenue
WSW-6
5600 Datha Avenue
5453 Datha Avenue
WSW Pump has
no power
Down gradient
6308 Burmith Avenue
WSW-5 Up gradient110*
5517 Collins Street
City Water
Connection?
No
No
No
No
No
No
No
No
No
No
No
No
Page 1 of 2
TABLE 5
WATER SUPPLY WELL INFORMATION
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Property
Address Property Owner Distance from Site
(feet)
Hydraulic
Setting
Well Status/
Comments
City Water
Connection?
Harry S. and Elizabeth P. Kinley
3310 Orr Street
Charlotte, NC 28269
Jeffery J. and Margaret E. Kryzewski
3415 Orr Street
Charlotte, NC 28269
Kenneth S. Greene and
Lisa and Richard Stikeleather
2824 The Plaza Road
Charlotte, NC 28205
Sherley B. Tarlton and R/E Inc.
1006 Elibren Lane
Matthews, NC 28105
Harold C. and Virginia F. Keith
5014 Statesville Road
Charlotte, NC 28213
Austin and Jacqueline T. Hughes
6542 Rumple Road
Charlotte, NC 28262
Betty J. Pennell
P.O. Box 26792
Charlotte, NC 28221
Harold C. and Virginia F. Keith
5014 Statesville Road
Charlotte, NC 28213
Nienke Steel Drafting Inc.
5530 Statesville Road
Charlotte, NC 28213
Oakdale Greenhouse LLC
Attn: William Kay
355 43rd Avenue NW
Hickory, NC 28601
Iola T. and Edward I. Wingate
5700 Statesville Road
Charlotte, NC 28269
Manchi LLC
6130 Harris Technology Drive
Charlotte, NC 28269
Manchi LLC
6130 Harris Technology Drive
Charlotte, NC 28269
Dianne G. Raymer
862 Countryside Court SE
Marietta, GA 30067
* Shaded Properties Represent Locations Designated for Sampling by NCDEQ
3415 Orr Street 680 Down gradient
3310 Orr Street 500 Down gradient
3421 Orr Street 790 Down gradient
3426 Orr Street 900
Down gradient
Down gradient
5407 Statesville Road 1,200
5441 Statesville Road 560
5432 Statesville Road 1,090
Down gradient
Down gradient
Down gradient
5700 Statesville Road
WSW-3 230*
5626 Statesville Road
WSW-1, WSW-2 200*
5524 Statesville Road 520 Down gradient
5440 Statesville Road 1,000
5800 Statesville Road 570
5724 Statesville Road 360
Down gradient
Cross Gradient WSW Pump has
no power
Up gradient
5915 Statesville Road 1,090 Up gradient
Up gradient
No
No
No
No
No
No
No
No
No
No
No
No
No
Yes
Page 2 of 2
TABLE 6
WATER SUPPLY WELL ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Water Supply Well
Sampling
Date Benzene Toluene Ethylbenzene Total Xylenes MTBE IPE EDB* Naphthalene Bromodichloromethane Chloroform Methylene Chloride 1,2-Dichloroethane Tetrachloroethene Dibromochloromethane1 600 600 500 20 70 0.02 6 0.6 70 5 0.4 0.7 0.4
3/21/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
9/28/2007 <0.5 <0.7 <0.8 1 <0.5 <0.8 <1 1 NA NA NA NA NA NA
10/30/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 <1 <0.8 <1 NA NA NA
5/5/2008 <1 <5 <5 <10 <5 <5 <0.02 <5 NA NA NA NA NA NA
10/14/2008 <0.5 <0.8 <0.7 <0.8 <0.5 <0.8 <0.0096 <1 NA NA NA NA NA NA
4/8/2009 <1 <1 <1 <1 <8 <1 <0.021 <10 NA NA NA NA NA NA
4/19/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.021 <0.1 NA NA NA NA NA NA
10/6/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.021 <0.1 NA NA NA NA NA NA
4/26/2011 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 <0.1 0.31 <0.1 NA NA NA
10/14/2011 <0.5 <0.5 <0.5 <0.5 0.1 J <0.5 <0.029 <0.5 <0.5 0.4 J <0.8 0.1 J <0.5 <0.5
3/21/2012 <0.5 <0.5 <0.5 <0.5 0.1 J <0.5 <0.029 <0.5 <0.5 0.3 J <0.8 <0.5 <0.5 <0.5
4/17/2012 <0.5 <0.5 <0.5 <0.5 0.1 J <0.5 <0.029 <0.5 <0.5 0.3 J <0.8 <0.5 <0.5 <0.5
7/20/2012 <0.5 <0.5 <0.5 <0.5 0.1 J <0.5 <0.030 <0.5 <0.5 0.3 J <0.8 <0.5 <0.5 <0.5
10/19/2012 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 0.3 J <0.2 0.1 J <0.1 <0.1
5/2/2013 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 0.4 J <0.1 0.1 J <0.1 <0.1
9/27/2013 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0098 <0.1 <0.1 0.4 J <0.2 0.1 J <0.1 <0.1
5/20/2014 <0.1 <0.1 <0.1 <0.1 0.1 J <0.1 <0.0095 <0.1 <0.1 0.4 J <0.2 0.2 J <0.1 <0.1
10/6/2014 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0095 <0.1 <0.1 0.3 J <0.2 0.2 J <0.1 <0.1
5/19/2015 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0094 <0.1 <0.1 0.4 J <0.2 0.3 J <0.1 <0.1
4/12/2016 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.0096 <0.1 <0.1 0.3 J <0.2 0.2 J <0.1 <0.1
10/19/2016 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.0094 <0.1 <0.1 0.2 J <0.2 0.15 J <0.1 <0.1
4/5/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0097 <0.13 <0.13 <0.13 <1.0 0.26 J <0.13 <0.13
10/19/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0097 <0.13 <0.13 0.19 J <1.0 0.15 J <0.13 <0.13
4/5/2018 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0092 <0.13 <0.13 0.19 J <1.0 0.14 J <0.13 <0.13
10/16/2018 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.31 J <1.0 0.21 J <0.13 <0.13
4/22/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.52 <1.0 0.15 J <0.13 <0.13
10/29/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.22 J <1.0 0.23 J <0.13 <0.13
5/20/2020 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.34 J <1.0 0.25 J <0.13 <0.13
11/20/2020 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 0.24 J <1.0 0.20 J <0.13 <0.13
4/16/2021 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0037 <0.13 <0.13 0.21 J <1.0 0.19 J <0.13 <0.13
10/29/2021 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0037 <0.13 <0.13 0.26 J <1.0 0.16 J <0.13 <0.13
4/29/2022 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0094 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
10/25/2022 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0094 <0.13 <0.13 0.28 J <1.0 NA <0.13 <0.13
3/21/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
9/28/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
5/5/2008 <1 <5 <5 <10 <5 <5 <0.02 <5 NA NA NA NA NA NA
10/14/2008 <0.5 <0.8 <0.7 <0.8 <0.5 <0.8 <0.0096 <1 NA NA NA NA NA NA
4/8/2009 <1 <1 <1 <1 <8 <1 <0.021 <10 NA NA NA NA NA NA
4/19/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA
10/6/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.021 <0.1 NA NA NA NA NA NA
4/26/2011 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.021 <0.1 <0.1 0.30 <0.1 NA NA NA
10/14/2011 <0.5 <0.5 <0.5 <0.5 0.1 J <0.5 <0.029 <0.5 <0.5 0.4 J <0.8 0.1 J <0.5 <0.5
3/21/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 0.3 J <0.8 <0.5 <0.5 <0.5
4/17/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 0.3 J <0.8 0.1 J <0.5 <0.5
7/20/2012 <0.5 <0.5 <0.5 <0.5 0.1 J <0.5 <0.030 <0.5 <0.5 0.3 J <0.8 <0.5 <0.5 <0.5
10/19/2012 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 0.4 J <0.2 <0.1 <0.1 <0.1
5/2/2013 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 0.3 J <0.2 <0.1 <0.1 <0.1
9/27/2013 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0098 <0.1 <0.1 0.2 J <0.2 <0.1 <0.1 <0.1
5/20/2014 <0.1 <0.1 <0.1 <0.1 0.1 J <0.1 <0.0096 <0.1 <0.1 0.4 J <0.2 0.2 J <0.1 <0.1
10/6/2014 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0097 <0.1 <0.1 0.2 J <0.2 0.1 J <0.1 <0.1
5/19/2015 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0094 <0.1 <0.1 0.3 J <0.2 0.2 J <0.1 <0.1
4/12/2016 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.0096 <0.1 <0.1 0.2 J <0.2 0.2 J <0.1 <0.1
10/19/2016 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.0096 <0.1 <0.1 0.33 J <0.2 0.25 J <0.1 <0.1
4/5/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0096 <0.13 <0.13 0.25 J <1.0 0.22 J <0.13 <0.13
10/19/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0097 0.37 J <0.13 0.29 J <1.0 0.31 J <0.13 <0.13
4/5/2018 <0.13 <0.13 <0.13 <0.25 0.14 J <0.13 <0.0092 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
10/16/2018 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.38 J <1.0 0.15 J <0.13 <0.13
4/22/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.26 J <1.0 0.20 J <0.13 <0.13
10/29/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.54 <1.0 0.30 J <0.13 <0.13
5/20/2020 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.33 J <1.0 0.24 J <0.13 <0.13
11/20/2020 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 0.26 J <1.0 0.21 J <0.13 <0.13
4/16/2021 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0037 <0.13 <0.13 0.19 J <1.0 0.29 J <0.13 <0.13
10/29/2021 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0038 <0.13 <0.13 0.25 J <1.0 0.18 J <0.13 <0.13
4/29/2022 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0096 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
10/25/2022 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0096 <0.13 <0.13 0.24 J <1.0 NA <0.13 <0.13
WSW-1 - South Well
Kay
Oakdale Nursery
5626 Statesville Road
WSW-2 - North Well
Kay
Oakdale Nursery
5626 Statesville Road
2L Standard
Page 1 of 4
TABLE 6
WATER SUPPLY WELL ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Water Supply Well
Sampling
Date Benzene Toluene Ethylbenzene Total Xylenes MTBE IPE EDB* Naphthalene Bromodichloromethane Chloroform Methylene Chloride 1,2-Dichloroethane Tetrachloroethene Dibromochloromethane1 600 600 500 20 70 0.02 6 0.6 70 5 0.4 0.7 0.42L Standard
3/21/2007 <0.5 <0.7 <0.8 <0.8 1 <0.8 <1 <1 NA NA NA NA NA NA
9/28/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
5/5/2008 <1 <5 <5 <10 <5 <5 <0.02 <5 NA NA NA NA NA NA
10/14/2008 <0.5 <0.8 <0.7 <0.8 <0.5 <0.8 <0.0096 <1 NA NA NA NA NA NA
4/8/2009 <1 <1 <1 <1 <8 <1 <0.021 <10 NA NA NA NA NA NA
4/19/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA
10/6/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA
4/26/2011 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 <0.1 <0.1 <0.1 NA NA NA
10/14/2011 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.8 <0.5 0.1 J <0.5
3/21/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.8 <0.5 0.1 J <0.5
4/17/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.8 <0.5 0.1 J <0.5
7/20/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.030 <0.5 <0.5 <0.5 <0.8 <0.5 <0.5 <0.5
10/19/2012 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1
5/2/2013 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.2 <0.1 0.1 J <0.1
9/27/2013 <0.1 <0.1 <0.1 <0.1 0.1 J <0.1 <0.0096 <0.1 <0.1 <0.1 <0.2 <0.1 0.1 J <0.1
5/20/2014 <0.1 <0.1 <0.1 <0.1 0.2 J <0.1 <0.0095 <0.1 <0.1 <0.1 <0.2 <0.1 0.1 J <0.1
10/6/2014 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.2 <0.1 0.1 J <0.1
5/19/2015 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0094 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1
4/12/2016
10/16/2018
10/29/2019
5/20/2020
11/20/2020
4/16/2021
10/29/2021
3/21/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
9/28/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
5/5/2008
10/14/2008
4/8/2009
4/19/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA
10/6/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.021 <0.1 12 33 3.9 NA NA NA
4/26/2011 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.02 <0.1 <0.1 <0.1 <0.1 NA NA NA
10/14/2011 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.8 <0.5 <0.5 <0.5
3/21/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.8 <0.5 <0.5 <0.5
4/17/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.8 <0.5 <0.5 <0.5
7/20/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.030 <0.5 <0.5 <0.5 <0.8 <0.5 <0.5 <0.5
10/19/2012 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 0.7 <0.2 <1.0 <0.1 <0.1
5/2/2013
9/27/2013
5/20/2014
10/6/2014
5/19/2015
4/12/2016
4/6/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 0.047 <0.13 10.2 10.3 <1.0 <0.13 <0.13 6.8
10/19/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 0.040 <0.13 12.3 16.0 <1.0 <0.13 <0.13 6.2
10/16/2018 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 8.9 20.2 <1.0 <0.13 <0.13 2.2
10/29/2019
5/20/2020
11/20/2020
4/16/2021
10/29/2021
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling
WSW-3
Wingate
5700 Statesville Road
WSW-4
Poindexter
6249 Burmith Ave.
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power (property is connected to city water)
Not Available for Sampling - Inoperable Pump Due to Lack of Power (property is connected to city water)
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - Inoperable/missing pump
Not Available for Sampling - Inoperable pump
Not Available for Sampling - Inoperable pump
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - Inoperable Pump
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - No Response from Property Owner/Occupant
Page 2 of 4
TABLE 6
WATER SUPPLY WELL ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Water Supply Well
Sampling
Date Benzene Toluene Ethylbenzene Total Xylenes MTBE IPE EDB* Naphthalene Bromodichloromethane Chloroform Methylene Chloride 1,2-Dichloroethane Tetrachloroethene Dibromochloromethane1 600 600 500 20 70 0.02 6 0.6 70 5 0.4 0.7 0.42L Standard
3/21/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
9/28/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
5/5/2008 <1 <5 <5 <10 <5 <5 <0.02 <5 NA NA NA NA NA NA
10/14/2008
4/8/2009 <1 <1 <1 <1 <8 <1 <0.021 <10 NA NA NA NA NA NA
4/19/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA
10/6/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 NA NA NA NA NA NA
4/26/2011 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.021 <0.1 <0.1 0.19 <0.1 NA NA NA
10/14/2011
3/21/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 0.2 J <0.8 <0.5 <0.5 <0.5
4/17/2012
7/20/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.030 <0.5 <0.5 0.1 J <0.8 <0.5 <0.5 <0.5
10/19/2012 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1
5/2/2013 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1
9/27/2013 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0098 <0.1 <0.1 0.1 J <0.2 <0.1 <0.1 <0.1
5/20/2014
10/6/2014
5/19/2015
10/16/2018
10/29/2019
5/20/2020
11/20/2020
4/16/2021
10/29/2021
4/19/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.021 <0.1 NA NA NA NA NA NA
4/26/2011 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 <0.1 0.22 <0.1 NA NA NA
10/14/2011 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 0.2 J <0.8 <0.5 <0.5 <0.5
3/21/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 <0.5 <0.8 <0.5 <0.5 <0.5
4/17/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.029 <0.5 <0.5 0.1 J <0.8 <0.5 <0.5 <0.5
7/20/2012 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.030 <0.5 <0.5 0.5 <0.8 <0.5 <0.5 <0.5
10/19/2012 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1
5/2/2013 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.0096 <0.1 <0.1 0.1 J <0.2 <0.1 <0.1 <0.1
9/27/2013
5/20/2014
10/6/2014
5/19/2015
4/12/2016 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.0095 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.1
10/19/2016 <0.1 <0.1 <0.1 <0.2 <0.1 <0.1 <0.0095 <0.1 <0.1 0.20 J <0.2 <0.1 <0.1 <0.1
4/6/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0095 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
10/19/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0097 <0.13 <0.13 0.32 J <1.0 <0.13 <0.13 <0.13
4/5/2018 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0093 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
10/16/2018 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 0.26 J <1.0 <0.13 <0.13 <0.13
4/22/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0091 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
11/22/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
5/20/2020 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
11/20/2020 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
4/16/2021 <0.50 <0.50 <0.50 <1.5 <0.50 <0.50 <0.020 <0.50 <0.50 <2.0 <0.50 <0.50 <0.50
10/29/2021 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0038 <0.13 <0.13 1.2 <1.0 <0.13 <0.13 <0.13
4/29/2022 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0096 <0.13 <0.13 <0.13 <1.0 <0.13 <0.13 <0.13
10/25/2022 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0097 <0.13 <0.13 1.5 <1.0 NA <0.13 <0.13
WSW - 6
Wallace
6325 Burmith Ave.
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power (property is connected to city water)
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - Inoperable Pump Due to Lack of Power
WSW-5
Young
6308 Burmith Ave.
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Page 3 of 4
TABLE 6
WATER SUPPLY WELL ANALYTICAL RESULTS
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Water Supply Well
Sampling
Date Benzene Toluene Ethylbenzene Total Xylenes MTBE IPE EDB* Naphthalene Bromodichloromethane Chloroform Methylene Chloride 1,2-Dichloroethane Tetrachloroethene Dibromochloromethane1 600 600 500 20 70 0.02 6 0.6 70 5 0.4 0.7 0.42L Standard
9/28/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 NA NA NA NA NA NA
10/30/2007 <0.5 <0.7 <0.8 <0.8 <0.5 <0.8 <1 <1 14 52 4 NA NA NA
5/5/2008
10/14/2008
4/8/2009
4/19/2010 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 12 35 3.1 NA NA NA
10/6/2010
4/26/2011 <0.1 <0.1 <0.1 <0.2 <0.2 <0.1 <0.022 <0.1 13 22 5.3 NA NA NA
10/14/2011
3/21/2012
4/17/2012
7/20/2012
10/19/2012
5/2/2013
9/27/2013
5/20/2014
10/6/2014
5/19/2015
10/19/2017 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0096 <0.13 11.9 15.0 0.21 J <0.13 <0.13 6.1
4/5/2018 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0093 <0.13 9.4 22.2 <1.0 <0.13 <0.13 3.6
10/16/2018
4/22/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0093 <0.13 5.8 18.4 <1.0 <0.13 <0.13 3.6
11/22/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.13 <0.13 9.4 27.5 <1.0 <0.13 <0.13 2.7
11/20/2020 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.13 <0.13 7.4 25.1 <1.0 <0.13 <0.13 1.6
4/16/2021
10/29/2021
Notes:
1. "<" or ND = Not detected at or above the method detection limit
2. Concentrations are reported in micrograms per liter (ug/l) or parts per billion (ppb) equivalents
3. 2L Standard = Title 15A NCAC 2L .0202 Groundwater Standard.
4. Values in BOLD indicate levels above 2L Groundwater Standards.
5. BTEX = Benzene, Toluene, Ethylbenzene, Total Xylenes
6. MTBE = Methyl Tertiary Butyl Ether
7. IPE = Isopropyl Ether
8. EDB = Ethylene Dibromide (1,2-Dibromoethane)
9. EDB* analyzed using EPA Method 504.1, except samples collected in April 2016 which were analyzed for EDB by Method 8011. 10. J = Estimated Value
Not Available for Sampling - No Response from Property Owner/Occupant
WSW-7
Picklesimer
6240 Burmith Ave.
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - Inoperable Pump Due to Lack of Power (property is connected to city water)
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - Inoperable Pump Due to Lack of Power (property is connected to city water)
Not Available for Sampling-No Response from Property Owner/Occupant
Not Available for Sampling
Not Available for Sampling - No Response from Property Owner/Occupant
Not Available for Sampling - No Response from Property Owner/Occupant
Page 4 of 4
TABLE 7
REMEDIAL SYSTEM SAMPLING
NPDES Permit NCG10000, Effective 10/1/2016
Former Star-Brite Laundry
5639 Statesville Road
Charlotte, North Carolina
NCDEQ Incident No.: 15635
RM No.: 0528
Sample
Location
Sample
Date
Benzene (ug/L)Toluene (ug/L)Ethylbenzene (ug/L)Total Xylenes (ug/L)MTBE (ug/L)1,2-Dichloroethane (ug/L)Lead (ug/L)Naphthalene (ug/L)Total Suspended Solids (mg/L) pH10/19/2016 0.16 J <0.13 <0.13 <0.31 361 6.6 NA 0.29 J NA NA
01/19/17 0.18 J <0.13 <0.13 <0.25 318 7.3 <5.0 0.25 J <2,500 NA
04/05/17 <0.13 <0.13 <0.13 <0.25 177 4.2 15.6 <0.13 <2,500 NA
07/17/17 <0.13 <0.13 <0.13 <0.25 113 3.9 7.0 0.13 J <2,500 NA
10/19/17 <0.13 <0.13 <0.13 <0.25 226 3.2 8.9 <0.63 <25,000 NA
01/30/18 <0.13 <0.13 <0.13 <0.25 204 4.7 <5.0 0.34 J <25,000 NA
03/22/18 <0.13 <0.13 <0.13 <0.25 197 4.3 11.4 0.39 J <2,500 NA
04/05/18 <0.13 <0.13 <0.13 <0.25 90.1 2.5 <5.0 <0.13 <5,000 NA
11/20/20 <0.25 <0.25 <0.25 <0.50 82.9 2.8 NA 0.50 J NA NA
10/20/21 <0.13 <0.13 <0.13 <0.25 119 3 1.8 J NA <5.0 6.37
01/18/22 <0.25 <0.25 <0.25 <0.50 48.3 1.8 4.8 J NA <4.2 5.78
04/13/22 <0.25 <0.25 <0.25 <0.50 26.9 1.2 3.7 J NA <2.5 7.14
10/25/22 <0.13 <0.13 <0.13 <0.25 30.2 1.7 <1.1 NA <2.5 6.35
05/17/18 <0.13 <0.13 <0.13 <0.25 195 3.7 <5.0 0.42 J <25,000 NA
07/23/18 <0.63 <0.63 <0.63 <1.3 146 3.7 <5.0 <0.63 <25,000 NA
10/16/18 <0.13 <0.13 <0.13 <0.25 123 3.4 NA 0.22 J NA NA
02/22/19 <0.13 <0.13 <0.13 <0.25 37.6 1.8 <5.0 NA <25,000 6.78
04/22/19 0.19 J <0.13 <0.13 <0.25 104 2.8 NA 0.61 NA NA
07/19/19 <0.13 <0.13 <0.13 <0.25 17.5 1 21.4 NA <25,000 NA
10/31/19 <0.13 <0.13 <0.13 <0.25 39.2 1.2 NA <0.13 NA NA
04/10/20 0.22 J <0.13 <0.13 0.22 J 43.2 1.9 NA <0.13 NA 6.55
08/06/20 <0.13 <0.13 <0.13 <0.13 47.4 1.7 5.9 <0.13 104 7.5
10/16/20 0.14 J <0.13 <0.13 <0.25 75.3 2.8 6.3 NA 8.0 6.71
10/20/21 <0.13 <0.13 <0.13 <0.25 94.8 2 70.9 NA <10 6.37
01/18/22 <0.13 <0.13 <0.13 <0.25 36.3 1.4 4.1 J NA <3.3 6.52
04/13/22 <0.31 <0.31 <0.31 <0.63 13.1 0.60 J 7.5 NA <5.6 7.36
10/25/22 <0.13 <0.13 <0.13 <0.25 <0.13 1 <1.1 NA <5.0 6.43
05/17/18 <0.13 <0.13 <0.13 <0.25 2,490 56.7 10.0 <0.13 <25,000 NA
07/23/18 <6.3 <6.3 <6.3 <13 3,660 84.8 20.7 <6.3 <25,000 NA
10/16/18 <13 <13 <13 <25 3,530 74.0 NA <13 NA NA
02/22/19 <6.3 <6.3 <6.3 <13 2,400 54.9 <5.0 NA <25,000 6.24
04/22/19 <6.3 <6.3 <6.3 <13 1,280 29.9 NA <6.3 NA NA
07/19/19 <2.5 <2.5 <2.5 <5.0 828 21.5 17.2 NA <25,000 NA
10/11/19 <2.5 6.2 J <2.5 <5.0 517 15.4 6.0 NA 43,000 NA
04/10/20 <0.63 0.83 J 1.2 J 5.2 J 243 7.8 3.7 J <0.63 8.3 J 6.52
10/16/20 0.39 J <0.31 <0.31 <0.63 104 4.7 1.3 J NA 53.2 6.37
10/20/21 <0.13 <0.13 <0.13 <0.25 134 3.3 <1.1 NA <5.0 6.31
01/18/22 <0.25 <0.25 <0.25 <0.50 85.9 3.2 4.1 J NA <4.4 6.13
04/13/22 <0.13 <0.13 <0.13 <0.25 70.5 3.3 2.1 J NA <2.6 7.46
10/25/22 <0.13 <0.13 <0.13 <0.25 45.7 2.7 11.7 NA 3.7 J 6.39
10/19/2016 <0.13 <0.13 <0.13 <0.31 <0.13 <0.13 <5.0 <0.13 <2.5 6.90
01/19/17 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <2.5 6.99
04/06/17 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <2.5 8.16
07/17/17 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <2.5 6.71
10/19/17 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <25 7.44
01/30/18 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <25 7.94
04/05/18 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <3 7.65
07/23/18 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <25 7.69
10/16/18 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <3 6.23
02/22/19 <0.13 <0.13 <0.13 <0.25 0.81 <0.13 <5.0 NA <3 7.51
4/22/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 <0.13 <2.5 7.61
7/19/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 NA <25 7.43
10/11/2019 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <5.0 NA 4.0 J 7.54
4/10/20 <0.13 0.15 J <0.13 <0.25 <0.13 <0.13 <5.0 NA 0.39 7.27
10/16/2020 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <1.1 NA 5.0 J 7.46
8/6/2020 <0.13 <0.13 <0.13 <0.25 0.14J <0.13 <0.13 <0.13 5.4 J 7.50
11/20/2020 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 NA <0.13 NA NA
10/20/2021 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <1.1 NA <5.0 7.82
1/18/2022 <0.13 <0.13 <0.13 <0.25 1.2 <0.13 1.4 J NA <4.3 7.78
4/13/2022 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <1.1 NA <6.3 7.70
10/25/22 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <1.1 NA <2.5 7.69
51 11 97 670 1,500 -----3 -----30 6 ≤ pH ≤ 9
Notes:
1. "<" = Not detected at or above the method detection limit
2. J = Estimated Value
3. NA = Not Analyzed
4. MTBE = Methyl Tertiary Butyl Ether
NPDES Permit Effluent Limits
Influent
Influent (RW-1)
Influent (RW-3)
Effluent
Page 1 of 1
Former Star-Brite Laundry Facility (RM No. 0528)

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
FIGURES
SITE LOCATION MAP
1"= 2,000'
1
Project Number:
Date:Scale:
Drawing File:
Figure:
App'd By:
Drn. By:
Ckd. By:
N
H:\2020\OTHER OFFICES\NORTH CAROLINA\NCDEQ-STATE LEAD\PHILLIP 66\RM #0528\P660528013-VIC.DWG, FIG106/19/2020
SEE LOWER LEFT
FORMER STAR-BRITE LAUNDRY FACILITY (RM 0528)
5639 STATESVILLE ROAD
CHARLOTTE, NORTH CAROLINA
P660528013 DH
SB
JW
XXXXXXXXXXXXXXXXXX XXXXDDDDDDDDDDDDDDDDDSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTMW-7MW-12DRW-2MW-8ARW-3MW-4DMW-10DRW-1MW-1AMW-9AMW-3RMW-2AMW-5AMW-11DAMW-6RPELICAN SNOBALLTREATMENTSYSTEMENCLOSURE
DISCHARGECONNECTIONPOINTBURMITH AVENUESTATESVILLE ROADLEGEND:SITE PROPERTY LINENOTE: ALL LOCATIONS ARE APPROXIMATEPARCEL LINEMONITORING WELL (TYPE II)Well IdentificationMW-1ASTSTORM SEWERDISCHARGE LINEDDMONITORING WELL (TYPE III)Well IdentificationMW-4DSCALE: 1" = 20'2005101520NCBCBCBCBRECOVERY WELLRW-1Well IdentificationXXFENCECATCH BASINCBFigure:Drawing File:
Project Number:
Ckd. By:
Drn. By:
App'd By:
Ckd. Date:Scale:Date:H:\2020\OTHER OFFICES\NORTH CAROLINA\NCDEQ-STATE LEAD\PHILLIP 66\RM #0528\P660528013-SITE.DWG, FIG2
SITE MAP07/20/2020SEE LOWER LEFTFORMER STAR-BRITE LAUNDRY FACILITY (RM 0528)
5639 STATESVILLE ROAD
CHARLOTTE, NORTH CAROLINA
P660528013AS SHOWNDH
JW2NOTES:
1.Features shown are not an authoritative location, nor are they presented
to a stated accuracy.
COORDINATE SYSTEM:
NAD 1983 NORTH CAROLINA STATE PLANE FIPS 3200, US SURVEY FEET
XXXXXXXXXXXXXXXXXXXXXX
DDDDDDDDDDDDDDDDDSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTMW-7MW-12DRW-2MW-8ARW-3MW-4DMW-10DRW-1MW-1AMW-9AMW-3RMW-2AMW-5AMW-11DAMW-6RPELICAN SNOBALLTREATMENTSYSTEMENCLOSURE
DISCHARGECONNECTIONPOINTBURMITH AVENUESTATESVILLE ROADLEGEND:SITE PROPERTY LINENOTE: ALL LOCATIONS ARE APPROXIMATEPARCEL LINESTSTORM SEWERDISCHARGE LINEDDMONITORING WELL (TYPE III)Well IdentificationMW-4DCBCBCBCBRECOVERY WELLRW-1Well IdentificationXXFENCECATCH BASINCBMW-1A<0.13MONITORING WELL (TYPE II)Well Identification1,2-DCE Concentration (µg/L).0.41,2-DCE ISOCONCENTRATION CONTOUR(DASHED WHERE INFERRED)(µg/L)SCALE: 1" = 20'05101520N0.43J<0.13<0.13<0.13<0.13<0.130.34J<0.130.20J2.2<0.13<0.13<0.13NS1.20.4Figure:Drawing File:
Project Number:
Ckd. By:
Drn. By:
App'd By:
Ckd. Date:Scale:Date:H:\2023\1 OTHER OFFICES\NORTH CAROLINA\NCDEQ-STATE LEAD\PHILLIP 66\RM #0528\P660528016-12DCE.DWG, FIG5
DISSOLVED 1,2 - DICHLOROETHANE
ISOCONCENTRATION MAP01/05/2023SEE LOWER LEFTFORMER STAR-BRITE LAUNDRY FACILITY (RM 0528)
5639 STATESVILLE ROAD
CHARLOTTE, NORTH CAROLINA
P660528016AS SHOWNBM
BB5NOTES:
1.Features shown are not an authoritative location, nor are they
presented to a stated accuracy.
2.Groundwater elevations were measured October 25, 2022.
3.
Groundwater measured in micrograms per liter (µg/L).
4.NS = Not Sampled.
5.J = Estimated value between the laboratory reporting and method
detection limits.
COORDINATE SYSTEM:
NAD 1983 NORTH CAROLINA STATE PLANE FIPS 3200, US SURVEY FEET
XXXXXXXXXXXXXXXXXX XXXXDDDDDDDDDDDDDDDDDSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTMW-7MW-12DRW-2MW-8ARW-3MW-4DMW-10DRW-1MW-1AMW-9AMW-3RMW-2AMW-5AMW-11DAMW-6RPELICAN SNOBALLTREATMENTSYSTEMENCLOSURE
DISCHARGECONNECTIONPOINTBURMITH AVENUESTATESVILLE ROADLEGEND:SITE PROPERTY LINENOTE: ALL LOCATIONS ARE APPROXIMATEPARCEL LINESTSTORM SEWERDISCHARGE LINEDDMONITORING WELL (TYPE II)Well IdentificationMW-1ACBCBCBCBRECOVERY WELLRW-1Well IdentificationXXFENCECATCH BASINCB72.2772.32MW-4D70.76MONITORING WELL (TYPE III)Well IdentificationRelative Groundwater Elevation (ft)72.0GROUNDWATER ELEVATION CONTOUR(DASHED WHERE INFERRED)GROUNDWATER FLOW DIRECTIONSCALE: 1" = 20'05101520N71.4970.767
1
.
5
0
7
1
.
7
5
72.0Figure:Drawing File:
Project Number:
Ckd. By:
Drn. By:
App'd By:
Ckd. Date:Scale:Date:H:\2023\1 OTHER OFFICES\NORTH CAROLINA\NCDEQ-STATE LEAD\PHILLIP 66\RM #0528\P660528016-DEEP.DWG, FIG3B
DEEP GROUNDWATER ELEVATION
CONTOUR MAP01/05/2023SEE LOWER LEFTFORMER STAR-BRITE LAUNDRY FACILITY (RM 0528)
5639 STATESVILLE ROAD
CHARLOTTE, NORTH CAROLINA
P660528016AS SHOWNBM
BB3bNOTES:
1.Features shown are not an authoritative location, nor are they presented
to a stated accuracy.
2.Groundwater elevations were measured October 25, 2022.
COORDINATE SYSTEM:
NAD 1983 NORTH CAROLINA STATE PLANE FIPS 3200, US SURVEY FEET
XXXXXXXXXXXXXXXXXXXXXX
DDDDDDDDDDDDDDDDDSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTMW-7MW-12DRW-2MW-8ARW-3MW-4DMW-10DRW-1MW-1AMW-9AMW-3RMW-2AMW-5AMW-11DAMW-6RPELICAN SNOBALLTREATMENTSYSTEMENCLOSURE
DISCHARGECONNECTIONPOINTBURMITH AVENUESTATESVILLE ROADLEGEND:SITE PROPERTY LINENOTE: ALL LOCATIONS ARE APPROXIMATEPARCEL LINESTSTORM SEWERDISCHARGE LINEDDMONITORING WELL (TYPE III)Well IdentificationMW-4DCBCBCBCBRECOVERY WELLRW-1Well IdentificationXXFENCECATCH BASINCBMW-1A<0.13MONITORING WELL (TYPE II)Well IdentificationMTBE Concentration (µg/L).20MTBE ISOCONCENTRATION CONTOUR(DASHED WHERE INFERRED)(µg/L)SCALE: 1" = 20'05101520N0.63<0.13<0.13<0.13<0.13<0.13<0.13<0.13<0.1338.8<0.13<0.13<0.13NS29.12
0
Figure:Drawing File:
Project Number:
Ckd. By:
Drn. By:
App'd By:
Ckd. Date:Scale:Date:H:\2023\1 OTHER OFFICES\NORTH CAROLINA\NCDEQ-STATE LEAD\PHILLIP 66\RM #0528\P660528016-MTBE.DWG, FIG4
DISSOLVED METHYL TERTIARY BUTYL ETHER
ISOCONCENTRATION MAP01/05/2023SEE LOWER LEFTFORMER STAR-BRITE LAUNDRY FACILITY (RM 0528)
5639 STATESVILLE ROAD
CHARLOTTE, NORTH CAROLINA
P660528016AS SHOWNBM
BB4NOTES:
1.Features shown are not an authoritative location, nor are they presented
to a stated accuracy.
2.Groundwater elevations were measured October 25, 2022.
3.
Groundwater measured in micrograms per liter (µg/L).
4.NS = Not Sampled.
COORDINATE SYSTEM:
NAD 1983 NORTH CAROLINA STATE PLANE FIPS 3200, US SURVEY FEET
XXXXXXXXXXXXXXXXXX XXXXDDDDDDDDDDDDDDDDDSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTMW-7MW-12DRW-2MW-8ARW-3MW-4DMW-10DRW-1MW-1AMW-9AMW-3RMW-2AMW-5AMW-11DAMW-6RPELICAN SNOBALLTREATMENTSYSTEMENCLOSURE
DISCHARGECONNECTIONPOINTBURMITH AVENUESTATESVILLE ROADLEGEND:SITE PROPERTY LINENOTE: ALL LOCATIONS ARE APPROXIMATEPARCEL LINESTSTORM SEWERDISCHARGE LINEDDMONITORING WELL (TYPE III)Well IdentificationMW-4DCBCBCBCBRECOVERY WELLRW-1Well IdentificationXXFENCECATCH BASINCB72.9072.3172.2871.6971.4171.30NSNSNSNSDRY72.50
72
.
2
5
72
.
0
71
.
7
5
71.
5
0 MW-1A71.41MONITORING WELL (TYPE II)Well IdentificationRelative Groundwater Elevation (ft)72.5GROUNDWATER ELEVATION CONTOUR(DASHED WHERE INFERRED)GROUNDWATER FLOW DIRECTIONSCALE: 1" = 20'05101520NFigure:Drawing File:
Project Number:
Ckd. By:
Drn. By:
App'd By:
Ckd. Date:Scale:Date:H:\2023\1 OTHER OFFICES\NORTH CAROLINA\NCDEQ-STATE LEAD\PHILLIP 66\RM #0528\P660528016-SHALLOW.DWG, FIG3A
SHALLOW GROUNDWATER ELEVATION
CONTOUR MAP01/05/2023SEE LOWER LEFTFORMER STAR-BRITE LAUNDRY FACILITY (RM 0528)
5639 STATESVILLE ROAD
CHARLOTTE, NORTH CAROLINA
P660528016AS SHOWNBM
BB3aNOTES:
1.Features shown are not an authoritative location, nor are they presented
to a stated accuracy.
2.Groundwater elevations were measured October 25, 2022.
3.NM = Not Measured.
4.NS = Not Surveyed.
COORDINATE SYSTEM:
NAD 1983 NORTH CAROLINA STATE PLANE FIPS 3200, US SURVEY FEET
ASSOCIATES OF NORTH CAROLINA, P.C.
[phone] FAX [phone]
PROJECT NO.
Charlotte, North Carolina 28217
NOTES:
DATE
TITLE
SCALEREV. BYPREP. BYCAD FILE
Former Star-Brite Laundry Facility (RM No. 0528)

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
GRAPHS
0
500
1,000
1,500
2,000
2,500
3,000
3,500
4,000
Micograms per liter (µg/L)Date
MTBE Influent Concentration Trend Graph -RW-3
MTBE
Page 1 of 1
Former Star-Brite Laundry Facility (RM No. 0528)

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
APPENDIX A

LABORATORY ANALYTICAL RESULTS
(MONITORING AND SUPPLY WELL SAMPLING)

11/22/22
Technical Report for
ATC Group Services LLC
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
RM0528
SGS Job Number: FC60
Sampling Date: 10/25/22
Report to:
ATC Group Services LLC.
7606 Whitehall Executive Center Dr. Suite 800
Charlotte, NC 28273
[e-mail]
ATTN: Rick Kleinfelter
Total number of pages in report:
Certifications: FL(E83510), LA(03051), KS(E-10327), NC(573), NJ(FL002), NY(12022), SC(96038001)
DoD ELAP(ANAB L2229), AZ(AZ0806), CA(2937), TX(T104704404), PA(68-03573), VA(460177),
AL, AK, AR, CT, IA, KY, MA, MI. MS, ND, NH, NV, OK, OR, IL, UT, VT, WA, WI, 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 11/22/22
e-Hardcopy 2.0
Automated Report
109
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]
1 of 109
FC60
Table of Contents
-1-
Sections:
Section 1: Sample Summary ...................................................................................................3
Section 2: Summary of Hits ....................................................................................................5
Section 3: Sample Results ........................................................................................................8
3.1: FC60-1: MW-1A ...........................................................................................................9
3.2: FC60-2: MW-3R ...........................................................................................................13
3.3: FC60-3: MW-4D ...........................................................................................................17
3.4: FC60-4: MW-5A ...........................................................................................................21
3.5: FC60-5: MW-6R ...........................................................................................................25
3.6: FC60-6: MW-8A ...........................................................................................................29
3.7: FC60-7: 9A-9A .............................................................................................................33
3.8: FC60-8: MW-10D .........................................................................................................37
3.9: FC60-9: MW-11DA ......................................................................................................41
3.10: FC60-10: MW-12D .....................................................................................................45
3.11: FC60-11: RW-1 ...........................................................................................................49
3.12: FC60-12: RW-2 ...........................................................................................................53
3.13: FC60-13: RW-3 ...........................................................................................................57
3.14: FC60-14: WSW-1 .......................................................................................................61
3.15: FC60-15: WSW-2 .......................................................................................................65
3.16: FC60-16: WSW-6 .......................................................................................................69
Section 4: Misc. Forms ............................................................................................................73
4.1: Chain of Custody ...........................................................................................................74
Section 5: MS Volatiles - QC Data Summaries .....................................................................78
5.1: Method Blank Summary ................................................................................................79
5.2: Blank Spike Summary ...................................................................................................89
5.3: Matrix Spike/Matrix Spike Duplicate Summary ...........................................................96
Section 6: GC Volatiles - QC Data Summaries .....................................................................106
6.1: Method Blank Summary ................................................................................................107
6.2: Blank Spike/Blank Spike Duplicate Summary ..............................................................108
6.3: Matrix Spike/Matrix Spike Duplicate Summary ...........................................................109 1234562 of 109
FC60
SGS North America Inc.
Sample Summary
ATC Group Services LLC
Job No:FC60
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Project No: RM0528
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
FC60-1 10/25/22 13:10 BPNR 10/26/22 AQ Ground Water MW-1A
FC60-2 10/25/22 08:40 BPNR 10/26/22 AQ Ground Water MW-3R
FC60-3 10/25/22 15:10 BPNR 10/26/22 AQ Ground Water MW-4D
FC60-4 10/25/22 09:40 BPNR 10/26/22 AQ Ground Water MW-5A
FC60-5 10/25/22 08:00 BPNR 10/26/22 AQ Ground Water MW-6R
FC60-6 10/25/22 11:30 BPNR 10/26/22 AQ Ground Water MW-8A
FC60-7 10/25/22 11:00 BPNR 10/26/22 AQ Ground Water 9A-9A
FC60-8 10/25/22 14:10 BPNR 10/26/22 AQ Ground Water MW-10D
FC60-9 10/25/22 10:40 BPNR 10/26/22 AQ Ground Water MW-11DA
FC60-10 10/25/22 12:40 BPNR 10/26/22 AQ Ground Water MW-12D
FC60-11 10/25/22 12:00 BPNR 10/26/22 AQ Ground Water RW-1
FC60-12 10/25/22 15:00 BPNR 10/26/22 AQ Ground Water RW-2
3 of 109
FC601
SGS North America Inc.
Sample Summary
(continued)
ATC Group Services LLC
Job No:FC60
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Project No: RM0528
Sample Collected Matrix Client
Number Date Time By Received Code Type Sample ID
FC60-13 10/25/22 12:40 BPNR 10/26/22 AQ Ground Water RW-3
FC60-14 10/25/22 17:05 BPNR 10/26/22 AQ Ground Water WSW-1
FC60-15 10/25/22 17:20 BPNR 10/26/22 AQ Ground Water WSW-2
FC60-16 10/25/22 16:00 BPNR 10/26/22 AQ Ground Water WSW-6
4 of 109
FC601
Summary of Hits Page 1 of 3
Job Number:FC60
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:10/25/22
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FC60-1 MW-1A
Acetone 4.4 J 10 2.0 ug/l SM 6200B
n-Butylbenzene 0.40 J 0.50 0.13 ug/l SM 6200B
sec-Butylbenzene 0.24 J 0.50 0.13 ug/l SM 6200B
Chloroethane 0.25 J 0.50 0.20 ug/l SM 6200B
Ethylbenzene 1.1 0.50 0.13 ug/l SM 6200B
Isopropylbenzene 0.46 J 0.50 0.13 ug/l SM 6200B
Naphthalene 21.2 0.50 0.13 ug/l SM 6200B
n-Propylbenzene 1.5 0.50 0.13 ug/l SM 6200B
1,2,4-Trimethylbenzene 0.14 J 0.50 0.13 ug/l SM 6200B
1,3,5-Trimethylbenzene 0.20 J 0.50 0.13 ug/l SM 6200B
FC60-2 MW-3R
Acetone 2.1 J 10 2.0 ug/l SM 6200B
Naphthalene 0.40 J 0.50 0.13 ug/l SM 6200B
1,3,5-Trimethylbenzene 0.27 J 0.50 0.13 ug/l SM 6200B
FC60-3 MW-4D
Benzene 0.17 J 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 0.43 J 0.50 0.13 ug/l SM 6200B
Methyl Tert Butyl Ether 0.63 0.50 0.13 ug/l SM 6200B
1,2-Dibromoethane a 0.077 0.019 0.0096 ug/l EPA 504.1
FC60-4 MW-5A
No hits reported in this sample.
FC60-5 MW-6R
No hits reported in this sample.
FC60-6 MW-8A
No hits reported in this sample.
FC60-7 9A-9A
Acetone 2.5 J 10 2.0 ug/l SM 6200B
1,2-Dichloroethane 0.34 J 0.50 0.13 ug/l SM 6200B
1,2-Dibromoethane a 0.043 0.019 0.0095 ug/l EPA 504.1
5 of 109
FC602
Summary of Hits Page 2 of 3
Job Number:FC60
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:10/25/22
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FC60-8 MW-10D
1,2-Dichloroethane 0.20 J 0.50 0.13 ug/l SM 6200B
1,2-Dibromoethane b 0.030 0.019 0.0097 ug/l EPA 504.1
FC60-9 MW-11DA
No hits reported in this sample.
FC60-10 MW-12D
No hits reported in this sample.
FC60-11 RW-1
1,2-Dichloroethane 1.2 0.50 0.13 ug/l SM 6200B
Methyl Tert Butyl Ether 29.1 0.50 0.13 ug/l SM 6200B
Naphthalene 0.34 J 0.50 0.13 ug/l SM 6200B
FC60-12 RW-2
No hits reported in this sample.
FC60-13 RW-3
Acetone c 5.4 J 20 4.0 ug/l SM 6200B
1,2-Dichloroethane c 2.2 1.0 0.25 ug/l SM 6200B
Methylene Chloride c 4.5 B 4.0 2.0 ug/l SM 6200B
Methyl Tert Butyl Ether c 38.8 1.0 0.25 ug/l SM 6200B
Naphthalene c 7.3 1.0 0.25 ug/l SM 6200B
FC60-14 WSW-1
Chloroform 0.28 J 0.50 0.13 ug/l SM 6200B
FC60-15 WSW-2
Chloroform 0.24 J 0.50 0.13 ug/l SM 6200B
FC60-16 WSW-6
Chloroform 1.5 0.50 0.13 ug/l SM 6200B
(a) All hits confirmed by dual column analysis.
(b) All hits confirmed by dual column analysis. Quantitation between primary and confirmation differed by >40%.
6 of 109
FC602
Summary of Hits Page 3 of 3
Job Number:FC60
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:10/25/22
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
Lower value reported due to possible coelution.
(c) No BS available for this run. No sample available for re-analysis.
7 of 109
FC602
SGS North America Inc.
Sample Results
Report of Analysis
Orlando, FL
Section 3
8 of 109
FC603
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-1A
Lab Sample ID:FC60-1 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235403.D 1 11/04/22 16:46 SS n/a n/a VA3278
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 4.4 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)ND 2.5 1.3 ug/l
104-51-8 n-Butylbenzene 0.40 0.50 0.13 ug/l J
135-98-8 sec-Butylbenzene 0.24 0.50 0.13 ug/l J
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 0.25 0.50 0.20 ug/l J
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
9 of 109
FC6033.1
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-1A
Lab Sample ID:FC60-1 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 1.1 0.50 0.13 ug/l
591-78-6 2-Hexanone ND 5.0 1.0 ug/l
98-82-8 Isopropylbenzene 0.46 0.50 0.13 ug/l J
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 21.2 0.50 0.13 ug/l
103-65-1 n-Propylbenzene 1.5 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 b 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 0.14 0.50 0.13 ug/l J
108-67-8 1,3,5-Trimethylbenzene 0.20 0.50 0.13 ug/l J
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 97%70-130%
17060-07-0 1,2-Dichloroethane-D4 111%70-130%
2037-26-5 Toluene-D8 98%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
10 of 109
FC6033.1
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-1A
Lab Sample ID:FC60-1 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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 109
FC6033.1
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-1A
Lab Sample ID:FC60-1 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086109.D 1 10/31/22 14:24 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.8 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0095 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 81%63-137%
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
12 of 109
FC6033.1
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-3R
Lab Sample ID:FC60-2 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235404.D 1 11/04/22 17:09 SS n/a n/a VA3278
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 2.1 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)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
13 of 109
FC6033.2
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-3R
Lab Sample ID:FC60-2 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 0.40 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 b 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 0.27 0.50 0.13 ug/l J
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 93%70-130%
17060-07-0 1,2-Dichloroethane-D4 106%70-130%
2037-26-5 Toluene-D8 100%70-130%
460-00-4 4-Bromofluorobenzene 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
14 of 109
FC6033.2
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-3R
Lab Sample ID:FC60-2 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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 109
FC6033.2
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-3R
Lab Sample ID:FC60-2 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086110.D 1 10/31/22 14:44 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.3 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0096 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 82%63-137%
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 109
FC6033.2
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-4D
Lab Sample ID:FC60-3 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235405.D 1 11/04/22 17:31 SS n/a n/a VA3278
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 0.17 0.50 0.13 ug/l J
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 0.43 0.50 0.13 ug/l J
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
17 of 109
FC6033.3
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-4D
Lab Sample ID:FC60-3 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 0.63 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 b 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 94%70-130%
17060-07-0 1,2-Dichloroethane-D4 108%70-130%
2037-26-5 Toluene-D8 102%70-130%
460-00-4 4-Bromofluorobenzene 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
18 of 109
FC6033.3
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-4D
Lab Sample ID:FC60-3 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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 109
FC6033.3
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-4D
Lab Sample ID:FC60-3 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 a CC086260.D 1 11/03/22 09:39 AF 10/28/22 11:45 OP93799 GCC2225
Run #2
Initial Volume Final Volume
Run #1 36.5 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane 0.077 0.019 0.0096 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 128%63-137%
(a) All hits confirmed by dual column analysis.
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 109
FC6033.3
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-5A
Lab Sample ID:FC60-4 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235406.D 1 11/04/22 17:54 SS n/a n/a VA3278
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
21 of 109
FC6033.4
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-5A
Lab Sample ID:FC60-4 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 95%70-130%
17060-07-0 1,2-Dichloroethane-D4 109%70-130%
2037-26-5 Toluene-D8 101%70-130%
460-00-4 4-Bromofluorobenzene 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
22 of 109
FC6033.4
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-5A
Lab Sample ID:FC60-4 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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
23 of 109
FC6033.4
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-5A
Lab Sample ID:FC60-4 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086112.D 1 10/31/22 15:22 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 37.1 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0094 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 80%63-137%
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
24 of 109
FC6033.4
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-6R
Lab Sample ID:FC60-5 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235407.D 1 11/04/22 18:17 SS n/a n/a VA3278
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
25 of 109
FC6033.5
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-6R
Lab Sample ID:FC60-5 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 97%70-130%
17060-07-0 1,2-Dichloroethane-D4 111%70-130%
2037-26-5 Toluene-D8 102%70-130%
460-00-4 4-Bromofluorobenzene 108%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
26 of 109
FC6033.5
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-6R
Lab Sample ID:FC60-5 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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 109
FC6033.5
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-6R
Lab Sample ID:FC60-5 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086113.D 1 10/31/22 15:42 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.7 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0095 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 85%63-137%
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 109
FC6033.5
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-8A
Lab Sample ID:FC60-6 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235408.D 1 11/04/22 18:40 SS n/a n/a VA3278
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
29 of 109
FC6033.6
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-8A
Lab Sample ID:FC60-6 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 97%70-130%
17060-07-0 1,2-Dichloroethane-D4 112%70-130%
2037-26-5 Toluene-D8 98%70-130%
460-00-4 4-Bromofluorobenzene 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
30 of 109
FC6033.6
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-8A
Lab Sample ID:FC60-6 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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
31 of 109
FC6033.6
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-8A
Lab Sample ID:FC60-6 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086115.D 1 10/31/22 16:21 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.2 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0097 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 85%63-137%
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
32 of 109
FC6033.6
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:9A-9A
Lab Sample ID:FC60-7 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235409.D 1 11/04/22 19:03 SS n/a n/a VA3278
Run #2 a A0235353.D 1 11/03/22 02:15 SS n/a n/a VA3276
Run #3 b A0235604.D 1 11/15/22 02:37 SS n/a n/a VA3289
Purge Volume
Run #1 10.0 ml
Run #2 10.0 ml
Run #3 10.0 ml
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone 2.5 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)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 0.34 0.50 0.13 ug/l J
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
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
33 of 109
FC6033.7
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:9A-9A
Lab Sample ID:FC60-7 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
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 c 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 d 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 Run# 3 Limits
1868-53-7 Dibromofluoromethane 98%102%118%70-130%
17060-07-0 1,2-Dichloroethane-D4 116%117%120%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
34 of 109
FC6033.7
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:9A-9A
Lab Sample ID:FC60-7 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Surrogate Recoveries Run# 1 Run# 2 Run# 3 Limits
2037-26-5 Toluene-D8 97%96%98%70-130%
460-00-4 4-Bromofluorobenzene 108%102%104%70-130%
(a) Confirmation run.
(b) Sample re-analyzed beyond hold time. Confirmation run.
(c) Associated ECC outside control limits low.
(d) Associated BS recovery outside control limits low.
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
35 of 109
FC6033.7
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:9A-9A
Lab Sample ID:FC60-7 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 a CC086262.D 1 11/03/22 10:18 AF 10/28/22 11:45 OP93799 GCC2225
Run #2
Initial Volume Final Volume
Run #1 36.8 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane 0.043 0.019 0.0095 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 79%63-137%
(a) All hits confirmed by dual column analysis.
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
36 of 109
FC6033.7
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-10D
Lab Sample ID:FC60-8 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235413.D 1 11/04/22 20:34 SS n/a n/a VA3278
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 0.20 0.50 0.13 ug/l J
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
37 of 109
FC6033.8
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-10D
Lab Sample ID:FC60-8 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 97%70-130%
17060-07-0 1,2-Dichloroethane-D4 113%70-130%
2037-26-5 Toluene-D8 105%70-130%
460-00-4 4-Bromofluorobenzene 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
38 of 109
FC6033.8
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-10D
Lab Sample ID:FC60-8 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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
39 of 109
FC6033.8
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-10D
Lab Sample ID:FC60-8 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 a CC086263.D 1 11/03/22 10:37 AF 10/28/22 11:45 OP93799 GCC2225
Run #2
Initial Volume Final Volume
Run #1 36.2 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane b 0.030 0.019 0.0097 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 80%63-137%
(a) All hits confirmed by dual column analysis.
(b) Quantitation between primary and confirmation differed by >40%. Lower value reported due to possible
coelution.
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
40 of 109
FC6033.8
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-11DA
Lab Sample ID:FC60-9 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235414.D 1 11/04/22 20:57 SS n/a n/a VA3278
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
41 of 109
FC6033.9
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-11DA
Lab Sample ID:FC60-9 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 97%70-130%
17060-07-0 1,2-Dichloroethane-D4 114%70-130%
2037-26-5 Toluene-D8 104%70-130%
460-00-4 4-Bromofluorobenzene 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
42 of 109
FC6033.9
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-11DA
Lab Sample ID:FC60-9 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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
43 of 109
FC6033.9
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-11DA
Lab Sample ID:FC60-9 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086118.D 1 10/31/22 17:19 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 37.0 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0095 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 82%63-137%
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
44 of 109
FC6033.9
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-12D
Lab Sample ID:FC60-10 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235415.D 1 11/04/22 21:19 SS n/a n/a VA3278
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
45 of 109
FC6033.10
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-12D
Lab Sample ID:FC60-10 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 99%70-130%
17060-07-0 1,2-Dichloroethane-D4 114%70-130%
2037-26-5 Toluene-D8 106%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
46 of 109
FC6033.10
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-12D
Lab Sample ID:FC60-10 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated ECC outside control limits low.
(b) Associated BS recovery outside control limits low.
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
47 of 109
FC6033.10
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-12D
Lab Sample ID:FC60-10 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086119.D 1 10/31/22 17:39 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.8 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0095 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 90%63-137%
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
48 of 109
FC6033.10
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:RW-1
Lab Sample ID:FC60-11 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235416.D 1 11/04/22 21:42 SS n/a n/a VA3278
Run #2 a A0235605.D 1 11/15/22 03:00 SS n/a n/a VA3289
Purge Volume
Run #1 10.0 ml
Run #2 10.0 ml
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 1.2 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
49 of 109
FC6033.11
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:RW-1
Lab Sample ID:FC60-11 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 29.1 0.50 0.13 ug/l
91-20-3 Naphthalene 0.34 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 c 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 95%112%70-130%
17060-07-0 1,2-Dichloroethane-D4 112%116%70-130%
2037-26-5 Toluene-D8 105%107%70-130%
460-00-4 4-Bromofluorobenzene 104%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
50 of 109
FC6033.11
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:RW-1
Lab Sample ID:FC60-11 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Sample re-analyzed beyond hold time. Confirmation run.
(b) Associated ECC outside control limits low.
(c) Associated BS recovery outside control limits low.
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
51 of 109
FC6033.11
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW-1
Lab Sample ID:FC60-11 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086120.D 1 10/31/22 17:58 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 35.9 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0097 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 87%63-137%
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
52 of 109
FC6033.11
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:RW-2
Lab Sample ID:FC60-12 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235417.D 1 11/04/22 22:06 SS n/a n/a VA3278
Run #2 a A0235461.D 1 11/08/22 12:57 SS n/a n/a VA3281
Purge Volume
Run #1 10.0 ml
Run #2 10.0 ml
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
53 of 109
FC6033.12
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:RW-2
Lab Sample ID:FC60-12 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 c 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 98%97%70-130%
17060-07-0 1,2-Dichloroethane-D4 115%114%70-130%
2037-26-5 Toluene-D8 107%101%70-130%
460-00-4 4-Bromofluorobenzene 102%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
54 of 109
FC6033.12
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:RW-2
Lab Sample ID:FC60-12 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Confirmation run.
(b) Associated ECC outside control limits low. Results confirmed by re-analysis beyond hold time.
(c) Associated BS recovery outside control limits low. Results confirmed by re-analysis beyond hold time.
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
55 of 109
FC6033.12
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW-2
Lab Sample ID:FC60-12 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086121.D 1 10/31/22 18:18 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.1 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0097 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 84%63-137%
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
56 of 109
FC6033.12
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:RW-3
Lab Sample ID:FC60-13 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 a A0235429.D 2 11/05/22 02:40 SS n/a n/a VA3279
Run #2 b A0235363.D 2 11/03/22 06:03 SS n/a n/a VA3276
Purge Volume
Run #1 10.0 ml
Run #2 10.0 ml
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
67-64-1 Acetone 5.4 20 4.0 ug/l J
71-43-2 Benzene ND 1.0 0.25 ug/l
108-86-1 Bromobenzene ND 1.0 0.25 ug/l
74-97-5 Bromochloromethane ND 1.0 0.25 ug/l
75-27-4 Bromodichloromethane ND 1.0 0.25 ug/l
75-25-2 Bromoform ND 1.0 0.25 ug/l
78-93-3 2-Butanone (MEK)ND 5.0 2.5 ug/l
104-51-8 n-Butylbenzene ND 1.0 0.25 ug/l
135-98-8 sec-Butylbenzene ND 1.0 0.25 ug/l
98-06-6 tert-Butylbenzene ND 1.0 0.25 ug/l
56-23-5 Carbon Tetrachloride ND 1.0 0.25 ug/l
108-90-7 Chlorobenzene ND 1.0 0.25 ug/l
75-00-3 Chloroethane ND 1.0 0.40 ug/l
67-66-3 Chloroform ND 1.0 0.25 ug/l
95-49-8 o-Chlorotoluene ND 1.0 0.25 ug/l
106-43-4 p-Chlorotoluene ND 1.0 0.25 ug/l
124-48-1 Dibromochloromethane ND 1.0 0.25 ug/l
106-93-4 1,2-Dibromoethane ND 1.0 0.25 ug/l
75-71-8 Dichlorodifluoromethane ND 1.0 0.40 ug/l
95-50-1 1,2-Dichlorobenzene ND 1.0 0.25 ug/l
541-73-1 1,3-Dichlorobenzene ND 1.0 0.25 ug/l
106-46-7 1,4-Dichlorobenzene ND 1.0 0.25 ug/l
75-34-3 1,1-Dichloroethane ND 1.0 0.25 ug/l
107-06-2 1,2-Dichloroethane 2.2 1.0 0.25 ug/l
75-35-4 1,1-Dichloroethylene ND 1.0 0.25 ug/l
156-59-2 cis-1,2-Dichloroethylene ND 1.0 0.25 ug/l
156-60-5 trans-1,2-Dichloroethylene ND 1.0 0.25 ug/l
78-87-5 1,2-Dichloropropane ND 1.0 0.25 ug/l
142-28-9 1,3-Dichloropropane ND 1.0 0.25 ug/l
594-20-7 2,2-Dichloropropane ND 1.0 0.25 ug/l
563-58-6 1,1-Dichloropropene ND 1.0 0.25 ug/l
10061-01-5 cis-1,3-Dichloropropene ND 1.0 0.25 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
57 of 109
FC6033.13
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:RW-3
Lab Sample ID:FC60-13 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
10061-02-6 trans-1,3-Dichloropropene ND 1.0 0.25 ug/l
108-20-3 Di-Isopropyl Ether ND 1.0 0.25 ug/l
64-17-5 Ethyl Alcohol c ND 200 130 ug/l
100-41-4 Ethylbenzene ND 1.0 0.25 ug/l
591-78-6 2-Hexanone ND 10 2.0 ug/l
98-82-8 Isopropylbenzene ND 1.0 0.25 ug/l
99-87-6 p-Isopropyltoluene ND 1.0 0.25 ug/l
74-83-9 Methyl Bromide ND 1.0 0.40 ug/l
74-87-3 Methyl Chloride ND 1.0 0.40 ug/l
75-09-2 Methylene Chloride 4.5 4.0 2.0 ug/l B
108-10-1 4-Methyl-2-pentanone (MIBK)ND 5.0 2.5 ug/l
1634-04-4 Methyl Tert Butyl Ether 38.8 1.0 0.25 ug/l
91-20-3 Naphthalene 7.3 1.0 0.25 ug/l
103-65-1 n-Propylbenzene ND 1.0 0.25 ug/l
100-42-5 Styrene ND 1.0 0.25 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 1.0 0.25 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 1.0 0.25 ug/l
127-18-4 Tetrachloroethylene ND 1.0 0.25 ug/l
108-88-3 Toluene ND 1.0 0.25 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 1.0 0.25 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 1.0 0.25 ug/l
71-55-6 1,1,1-Trichloroethane ND 1.0 0.25 ug/l
79-00-5 1,1,2-Trichloroethane ND 1.0 0.25 ug/l
79-01-6 Trichloroethylene ND 1.0 0.25 ug/l
75-69-4 Trichlorofluoromethane d ND 1.0 0.40 ug/l
96-18-4 1,2,3-Trichloropropane ND 1.0 0.25 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 1.0 0.25 ug/l
108-67-8 1,3,5-Trimethylbenzene ND 1.0 0.25 ug/l
108-05-4 Vinyl Acetate ND 10 2.0 ug/l
75-01-4 Vinyl Chloride ND 1.0 0.25 ug/l
m,p-Xylene ND 2.0 0.25 ug/l
95-47-6 o-Xylene ND 1.0 0.25 ug/l
1330-20-7 Xylene (total)ND 3.0 0.50 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 105%102%70-130%
17060-07-0 1,2-Dichloroethane-D4 121%119%70-130%
2037-26-5 Toluene-D8 102%105%70-130%
460-00-4 4-Bromofluorobenzene 98%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
58 of 109
FC6033.13
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:RW-3
Lab Sample ID:FC60-13 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) No BS available for this run. No sample available for re-analysis.
(b) No BFB tune available for this run. Confirmation run.
(c) Associated CCV and ECC outside control limits low.
(d) Associated ECC outside control limits low.
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
59 of 109
FC6033.13
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW-3
Lab Sample ID:FC60-13 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086122.D 1 10/31/22 18:37 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.2 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0097 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 89%63-137%
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
60 of 109
FC6033.13
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:WSW-1
Lab Sample ID:FC60-14 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235462.D 1 11/08/22 13:20 SS n/a n/a VA3281
Run #2 a A0235426.D 1 11/05/22 01:32 SS n/a n/a VA3279
Run #3 b A0235606.D 1 11/15/22 03:22 SS n/a n/a VA3289
Purge Volume
Run #1 10.0 ml
Run #2 10.0 ml
Run #3 10.0 ml
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 0.28 0.50 0.13 ug/l J
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
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
61 of 109
FC6033.14
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:WSW-1
Lab Sample ID:FC60-14 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
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
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 c 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 Run# 3 Limits
1868-53-7 Dibromofluoromethane 99%100%118%70-130%
17060-07-0 1,2-Dichloroethane-D4 116%115%119%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
62 of 109
FC6033.14
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:WSW-1
Lab Sample ID:FC60-14 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Surrogate Recoveries Run# 1 Run# 2 Run# 3 Limits
2037-26-5 Toluene-D8 101%103%105%70-130%
460-00-4 4-Bromofluorobenzene 103%103%99%70-130%
(a) Confirmation run.
(b) Sample re-analyzed beyond hold time. Confirmation run.
(c) Associated CCV and BS outside control limits low. Results confirmed by re-analysis.
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
63 of 109
FC6033.14
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:WSW-1
Lab Sample ID:FC60-14 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086123.D 1 10/31/22 18:57 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 37.1 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0094 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 88%63-137%
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
64 of 109
FC6033.14
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:WSW-2
Lab Sample ID:FC60-15 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235463.D 1 11/08/22 13:45 SS n/a n/a VA3281
Run #2 a A0235607.D 1 11/15/22 03:45 SS n/a n/a VA3289
Purge Volume
Run #1 10.0 ml
Run #2 10.0 ml
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 0.24 0.50 0.13 ug/l J
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
65 of 109
FC6033.15
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:WSW-2
Lab Sample ID:FC60-15 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 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 b 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 98%119%70-130%
17060-07-0 1,2-Dichloroethane-D4 117%121%70-130%
2037-26-5 Toluene-D8 100%105%70-130%
460-00-4 4-Bromofluorobenzene 109%101%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
66 of 109
FC6033.15
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:WSW-2
Lab Sample ID:FC60-15 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Sample re-analyzed beyond hold time. Confirmation run.
(b) Associated CCV and BS outside control limits low. Results confirmed by re-analysis.
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
67 of 109
FC6033.15
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:WSW-2
Lab Sample ID:FC60-15 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086124.D 1 10/31/22 19:16 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.5 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0096 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 91%63-137%
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
68 of 109
FC6033.15
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:WSW-6
Lab Sample ID:FC60-16 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235464.D 1 11/08/22 14:08 SS n/a n/a VA3281
Run #2 a A0235608.D 1 11/15/22 04:08 SS n/a n/a VA3289
Purge Volume
Run #1 10.0 ml
Run #2 10.0 ml
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 1.5 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
69 of 109
FC6033.16
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:WSW-6
Lab Sample ID:FC60-16 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 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 b 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 99%120%70-130%
17060-07-0 1,2-Dichloroethane-D4 117%123%70-130%
2037-26-5 Toluene-D8 102%105%70-130%
460-00-4 4-Bromofluorobenzene 105%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
70 of 109
FC6033.16
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:WSW-6
Lab Sample ID:FC60-16 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Sample re-analyzed beyond hold time. Confirmation run.
(b) Associated CCV and BS outside control limits low. Results confirmed by re-analysis.
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
71 of 109
FC6033.16
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:WSW-6
Lab Sample ID:FC60-16 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086126.D 1 10/31/22 19:55 AF 10/28/22 11:45 OP93799 GCC2221
Run #2
Initial Volume Final Volume
Run #1 36.2 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0097 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 88%63-137%
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
72 of 109
FC6033.16
SGS North America Inc.
Misc. Forms
Custody Documents and Other Forms
Includes the following where applicable:
• Chain of Custody
Orlando, FL
Section 4
73 of 109
FC604
FC60: Chain of Custody
Page 1 of 4
74 of 109
FC6044.1
FC60: Chain of Custody
Page 2 of 4
75 of 109
FC6044.1
SGS Sample Receipt Summary
Job Number:FC60 Client:ATLAS TECHNICAL CONSULTANTS - CH
Date / Time Received:10/26/2022 9:15:00 AM Delivery Method:FEDEX
Project:STARBRITE RM 0528
Airbill #'s:1009 6379 8868
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 DID NOT RECEIVE ANY VOLUME FOR SAMPLE ID: "MW2A".
Cooler Temps (Raw Measured) °C:
Cooler Temps (Corrected) °C:
Cooler 1: (1.2);
Cooler 1: (1.8);
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:0.6; # of Coolers:1
Y or N N/A
12. Residual Chlorine Present?
Residual Chlorine Test Strip Lot #:
Technician:Reviewer:SAMUELM Date:Date: 10/26/2022 9:15:00 A
SM001Rev. Date 05/24/17
FC60: Chain of Custody
Page 3 of 4
76 of 109
FC6044.1
Client has been notified. Client will re-collect the sample.Response:
Response Date:10/26/22CSR:Muna Mohammed
SM001Rev. Date 05/24/17
FC60: Chain of Custody
Page 4 of 4
77 of 109
FC6044.1
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
78 of 109
FC605
Method Blank Summary Page 1 of 1
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3276-MB A0235342.D 1 11/02/22 SS n/a n/a VA3276
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
CAS No.Compound Result RL MDL Units Q
CAS No.Surrogate Recoveries Limits
1868-53-7 Dibromofluoromethane 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 111%70-130%
2037-26-5 Toluene-D8 101%70-130%
460-00-4 4-Bromofluorobenzene 112%70-130%
79 of 109
FC6055.1.1
Method Blank Summary Page 1 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3278-MB A0235398.D 1 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
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
80 of 109
FC6055.1.2
Method Blank Summary Page 2 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3278-MB A0235398.D 1 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
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 90%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%70-130%
2037-26-5 Toluene-D8 101%70-130%
81 of 109
FC6055.1.2
Method Blank Summary Page 3 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3278-MB A0235398.D 1 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 113%70-130%
82 of 109
FC6055.1.2
Method Blank Summary Page 1 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3279-MB A0235425.D 1 11/05/22 SS n/a n/a VA3279
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
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
83 of 109
FC6055.1.3
Method Blank Summary Page 2 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3279-MB A0235425.D 1 11/05/22 SS n/a n/a VA3279
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
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 1.1 2.0 1.0 ug/l J
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 116%70-130%
2037-26-5 Toluene-D8 103%70-130%
84 of 109
FC6055.1.3
Method Blank Summary Page 3 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3279-MB A0235425.D 1 11/05/22 SS n/a n/a VA3279
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 103%70-130%
85 of 109
FC6055.1.3
Method Blank Summary Page 1 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3281-MB A0235458.D 1 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
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
86 of 109
FC6055.1.4
Method Blank Summary Page 2 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3281-MB A0235458.D 1 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
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 92%70-130%
17060-07-0 1,2-Dichloroethane-D4 109%70-130%
2037-26-5 Toluene-D8 101%70-130%
87 of 109
FC6055.1.4
Method Blank Summary Page 3 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3281-MB A0235458.D 1 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 106%70-130%
88 of 109
FC6055.1.4
Blank Spike Summary Page 1 of 1
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3276-BS A0235340.D 1 11/02/22 SS n/a n/a VA3276
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 86%70-130%
17060-07-0 1,2-Dichloroethane-D4 99%70-130%
2037-26-5 Toluene-D8 97%70-130%
460-00-4 4-Bromofluorobenzene 104%70-130%
* = Outside of Control Limits.
89 of 109
FC6055.2.1
Blank Spike Summary Page 1 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3278-BS A0235396.D 1 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
67-64-1 Acetone 50 46.8 94 70-130
71-43-2 Benzene 10 10.7 107 70-130
108-86-1 Bromobenzene 10 10.3 103 70-130
74-97-5 Bromochloromethane 10 10.6 106 70-130
75-27-4 Bromodichloromethane 10 11.0 110 70-130
75-25-2 Bromoform 10 11.2 112 70-130
78-93-3 2-Butanone (MEK)50 44.7 89 70-130
104-51-8 n-Butylbenzene 10 9.6 96 70-130
135-98-8 sec-Butylbenzene 10 10.8 108 70-130
98-06-6 tert-Butylbenzene 10 10.2 102 70-130
56-23-5 Carbon Tetrachloride 10 10.9 109 70-130
108-90-7 Chlorobenzene 10 10.6 106 70-130
75-00-3 Chloroethane 10 6.7 67 60-140
67-66-3 Chloroform 10 10.3 103 70-130
95-49-8 o-Chlorotoluene 10 10.0 100 70-130
106-43-4 p-Chlorotoluene 10 9.9 99 70-130
124-48-1 Dibromochloromethane 10 10.4 104 70-130
106-93-4 1,2-Dibromoethane 10 10.5 105 70-130
75-71-8 Dichlorodifluoromethane 10 7.0 70 60-140
95-50-1 1,2-Dichlorobenzene 10 10.8 108 70-130
541-73-1 1,3-Dichlorobenzene 10 11.2 112 70-130
106-46-7 1,4-Dichlorobenzene 10 10.4 104 70-130
75-34-3 1,1-Dichloroethane 10 11.0 110 70-130
107-06-2 1,2-Dichloroethane 10 10 100 70-130
75-35-4 1,1-Dichloroethylene 10 10.6 106 70-130
156-59-2 cis-1,2-Dichloroethylene 10 10.7 107 70-130
156-60-5 trans-1,2-Dichloroethylene 10 10.8 108 70-130
78-87-5 1,2-Dichloropropane 10 10.3 103 70-130
142-28-9 1,3-Dichloropropane 10 9.9 99 70-130
594-20-7 2,2-Dichloropropane 10 11.6 116 70-130
563-58-6 1,1-Dichloropropene 10 10.9 109 70-130
10061-01-5 cis-1,3-Dichloropropene 10 10.3 103 70-130
10061-02-6 trans-1,3-Dichloropropene 10 10.6 106 70-130
108-20-3 Di-Isopropyl Ether 10 9.8 98 70-130
64-17-5 Ethyl Alcohol 500 450 90 70-130
100-41-4 Ethylbenzene 10 10.5 105 70-130
* = Outside of Control Limits.
90 of 109
FC6055.2.2
Blank Spike Summary Page 2 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3278-BS A0235396.D 1 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
591-78-6 2-Hexanone 50 48.0 96 70-130
98-82-8 Isopropylbenzene 10 10.4 104 70-130
99-87-6 p-Isopropyltoluene 10 10.4 104 70-130
74-83-9 Methyl Bromide 10 5.8 58*60-140
74-87-3 Methyl Chloride 10 8.8 88 60-140
75-09-2 Methylene Chloride 10 8.6 86 70-130
108-10-1 4-Methyl-2-pentanone (MIBK)50 44.7 89 70-130
1634-04-4 Methyl Tert Butyl Ether 10 8.4 84 70-130
91-20-3 Naphthalene 10 10.3 103 70-130
103-65-1 n-Propylbenzene 10 10.2 102 70-130
100-42-5 Styrene 10 10.6 106 70-130
630-20-6 1,1,1,2-Tetrachloroethane 10 10.5 105 70-130
79-34-5 1,1,2,2-Tetrachloroethane 10 10.5 105 70-130
127-18-4 Tetrachloroethylene 10 11.2 112 70-130
108-88-3 Toluene 10 10.2 102 70-130
87-61-6 1,2,3-Trichlorobenzene 10 10.9 109 70-130
120-82-1 1,2,4-Trichlorobenzene 10 10.5 105 70-130
71-55-6 1,1,1-Trichloroethane 10 10.8 108 70-130
79-00-5 1,1,2-Trichloroethane 10 10.7 107 70-130
79-01-6 Trichloroethylene 10 11.0 110 70-130
75-69-4 Trichlorofluoromethane 10 4.6 46*60-140
96-18-4 1,2,3-Trichloropropane 10 9.2 92 70-130
95-63-6 1,2,4-Trimethylbenzene 10 10.1 101 70-130
108-67-8 1,3,5-Trimethylbenzene 10 9.7 97 70-130
108-05-4 Vinyl Acetate 50 60.8 122 70-130
75-01-4 Vinyl Chloride 10 7.2 72 60-140
m,p-Xylene 20 18.9 95 70-130
95-47-6 o-Xylene 10 9.8 98 70-130
1330-20-7 Xylene (total)30 28.6 95 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 86%70-130%
17060-07-0 1,2-Dichloroethane-D4 95%70-130%
2037-26-5 Toluene-D8 98%70-130%
* = Outside of Control Limits.
91 of 109
FC6055.2.2
Blank Spike Summary Page 3 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3278-BS A0235396.D 1 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 102%70-130%
* = Outside of Control Limits.
92 of 109
FC6055.2.2
Blank Spike Summary Page 1 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3281-BS a A0235456.D 1 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
67-64-1 Acetone 50 49.4 99 70-130
71-43-2 Benzene 10 9.6 96 70-130
108-86-1 Bromobenzene 10 9.3 93 70-130
74-97-5 Bromochloromethane 10 9.6 96 70-130
75-27-4 Bromodichloromethane 10 10 100 70-130
75-25-2 Bromoform 10 10.0 100 70-130
78-93-3 2-Butanone (MEK)50 47.4 95 70-130
104-51-8 n-Butylbenzene 10 8.4 84 70-130
135-98-8 sec-Butylbenzene 10 9.4 94 70-130
98-06-6 tert-Butylbenzene 10 8.8 88 70-130
56-23-5 Carbon Tetrachloride 10 10 100 70-130
108-90-7 Chlorobenzene 10 9.4 94 70-130
75-00-3 Chloroethane 10 6.0 60 60-140
67-66-3 Chloroform 10 9.3 93 70-130
95-49-8 o-Chlorotoluene 10 8.8 88 70-130
106-43-4 p-Chlorotoluene 10 8.8 88 70-130
124-48-1 Dibromochloromethane 10 9.4 94 70-130
106-93-4 1,2-Dibromoethane 10 9.5 95 70-130
75-71-8 Dichlorodifluoromethane 10 6.7 67 60-140
95-50-1 1,2-Dichlorobenzene 10 9.4 94 70-130
541-73-1 1,3-Dichlorobenzene 10 9.8 98 70-130
106-46-7 1,4-Dichlorobenzene 10 9.2 92 70-130
75-34-3 1,1-Dichloroethane 10 9.9 99 70-130
107-06-2 1,2-Dichloroethane 10 9.3 93 70-130
75-35-4 1,1-Dichloroethylene 10 9.4 94 70-130
156-59-2 cis-1,2-Dichloroethylene 10 9.6 96 70-130
156-60-5 trans-1,2-Dichloroethylene 10 9.6 96 70-130
78-87-5 1,2-Dichloropropane 10 9.5 95 70-130
142-28-9 1,3-Dichloropropane 10 8.8 88 70-130
594-20-7 2,2-Dichloropropane 10 10.9 109 70-130
563-58-6 1,1-Dichloropropene 10 9.7 97 70-130
10061-01-5 cis-1,3-Dichloropropene 10 9.5 95 70-130
10061-02-6 trans-1,3-Dichloropropene 10 9.4 94 70-130
108-20-3 Di-Isopropyl Ether 10 8.5 85 70-130
64-17-5 Ethyl Alcohol 500 519 104 70-130
100-41-4 Ethylbenzene 10 9.1 91 70-130
* = Outside of Control Limits.
93 of 109
FC6055.2.3
Blank Spike Summary Page 2 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3281-BS a A0235456.D 1 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
591-78-6 2-Hexanone 50 48.6 97 70-130
98-82-8 Isopropylbenzene 10 8.9 89 70-130
99-87-6 p-Isopropyltoluene 10 9.1 91 70-130
74-83-9 Methyl Bromide 10 5.1 51*60-140
74-87-3 Methyl Chloride 10 8.5 85 60-140
75-09-2 Methylene Chloride 10 7.0 70 70-130
108-10-1 4-Methyl-2-pentanone (MIBK)50 44.7 89 70-130
1634-04-4 Methyl Tert Butyl Ether 10 7.6 76 70-130
91-20-3 Naphthalene 10 9.0 90 70-130
103-65-1 n-Propylbenzene 10 8.9 89 70-130
100-42-5 Styrene 10 9.3 93 70-130
630-20-6 1,1,1,2-Tetrachloroethane 10 9.3 93 70-130
79-34-5 1,1,2,2-Tetrachloroethane 10 9.6 96 70-130
127-18-4 Tetrachloroethylene 10 10.1 101 70-130
108-88-3 Toluene 10 9.0 90 70-130
87-61-6 1,2,3-Trichlorobenzene 10 9.7 97 70-130
120-82-1 1,2,4-Trichlorobenzene 10 9.1 91 70-130
71-55-6 1,1,1-Trichloroethane 10 9.7 97 70-130
79-00-5 1,1,2-Trichloroethane 10 9.6 96 70-130
79-01-6 Trichloroethylene 10 9.9 99 70-130
75-69-4 Trichlorofluoromethane 10 7.5 75 60-140
96-18-4 1,2,3-Trichloropropane 10 8.7 87 70-130
95-63-6 1,2,4-Trimethylbenzene 10 8.8 88 70-130
108-67-8 1,3,5-Trimethylbenzene 10 8.5 85 70-130
108-05-4 Vinyl Acetate 50 56.2 112 70-130
75-01-4 Vinyl Chloride 10 6.8 68 60-140
m,p-Xylene 20 16.3 82 70-130
95-47-6 o-Xylene 10 8.2 82 70-130
1330-20-7 Xylene (total)30 24.5 82 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 85%70-130%
17060-07-0 1,2-Dichloroethane-D4 99%70-130%
2037-26-5 Toluene-D8 96%70-130%
* = Outside of Control Limits.
94 of 109
FC6055.2.3
Blank Spike Summary Page 3 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3281-BS a A0235456.D 1 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 101%70-130%
(a) No ECC available for this run.
* = Outside of Control Limits.
95 of 109
FC6055.2.3
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 1
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FC60-13MS A0235354.D 2 11/03/22 SS n/a n/a VA3276
FC60-13MSD A0235355.D 2 11/03/22 SS n/a n/a VA3276
FC60-13 a A0235363.D 2 11/03/22 SS n/a n/a VA3276
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
FC60-13 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
CAS No.Surrogate Recoveries MS MSD FC60-13 Limits
1868-53-7 Dibromofluoromethane 92%90%102%70-130%
17060-07-0 1,2-Dichloroethane-D4 107%103%119%70-130%
2037-26-5 Toluene-D8 92%92%105%70-130%
460-00-4 4-Bromofluorobenzene 96%99%104%70-130%
(a) No BFB tune available for this run. Confirmation run.
* = Outside of Control Limits.
96 of 109
FC6055.3.1
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA99977-6MS A0235410.D 5 11/04/22 SS n/a n/a VA3278
FA99977-6MSD A0235411.D 5 11/04/22 SS n/a n/a VA3278
FA99977-6 a A0235418.D 5 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
FA99977-6 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 22.8 J 250 240 87 250 256 93 6 70-130/20
71-43-2 Benzene ND 50 52.5 105 50 56.2 112 7 70-130/20
108-86-1 Bromobenzene ND 50 47.5 95 50 52.3 105 10 70-130/20
74-97-5 Bromochloromethane ND 50 50.8 102 50 53.8 108 6 70-130/20
75-27-4 Bromodichloromethane ND 50 54.7 109 50 57.5 115 5 70-130/20
75-25-2 Bromoform ND 50 51.0 102 50 56.3 113 10 70-130/20
78-93-3 2-Butanone (MEK)ND 250 232 93 250 237 95 2 70-130/20
104-51-8 n-Butylbenzene ND 50 46.3 93 50 51.4 103 10 70-130/20
135-98-8 sec-Butylbenzene ND 50 50.1 100 50 55.0 110 9 70-130/20
98-06-6 tert-Butylbenzene ND 50 48.4 97 50 53.5 107 10 70-130/20
56-23-5 Carbon Tetrachloride ND 50 52.8 106 50 55.2 110 4 70-130/20
108-90-7 Chlorobenzene ND 50 51.7 103 50 55.3 111 7 70-130/20
75-00-3 Chloroethane ND 50 39.0 78 50 45.7 91 16 60-140/20
67-66-3 Chloroform ND 50 51.5 103 50 54.0 108 5 70-130/20
95-49-8 o-Chlorotoluene ND 50 48.2 96 50 52.2 104 8 70-130/20
106-43-4 p-Chlorotoluene ND 50 48.6 97 50 53.1 106 9 70-130/20
124-48-1 Dibromochloromethane ND 50 47.6 95 50 53.2 106 11 70-130/20
106-93-4 1,2-Dibromoethane ND 50 50.8 102 50 55.7 111 9 70-130/20
75-71-8 Dichlorodifluoromethane ND 50 37.1 74 50 46.0 92 21*60-140/20
95-50-1 1,2-Dichlorobenzene ND 50 52.3 105 50 57.1 114 9 70-130/20
541-73-1 1,3-Dichlorobenzene ND 50 52.8 106 50 57.3 115 8 70-130/20
106-46-7 1,4-Dichlorobenzene ND 50 51.2 102 50 54.0 108 5 70-130/20
75-34-3 1,1-Dichloroethane ND 50 54.5 109 50 58.0 116 6 70-130/20
107-06-2 1,2-Dichloroethane 1.2 J 50 52.3 102 50 55.3 108 6 70-130/20
75-35-4 1,1-Dichloroethylene ND 50 51.7 103 50 56.5 113 9 70-130/20
156-59-2 cis-1,2-Dichloroethylene ND 50 49.4 99 50 54.2 108 9 70-130/20
156-60-5 trans-1,2-Dichloroethylene ND 50 51.8 104 50 56.0 112 8 70-130/20
78-87-5 1,2-Dichloropropane ND 50 51.4 103 50 54.9 110 7 70-130/20
142-28-9 1,3-Dichloropropane ND 50 47.2 94 50 51.8 104 9 70-130/20
594-20-7 2,2-Dichloropropane ND 50 52.5 105 50 54.9 110 4 70-130/20
563-58-6 1,1-Dichloropropene ND 50 50.9 102 50 55.6 111 9 70-130/20
10061-01-5 cis-1,3-Dichloropropene ND 50 41.4 83 50 46.5 93 12 70-130/20
10061-02-6 trans-1,3-Dichloropropene ND 50 48.6 97 50 52.9 106 8 70-130/20
108-20-3 Di-Isopropyl Ether 31.5 50 83.4 104 50 87.1 111 4 70-130/20
64-17-5 Ethyl Alcohol ND 2500 1750 70 2500 2160 86 21*70-130/20
100-41-4 Ethylbenzene 2.4 J 50 54.1 103 50 57.9 111 7 70-130/20
* = Outside of Control Limits.
97 of 109
FC6055.3.2
Matrix Spike/Matrix Spike Duplicate Summary Page 2 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA99977-6MS A0235410.D 5 11/04/22 SS n/a n/a VA3278
FA99977-6MSD A0235411.D 5 11/04/22 SS n/a n/a VA3278
FA99977-6 a A0235418.D 5 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
FA99977-6 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 250 252 101 250 257 103 2 70-130/20
98-82-8 Isopropylbenzene ND 50 47.7 95 50 53.8 108 12 70-130/20
99-87-6 p-Isopropyltoluene ND 50 48.2 96 50 52.9 106 9 70-130/20
74-83-9 Methyl Bromide ND 50 38.9 78 50 43.6 87 11 60-140/20
74-87-3 Methyl Chloride ND 50 46.1 92 50 56.9 114 21*60-140/20
75-09-2 Methylene Chloride 22.7 50 57.6 70 50 60.0 75 4 70-130/20
108-10-1 4-Methyl-2-pentanone (MIBK)ND 250 242 97 250 248 99 2 70-130/20
1634-04-4 Methyl Tert Butyl Ether 474 E 50 537 126 50 534 120 1 70-130/20
91-20-3 Naphthalene ND 50 48.7 97 50 56.6 113 15 70-130/20
103-65-1 n-Propylbenzene ND 50 48.4 97 50 52.8 106 9 70-130/20
100-42-5 Styrene ND 50 47.5 95 50 53.2 106 11 70-130/20
630-20-6 1,1,1,2-Tetrachloroethane ND 50 49.4 99 50 54.2 108 9 70-130/20
79-34-5 1,1,2,2-Tetrachloroethane ND 50 53.0 106 50 57.0 114 7 70-130/20
127-18-4 Tetrachloroethylene ND 50 51.1 102 50 56.3 113 10 70-130/20
108-88-3 Toluene ND 50 48.4 97 50 53.3 107 10 70-130/20
87-61-6 1,2,3-Trichlorobenzene ND 50 50.5 101 50 56.2 112 11 70-130/20
120-82-1 1,2,4-Trichlorobenzene ND 50 49.8 100 50 56.0 112 12 70-130/20
71-55-6 1,1,1-Trichloroethane ND 50 52.1 104 50 55.9 112 7 70-130/20
79-00-5 1,1,2-Trichloroethane ND 50 52.3 105 50 56.8 114 8 70-130/20
79-01-6 Trichloroethylene ND 50 53.2 106 50 56.4 113 6 70-130/20
75-69-4 Trichlorofluoromethane ND 50 43.9 88 50 52.1 104 17 60-140/20
96-18-4 1,2,3-Trichloropropane ND 50 45.4 91 50 49.8 100 9 70-130/20
95-63-6 1,2,4-Trimethylbenzene ND 50 48.1 96 50 52.7 105 9 70-130/20
108-67-8 1,3,5-Trimethylbenzene ND 50 46.5 93 50 50.8 102 9 70-130/20
108-05-4 Vinyl Acetate ND 250 323 129 250 328 131*2 70-130/20
75-01-4 Vinyl Chloride ND 50 39.8 80 50 49.5 99 22*60-140/20
m,p-Xylene ND 100 91.9 92 100 99.7 100 8 70-130/20
95-47-6 o-Xylene ND 50 49.3 99 50 54.8 110 11 70-130/20
1330-20-7 Xylene (total)ND 150 141 94 150 155 103 9 70-130/20
CAS No.Surrogate Recoveries MS MSD FA99977-6 Limits
1868-53-7 Dibromofluoromethane 88%86%90%70-130%
17060-07-0 1,2-Dichloroethane-D4 102%99%104%70-130%
2037-26-5 Toluene-D8 97%98%104%70-130%
* = Outside of Control Limits.
98 of 109
FC6055.3.2
Matrix Spike/Matrix Spike Duplicate Summary Page 3 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA99977-6MS A0235410.D 5 11/04/22 SS n/a n/a VA3278
FA99977-6MSD A0235411.D 5 11/04/22 SS n/a n/a VA3278
FA99977-6 a A0235418.D 5 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12
CAS No.Surrogate Recoveries MS MSD FA99977-6 Limits
460-00-4 4-Bromofluorobenzene 100%104%105%70-130%
(a) Sample re-analyzed beyond hold time.
* = Outside of Control Limits.
99 of 109
FC6055.3.2
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FC60-13MS A0235430.D 2 11/05/22 SS n/a n/a VA3279
FC60-13MSD A0235431.D 2 11/05/22 SS n/a n/a VA3279
FC60-13 a A0235429.D 2 11/05/22 SS n/a n/a VA3279
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
FC60-13 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 5.4 J 100 82.4 77 100 81.1 76 2 70-130/20
71-43-2 Benzene ND 20 21.6 108 20 21.7 109 0 70-130/20
108-86-1 Bromobenzene ND 20 20.0 100 20 20.3 102 1 70-130/20
74-97-5 Bromochloromethane ND 20 21.8 109 20 21.8 109 0 70-130/20
75-27-4 Bromodichloromethane ND 20 22.5 113 20 22.4 112 0 70-130/20
75-25-2 Bromoform ND 20 21.3 107 20 21.4 107 0 70-130/20
78-93-3 2-Butanone (MEK)ND 100 89.3 89 100 89.0 89 0 70-130/20
104-51-8 n-Butylbenzene ND 20 17.5 88 20 18.5 93 6 70-130/20
135-98-8 sec-Butylbenzene ND 20 20.3 102 20 21.1 106 4 70-130/20
98-06-6 tert-Butylbenzene ND 20 19.0 95 20 20.0 100 5 70-130/20
56-23-5 Carbon Tetrachloride ND 20 22.1 111 20 22.5 113 2 70-130/20
108-90-7 Chlorobenzene ND 20 21.3 107 20 21.2 106 0 70-130/20
75-00-3 Chloroethane ND 20 20.0 100 20 19.3 97 4 60-140/20
67-66-3 Chloroform ND 20 22.0 110 20 21.8 109 1 70-130/20
95-49-8 o-Chlorotoluene ND 20 19.6 98 20 20.0 100 2 70-130/20
106-43-4 p-Chlorotoluene ND 20 18.7 94 20 19.5 98 4 70-130/20
124-48-1 Dibromochloromethane ND 20 19.8 99 20 20.3 102 2 70-130/20
106-93-4 1,2-Dibromoethane ND 20 19.5 98 20 20.1 101 3 70-130/20
75-71-8 Dichlorodifluoromethane ND 20 18.6 93 20 19.3 97 4 60-140/20
95-50-1 1,2-Dichlorobenzene ND 20 21.3 107 20 21.7 109 2 70-130/20
541-73-1 1,3-Dichlorobenzene ND 20 21.8 109 20 22.3 112 2 70-130/20
106-46-7 1,4-Dichlorobenzene ND 20 20.7 104 20 20.7 104 0 70-130/20
75-34-3 1,1-Dichloroethane ND 20 22.9 115 20 23.1 116 1 70-130/20
107-06-2 1,2-Dichloroethane 2.2 20 22.9 104 20 23.1 105 1 70-130/20
75-35-4 1,1-Dichloroethylene ND 20 22.4 112 20 23.1 116 3 70-130/20
156-59-2 cis-1,2-Dichloroethylene ND 20 20.3 102 20 21.5 108 6 70-130/20
156-60-5 trans-1,2-Dichloroethylene ND 20 21.8 109 20 22.3 112 2 70-130/20
78-87-5 1,2-Dichloropropane ND 20 20.7 104 20 21.0 105 1 70-130/20
142-28-9 1,3-Dichloropropane ND 20 18.5 93 20 19.0 95 3 70-130/20
594-20-7 2,2-Dichloropropane ND 20 17.9 90 20 18.5 93 3 70-130/20
563-58-6 1,1-Dichloropropene ND 20 20.9 105 20 21.7 109 4 70-130/20
10061-01-5 cis-1,3-Dichloropropene ND 20 15.2 76 20 16.4 82 8 70-130/20
10061-02-6 trans-1,3-Dichloropropene ND 20 19.0 95 20 19.4 97 2 70-130/20
108-20-3 Di-Isopropyl Ether ND 20 23.6 118 20 24.5 123 4 70-130/20
64-17-5 Ethyl Alcohol ND 1000 432 43*1000 591 59*31*70-130/20
100-41-4 Ethylbenzene ND 20 21.0 105 20 21.2 106 1 70-130/20
* = Outside of Control Limits.
100 of 109
FC6055.3.3
Matrix Spike/Matrix Spike Duplicate Summary Page 2 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FC60-13MS A0235430.D 2 11/05/22 SS n/a n/a VA3279
FC60-13MSD A0235431.D 2 11/05/22 SS n/a n/a VA3279
FC60-13 a A0235429.D 2 11/05/22 SS n/a n/a VA3279
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
FC60-13 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 100 94.5 95 100 93.7 94 1 70-130/20
98-82-8 Isopropylbenzene ND 20 19.3 97 20 20.4 102 6 70-130/20
99-87-6 p-Isopropyltoluene ND 20 18.9 95 20 19.9 100 5 70-130/20
74-83-9 Methyl Bromide ND 20 20.4 102 20 19.3 97 6 60-140/20
74-87-3 Methyl Chloride ND 20 19.9 100 20 20.1 101 1 60-140/20
75-09-2 Methylene Chloride 4.5 B 20 19.4 75 20 19.7 76 2 70-130/20
108-10-1 4-Methyl-2-pentanone (MIBK)ND 100 92.4 92 100 90.9 91 2 70-130/20
1634-04-4 Methyl Tert Butyl Ether 38.8 20 52.6 69*20 54.5 79 4 70-130/20
91-20-3 Naphthalene 7.3 20 26.3 95 20 27.2 100 3 70-130/20
103-65-1 n-Propylbenzene ND 20 19.1 96 20 19.9 100 4 70-130/20
100-42-5 Styrene ND 20 16.6 83 20 17.4 87 5 70-130/20
630-20-6 1,1,1,2-Tetrachloroethane ND 20 21.3 107 20 21.6 108 1 70-130/20
79-34-5 1,1,2,2-Tetrachloroethane ND 20 22.2 111 20 21.9 110 1 70-130/20
127-18-4 Tetrachloroethylene ND 20 21.5 108 20 21.9 110 2 70-130/20
108-88-3 Toluene ND 20 20.2 101 20 20.5 103 1 70-130/20
87-61-6 1,2,3-Trichlorobenzene ND 20 21.7 109 20 22.4 112 3 70-130/20
120-82-1 1,2,4-Trichlorobenzene ND 20 20.7 104 20 22.1 111 7 70-130/20
71-55-6 1,1,1-Trichloroethane ND 20 21.9 110 20 22.2 111 1 70-130/20
79-00-5 1,1,2-Trichloroethane ND 20 21.4 107 20 21.6 108 1 70-130/20
79-01-6 Trichloroethylene ND 20 22.2 111 20 22.4 112 1 70-130/20
75-69-4 Trichlorofluoromethane ND 20 22.0 110 20 21.7 109 1 60-140/20
96-18-4 1,2,3-Trichloropropane ND 20 19.5 98 20 18.8 94 4 70-130/20
95-63-6 1,2,4-Trimethylbenzene ND 20 19.3 97 20 20.1 101 4 70-130/20
108-67-8 1,3,5-Trimethylbenzene ND 20 18.5 93 20 19.3 97 4 70-130/20
108-05-4 Vinyl Acetate ND 100 117 117 100 115 115 2 70-130/20
75-01-4 Vinyl Chloride ND 20 19.8 99 20 20.4 102 3 60-140/20
m,p-Xylene ND 40 37.1 93 40 37.6 94 1 70-130/20
95-47-6 o-Xylene ND 20 17.9 90 20 18.8 94 5 70-130/20
1330-20-7 Xylene (total)ND 60 55.1 92 60 56.4 94 2 70-130/20
CAS No.Surrogate Recoveries MS MSD FC60-13 Limits
1868-53-7 Dibromofluoromethane 90%89%105%70-130%
17060-07-0 1,2-Dichloroethane-D4 101%105%121%70-130%
2037-26-5 Toluene-D8 95%96%102%70-130%
* = Outside of Control Limits.
101 of 109
FC6055.3.3
Matrix Spike/Matrix Spike Duplicate Summary Page 3 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FC60-13MS A0235430.D 2 11/05/22 SS n/a n/a VA3279
FC60-13MSD A0235431.D 2 11/05/22 SS n/a n/a VA3279
FC60-13 a A0235429.D 2 11/05/22 SS n/a n/a VA3279
The QC reported here applies to the following samples:Method: SM 6200B
FC60-13
CAS No.Surrogate Recoveries MS MSD FC60-13 Limits
460-00-4 4-Bromofluorobenzene 94%98%98%70-130%
(a) No BS available for this run. No sample available for re-analysis.
* = Outside of Control Limits.
102 of 109
FC6055.3.3
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FC170-3MS A0235468.D 1000 11/08/22 SS n/a n/a VA3281
FC170-3MSD A0235469.D 1000 11/08/22 SS n/a n/a VA3281
FC170-3 a A0235467.D 1000 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
FC170-3 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 7830 J 50000 53200 91 50000 52900 90 1 70-130/20
71-43-2 Benzene 7240 10000 17000 98 10000 17400 102 2 70-130/20
108-86-1 Bromobenzene ND 10000 8810 88 10000 9690 97 10 70-130/20
74-97-5 Bromochloromethane ND 10000 9140 91 10000 10300 103 12 70-130/20
75-27-4 Bromodichloromethane ND 10000 9840 98 10000 10800 108 9 70-130/20
75-25-2 Bromoform ND 10000 9520 95 10000 10600 106 11 70-130/20
78-93-3 2-Butanone (MEK)ND 50000 45800 92 50000 47000 94 3 70-130/20
104-51-8 n-Butylbenzene ND 10000 7710 77 10000 8940 89 15 70-130/20
135-98-8 sec-Butylbenzene ND 10000 8610 86 10000 9810 98 13 70-130/20
98-06-6 tert-Butylbenzene ND 10000 8120 81 10000 9310 93 14 70-130/20
56-23-5 Carbon Tetrachloride ND 10000 9360 94 10000 10400 104 11 70-130/20
108-90-7 Chlorobenzene ND 10000 9030 90 10000 10000 100 10 70-130/20
75-00-3 Chloroethane ND 10000 6280 63 10000 8300 83 28*60-140/20
67-66-3 Chloroform ND 10000 9110 91 10000 10000 100 9 70-130/20
95-49-8 o-Chlorotoluene ND 10000 8360 84 10000 9310 93 11 70-130/20
106-43-4 p-Chlorotoluene ND 10000 8240 82 10000 9170 92 11 70-130/20
124-48-1 Dibromochloromethane ND 10000 8740 87 10000 9780 98 11 70-130/20
106-93-4 1,2-Dibromoethane ND 10000 8950 90 10000 9960 100 11 70-130/20
75-71-8 Dichlorodifluoromethane ND 10000 6540 65 10000 8240 82 23*60-140/20
95-50-1 1,2-Dichlorobenzene ND 10000 8920 89 10000 10100 101 12 70-130/20
541-73-1 1,3-Dichlorobenzene ND 10000 9390 94 10000 10400 104 10 70-130/20
106-46-7 1,4-Dichlorobenzene ND 10000 8860 89 10000 9880 99 11 70-130/20
75-34-3 1,1-Dichloroethane ND 10000 9540 95 10000 10500 105 10 70-130/20
107-06-2 1,2-Dichloroethane 315 J 10000 9220 89 10000 10000 97 8 70-130/20
75-35-4 1,1-Dichloroethylene ND 10000 9040 90 10000 10200 102 12 70-130/20
156-59-2 cis-1,2-Dichloroethylene ND 10000 8670 87 10000 10000 100 14 70-130/20
156-60-5 trans-1,2-Dichloroethylene ND 10000 9130 91 10000 10100 101 10 70-130/20
78-87-5 1,2-Dichloropropane ND 10000 9190 92 10000 9910 99 8 70-130/20
142-28-9 1,3-Dichloropropane ND 10000 8190 82 10000 9110 91 11 70-130/20
594-20-7 2,2-Dichloropropane ND 10000 8980 90 10000 10700 107 17 70-130/20
563-58-6 1,1-Dichloropropene ND 10000 9190 92 10000 10200 102 10 70-130/20
10061-01-5 cis-1,3-Dichloropropene ND 10000 9150 92 10000 10000 100 9 70-130/20
10061-02-6 trans-1,3-Dichloropropene ND 10000 8650 87 10000 9630 96 11 70-130/20
108-20-3 Di-Isopropyl Ether 168 J 10000 8050 79 10000 9170 90 13 70-130/20
64-17-5 Ethyl Alcohol ND 500000 395000 79 500000 365000 73 8 70-130/20
100-41-4 Ethylbenzene 1690 10000 10800 91 10000 11700 100 8 70-130/20
* = Outside of Control Limits.
103 of 109
FC6055.3.4
Matrix Spike/Matrix Spike Duplicate Summary Page 2 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FC170-3MS A0235468.D 1000 11/08/22 SS n/a n/a VA3281
FC170-3MSD A0235469.D 1000 11/08/22 SS n/a n/a VA3281
FC170-3 a A0235467.D 1000 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
FC170-3 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 50000 46900 94 50000 47800 96 2 70-130/20
98-82-8 Isopropylbenzene ND 10000 8220 82 10000 9410 94 13 70-130/20
99-87-6 p-Isopropyltoluene ND 10000 8220 82 10000 9480 95 14 70-130/20
74-83-9 Methyl Bromide ND 10000 6390 64 10000 8140 81 24*60-140/20
74-87-3 Methyl Chloride ND 10000 8670 87 10000 10700 107 21*60-140/20
75-09-2 Methylene Chloride 1820 J 10000 7740 59*10000 8550 67*10 70-130/20
108-10-1 4-Methyl-2-pentanone (MIBK)ND 50000 42300 85 50000 44600 89 5 70-130/20
1634-04-4 Methyl Tert Butyl Ether ND 10000 6910 69*10000 7870 79 13 70-130/20
91-20-3 Naphthalene 349 J 10000 7950 76 10000 9850 95 21*70-130/20
103-65-1 n-Propylbenzene 219 J 10000 8480 83 10000 9420 92 11 70-130/20
100-42-5 Styrene ND 10000 8790 88 10000 9640 96 9 70-130/20
630-20-6 1,1,1,2-Tetrachloroethane ND 10000 8630 86 10000 9770 98 12 70-130/20
79-34-5 1,1,2,2-Tetrachloroethane ND 10000 9030 90 10000 9890 99 9 70-130/20
127-18-4 Tetrachloroethylene ND 10000 9320 93 10000 10600 106 13 70-130/20
108-88-3 Toluene 21900 10000 28000 61* b 10000 28400 65* b 1 70-130/20
87-61-6 1,2,3-Trichlorobenzene ND 10000 8500 85 10000 10100 101 17 70-130/20
120-82-1 1,2,4-Trichlorobenzene ND 10000 8030 80 10000 9880 99 21*70-130/20
71-55-6 1,1,1-Trichloroethane ND 10000 9360 94 10000 10400 104 11 70-130/20
79-00-5 1,1,2-Trichloroethane ND 10000 9260 93 10000 10100 101 9 70-130/20
79-01-6 Trichloroethylene ND 10000 9700 97 10000 10500 105 8 70-130/20
75-69-4 Trichlorofluoromethane ND 10000 7530 75 10000 9560 96 24*60-140/20
96-18-4 1,2,3-Trichloropropane ND 10000 8280 83 10000 8890 89 7 70-130/20
95-63-6 1,2,4-Trimethylbenzene 1400 10000 10600 92 10000 11500 101 8 70-130/20
108-67-8 1,3,5-Trimethylbenzene 523 10000 8630 81 10000 9590 91 11 70-130/20
108-05-4 Vinyl Acetate ND 50000 51500 103 50000 57300 115 11 70-130/20
75-01-4 Vinyl Chloride ND 10000 6930 69 10000 8830 88 24*60-140/20
m,p-Xylene 6810 20000 23400 83 20000 24800 90 6 70-130/20
95-47-6 o-Xylene 2630 10000 11200 86 10000 12200 96 9 70-130/20
1330-20-7 Xylene (total)9450 30000 34600 84 30000 37100 92 7 70-130/20
CAS No.Surrogate Recoveries MS MSD FC170-3 Limits
1868-53-7 Dibromofluoromethane 86%86%90%70-130%
17060-07-0 1,2-Dichloroethane-D4 101%99%108%70-130%
2037-26-5 Toluene-D8 92%95%102%70-130%
* = Outside of Control Limits.
104 of 109
FC6055.3.4
Matrix Spike/Matrix Spike Duplicate Summary Page 3 of 3
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FC170-3MS A0235468.D 1000 11/08/22 SS n/a n/a VA3281
FC170-3MSD A0235469.D 1000 11/08/22 SS n/a n/a VA3281
FC170-3 a A0235467.D 1000 11/08/22 SS n/a n/a VA3281
The QC reported here applies to the following samples:Method: SM 6200B
FC60-14, FC60-15, FC60-16
CAS No.Surrogate Recoveries MS MSD FC170-3 Limits
460-00-4 4-Bromofluorobenzene 99%100%106%70-130%
(a) Confirmation run.
(b) Outside control limits due to high level in sample relative to spike amount.
* = Outside of Control Limits.
105 of 109
FC6055.3.4
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
106 of 109
FC606
Method Blank Summary Page 1 of 1
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP93799-MB CC086104.D 1 10/31/22 AF 10/28/22 OP93799 GCC2221
The QC reported here applies to the following samples:Method: EPA 504.1
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12, FC60-13,
FC60-14, FC60-15, FC60-16
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.020 0.010 ug/l
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 99%63-137%
107 of 109
FC6066.1.1
Blank Spike/Blank Spike Duplicate Summary Page 1 of 1
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP93799-BS CC086105.D 1 10/31/22 AF 10/28/22 OP93799 GCC2221
OP93799-BSD CC086106.D 1 10/31/22 AF 10/28/22 OP93799 GCC2221
The QC reported here applies to the following samples:Method: EPA 504.1
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12, FC60-13,
FC60-14, FC60-15, FC60-16
Spike BSP BSP BSD BSD Limits
CAS No.Compound ug/l ug/l %ug/l %RPD Rec/RPD
106-93-4 1,2-Dibromoethane 0.25 0.20 80 0.22 88 10 70-130/25
CAS No.Surrogate Recoveries BSP BSD Limits
460-00-4 4-Bromofluorobenzene 83%92%63-137%
* = Outside of Control Limits.
108 of 109
FC6066.2.1
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 1
Job Number:FC60
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP93799-MS CC086107.D 1 10/31/22 AF 10/28/22 OP93799 GCC2221
OP93799-MSD CC086108.D 1 10/31/22 AF 10/28/22 OP93799 GCC2221
FC125-2 CC086128.D 1 10/31/22 AF 10/28/22 OP93799 GCC2221
The QC reported here applies to the following samples:Method: EPA 504.1
FC60-1, FC60-2, FC60-3, FC60-4, FC60-5, FC60-6, FC60-7, FC60-8, FC60-9, FC60-10, FC60-11, FC60-12, FC60-13,
FC60-14, FC60-15, FC60-16
FC125-2 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
106-93-4 1,2-Dibromoethane 0.019 U 0.242 0.19 79 0.246 0.19 77 0 70-130/25
CAS No.Surrogate Recoveries MS MSD FC125-2 Limits
460-00-4 4-Bromofluorobenzene 103%102%98%63-137%
* = Outside of Control Limits.
109 of 109
FC6066.3.1
11/27/22
Technical Report for
ATC Group Services LLC
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
RM0528
SGS Job Number: FC416
Sampling Date: 11/07/22
Report to:
ATC Group Services LLC.
7606 Whitehall Executive Center Dr. Suite 800
Charlotte, NC 28273
[e-mail]
ATTN: Rick Kleinfelter
Total number of pages in report:
Certifications: FL(E83510), LA(03051), KS(E-10327), NC(573), NJ(FL002), NY(12022), SC(96038001)
DoD ELAP(ANAB L2229), AZ(AZ0806), CA(2937), TX(T104704404), PA(68-03573), VA(460177),
AL, AK, AR, CT, IA, KY, MA, MI. MS, ND, NH, NV, OK, OR, IL, UT, VT, WA, WI, 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 11/27/22
e-Hardcopy 2.0
Automated Report
23
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]
1 of 23
FC416
Table of Contents
-1-
Sections:
Section 1: Sample Summary ...................................................................................................3
Section 2: Summary of Hits ....................................................................................................4
Section 3: Sample Results ........................................................................................................5
3.1: FC416-1: MW-2A .........................................................................................................6
Section 4: Misc. Forms ............................................................................................................10
4.1: Chain of Custody ...........................................................................................................11
Section 5: MS Volatiles - QC Data Summaries .....................................................................13
5.1: Method Blank Summary ................................................................................................14
5.2: Blank Spike Summary ...................................................................................................17
Section 6: GC Volatiles - QC Data Summaries .....................................................................20
6.1: Method Blank Summary ................................................................................................21
6.2: Blank Spike Summary ...................................................................................................22
6.3: Matrix Spike/Matrix Spike Duplicate Summary ...........................................................23 1234562 of 23
FC416
SGS North America Inc.
Sample Summary
ATC Group Services LLC
Job No:FC416
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Project No: RM0528
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
FC416-1 11/07/22 10:40 BP 11/08/22 AQ Ground Water MW-2A
3 of 23
FC4161
Summary of Hits Page 1 of 1
Job Number:FC416
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:11/07/22
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FC416-1 MW-2A
No hits reported in this sample.
4 of 23
FC4162
SGS North America Inc.
Sample Results
Report of Analysis
Orlando, FL
Section 3
5 of 23
FC4163
SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW-2A
Lab Sample ID:FC416-1 Date Sampled:11/07/22
Matrix:AQ - Ground Water Date Received:11/08/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235730.D 1 11/21/22 20:38 SS n/a n/a VA3295
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
6 of 23
FC41633.1
SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW-2A
Lab Sample ID:FC416-1 Date Sampled:11/07/22
Matrix:AQ - Ground Water Date Received:11/08/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, 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 b 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 c 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 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
7 of 23
FC41633.1
SGS North America Inc.
Report of Analysis Page 3 of 3
Client Sample ID:MW-2A
Lab Sample ID:FC416-1 Date Sampled:11/07/22
Matrix:AQ - Ground Water Date Received:11/08/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
VOA List for NC, May 2012
CAS No.Compound Result RL MDL Units Q
(a) Associated Initial Calibration outside control limits (%RSD > 15%); sample is ND.
(b) Associated BS recovery outside control limits high, sample is ND.
(c) Associated ECC outside of control limits high, 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
8 of 23
FC41633.1
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW-2A
Lab Sample ID:FC416-1 Date Sampled:11/07/22
Matrix:AQ - Ground Water Date Received:11/08/22
Method:EPA 504.1 SW846 8011 Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 CC086505.D 1 11/17/22 13:26 AF 11/16/22 10:00 OP94113 GCC2233
Run #2
Initial Volume Final Volume
Run #1 36.2 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0097 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 86%63-137%
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 23
FC41633.1
SGS North America Inc.
Misc. Forms
Custody Documents and Other Forms
Includes the following where applicable:
• Chain of Custody
Orlando, FL
Section 4
10 of 23
FC4164
FC416: Chain of Custody
Page 1 of 2
11 of 23
FC41644.1
Job Number:FC416 Client:ATLAS TECHNICAL CONSULTANTS
Date / Time Received:11/8/2022 9:30:00 AM Delivery Method:FEDEX
Project:STARBRITE
Airbill #'s:1009 6379 9614
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: (4.0);
Cooler 1: (4.6);
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:0.6; # of Coolers:1
Y or N N/A
12. Residual Chlorine Present?
Residual Chlorine Test Strip Lot #:
Technician:Reviewer:SAMUELM Date:Date:11/8/2022 9:30:00 AM
FC416: Chain of Custody
Page 2 of 2
12 of 23
FC41644.1
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
13 of 23
FC4165
Method Blank Summary Page 1 of 3
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3295-MB A0235728.D 1 11/21/22 SS n/a n/a VA3295
The QC reported here applies to the following samples:Method: SM 6200B
FC416-1
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
14 of 23
FC41655.1.1
Method Blank Summary Page 2 of 3
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3295-MB A0235728.D 1 11/21/22 SS n/a n/a VA3295
The QC reported here applies to the following samples:Method: SM 6200B
FC416-1
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 99%70-130%
17060-07-0 1,2-Dichloroethane-D4 101%70-130%
2037-26-5 Toluene-D8 99%70-130%
15 of 23
FC41655.1.1
Method Blank Summary Page 3 of 3
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3295-MB A0235728.D 1 11/21/22 SS n/a n/a VA3295
The QC reported here applies to the following samples:Method: SM 6200B
FC416-1
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 100%70-130%
16 of 23
FC41655.1.1
Blank Spike Summary Page 1 of 3
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3295-BS a A0235726.D 1 11/21/22 SS n/a n/a VA3295
The QC reported here applies to the following samples:Method: SM 6200B
FC416-1
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
67-64-1 Acetone 50 42.6 85 70-130
71-43-2 Benzene 10 9.0 90 70-130
108-86-1 Bromobenzene 10 8.7 87 70-130
74-97-5 Bromochloromethane 10 10 100 70-130
75-27-4 Bromodichloromethane 10 8.6 86 70-130
75-25-2 Bromoform 10 10.3 103 70-130
78-93-3 2-Butanone (MEK)50 50.9 102 70-130
104-51-8 n-Butylbenzene 10 8.8 88 70-130
135-98-8 sec-Butylbenzene 10 9.9 99 70-130
98-06-6 tert-Butylbenzene 10 9.4 94 70-130
56-23-5 Carbon Tetrachloride 10 10.8 108 70-130
108-90-7 Chlorobenzene 10 9.1 91 70-130
75-00-3 Chloroethane 10 6.4 64 60-140
67-66-3 Chloroform 10 8.5 85 70-130
95-49-8 o-Chlorotoluene 10 8.4 84 70-130
106-43-4 p-Chlorotoluene 10 8.8 88 70-130
124-48-1 Dibromochloromethane 10 9.7 97 70-130
106-93-4 1,2-Dibromoethane 10 9.6 96 70-130
75-71-8 Dichlorodifluoromethane 10 7.6 76 60-140
95-50-1 1,2-Dichlorobenzene 10 9.9 99 70-130
541-73-1 1,3-Dichlorobenzene 10 9.9 99 70-130
106-46-7 1,4-Dichlorobenzene 10 8.6 86 70-130
75-34-3 1,1-Dichloroethane 10 9.8 98 70-130
107-06-2 1,2-Dichloroethane 10 8.6 86 70-130
75-35-4 1,1-Dichloroethylene 10 10.6 106 70-130
156-59-2 cis-1,2-Dichloroethylene 10 10.5 105 70-130
156-60-5 trans-1,2-Dichloroethylene 10 10.2 102 70-130
78-87-5 1,2-Dichloropropane 10 8.9 89 70-130
142-28-9 1,3-Dichloropropane 10 8.1 81 70-130
594-20-7 2,2-Dichloropropane 10 11.1 111 70-130
563-58-6 1,1-Dichloropropene 10 9.0 90 70-130
10061-01-5 cis-1,3-Dichloropropene 10 8.6 86 70-130
10061-02-6 trans-1,3-Dichloropropene 10 9.2 92 70-130
108-20-3 Di-Isopropyl Ether 10 12.1 121 70-130
64-17-5 Ethyl Alcohol 500 509 102 70-130
100-41-4 Ethylbenzene 10 9.0 90 70-130
* = Outside of Control Limits.
17 of 23
FC41655.2.1
Blank Spike Summary Page 2 of 3
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3295-BS a A0235726.D 1 11/21/22 SS n/a n/a VA3295
The QC reported here applies to the following samples:Method: SM 6200B
FC416-1
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
591-78-6 2-Hexanone 50 54.8 110 70-130
98-82-8 Isopropylbenzene 10 10.7 107 70-130
99-87-6 p-Isopropyltoluene 10 10.5 105 70-130
74-83-9 Methyl Bromide 10 9.3 93 60-140
74-87-3 Methyl Chloride 10 9.5 95 60-140
75-09-2 Methylene Chloride 10 13.8 138*70-130
108-10-1 4-Methyl-2-pentanone (MIBK)50 55.5 111 70-130
1634-04-4 Methyl Tert Butyl Ether 10 10.3 103 70-130
91-20-3 Naphthalene 10 12.2 122 70-130
103-65-1 n-Propylbenzene 10 8.8 88 70-130
100-42-5 Styrene 10 10.6 106 70-130
630-20-6 1,1,1,2-Tetrachloroethane 10 9.8 98 70-130
79-34-5 1,1,2,2-Tetrachloroethane 10 7.1 71 70-130
127-18-4 Tetrachloroethylene 10 10.6 106 70-130
108-88-3 Toluene 10 9.3 93 70-130
87-61-6 1,2,3-Trichlorobenzene 10 9.9 99 70-130
120-82-1 1,2,4-Trichlorobenzene 10 11.1 111 70-130
71-55-6 1,1,1-Trichloroethane 10 10.3 103 70-130
79-00-5 1,1,2-Trichloroethane 10 8.0 80 70-130
79-01-6 Trichloroethylene 10 9.1 91 70-130
75-69-4 Trichlorofluoromethane 10 8.0 80 60-140
96-18-4 1,2,3-Trichloropropane 10 7.5 75 70-130
95-63-6 1,2,4-Trimethylbenzene 10 9.4 94 70-130
108-67-8 1,3,5-Trimethylbenzene 10 9.0 90 70-130
108-05-4 Vinyl Acetate 50 49.5 99 70-130
75-01-4 Vinyl Chloride 10 7.7 77 60-140
m,p-Xylene 20 18.5 93 70-130
95-47-6 o-Xylene 10 10.3 103 70-130
1330-20-7 Xylene (total)30 28.8 96 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 99%70-130%
17060-07-0 1,2-Dichloroethane-D4 89%70-130%
2037-26-5 Toluene-D8 101%70-130%
* = Outside of Control Limits.
18 of 23
FC41655.2.1
Blank Spike Summary Page 3 of 3
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3295-BS a A0235726.D 1 11/21/22 SS n/a n/a VA3295
The QC reported here applies to the following samples:Method: SM 6200B
FC416-1
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 102%70-130%
(a) No MS/MSD available for this run.
* = Outside of Control Limits.
19 of 23
FC41655.2.1
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
20 of 23
FC4166
Method Blank Summary Page 1 of 1
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP94113-MB CC086486.D 1 11/16/22 AF 11/16/22 OP94113 GCC2232
The QC reported here applies to the following samples:Method: EPA 504.1
FC416-1
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.020 0.010 ug/l
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 89%63-137%
21 of 23
FC41666.1.1
Blank Spike Summary Page 1 of 1
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP94113-BS CC086487.D 1 11/16/22 AF 11/16/22 OP94113 GCC2232
The QC reported here applies to the following samples:Method: EPA 504.1
FC416-1
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
106-93-4 1,2-Dibromoethane 0.25 0.19 76 70-130
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 87%63-137%
* = Outside of Control Limits.
22 of 23
FC41666.2.1
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 1
Job Number:FC416
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
OP94113-MS CC086488.D 1 11/16/22 AF 11/16/22 OP94113 GCC2232
OP94113-MSD CC086489.D 1 11/16/22 AF 11/16/22 OP94113 GCC2232
FC386-1 CC086491.D 1 11/16/22 AF 11/16/22 OP94113 GCC2232
The QC reported here applies to the following samples:Method: EPA 504.1
FC416-1
FC386-1 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
106-93-4 1,2-Dibromoethane 0.019 U 0.24 0.15 63*0.242 0.16 66*6 70-130/25
CAS No.Surrogate Recoveries MS MSD FC386-1 Limits
460-00-4 4-Bromofluorobenzene 71%74%72%63-137%
* = Outside of Control Limits.
23 of 23
FC41666.3.1
Former Star-Brite Laundry Facility (RM No. 0528)

Former Star-Brite Laundry Facility (RM Site No. 0528) Phillips 66 Company
APPENDIX B

LABORATORY ANALYTICAL RESULTS
(NPDES SYSTEM SAMPLING)

11/08/22
Technical Report for
ATC Group Services LLC
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
RM0528
SGS Job Number: FC59
Sampling Date: 10/25/22
Report to:
ATC Group Services LLC.
7606 Whitehall Executive Center Dr. Suite 800
Charlotte, NC 28273
[e-mail]
ATTN: Rick Kleinfelter
Total number of pages in report:
Certifications: FL(E83510), LA(03051), KS(E-10327), NC(573), NJ(FL002), NY(12022), SC(96038001)
DoD ELAP(ANAB L2229), AZ(AZ0806), CA(2937), TX(T104704404), PA(68-03573), VA(460177),
AL, AK, AR, CT, IA, KY, MA, MI. MS, ND, NH, NV, OK, OR, IL, UT, VT, WA, WI, 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 11/08/22
e-Hardcopy 2.0
Automated Report
34
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]
1 of 34
FC59
Table of Contents
-1-
Sections:
Section 1: Sample Summary ...................................................................................................3
Section 2: Summary of Hits ....................................................................................................4
Section 3: Sample Results ........................................................................................................5
3.1: FC59-1: RW 1 ...............................................................................................................6
3.2: FC59-2: RW 3 ...............................................................................................................9
3.3: FC59-3: INF ..................................................................................................................12
3.4: FC59-4: EFF .................................................................................................................15
Section 4: Misc. Forms ............................................................................................................18
4.1: Chain of Custody ...........................................................................................................19
Section 5: MS Volatiles - QC Data Summaries .....................................................................21
5.1: Method Blank Summary ................................................................................................22
5.2: Blank Spike Summary ...................................................................................................23
5.3: Matrix Spike/Matrix Spike Duplicate Summary ...........................................................24
Section 6: Metals Analysis - QC Data Summaries ................................................................25
6.1: Prep QC MP41398: Ca,Pb,Mg ......................................................................................26
Section 7: General Chemistry - QC Data Summaries ..........................................................32
7.1: Method Blank and Spike Results Summary ..................................................................33
7.2: Duplicate Results Summary ..........................................................................................34 12345672 of 34
FC59
SGS North America Inc.
Sample Summary
ATC Group Services LLC
Job No:FC59
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Project No: RM0528
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
Metals ND = Not detected above the MDL
General Chemistry ND = Not detected above the MDL
FC59-1 10/25/22 15:30 BP 10/26/22 AQ Ground Water RW 1
FC59-2 10/25/22 16:00 BP 10/26/22 AQ Ground Water RW 3
FC59-3 10/25/22 16:30 BP 10/26/22 AQ Ground Water INF
FC59-4 10/25/22 16:40 BP 10/26/22 AQ Ground Water EFF
3 of 34
FC591
Summary of Hits Page 1 of 1
Job Number:FC59
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:10/25/22
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FC59-1 RW 1
1,2-Dichloroethane 1.0 0.50 0.13 ug/l SM 6200B
Calcium 14600 1000 50 ug/l SW846 6010D
Magnesium 5270 5000 35 ug/l SW846 6010D
Hardness, Total as CaCO3 a 58.2 23 0.27 mg/l SM19 2340B
pH b 6.43 su SM4500H B-11/SW9040C
FC59-2 RW 3
Methyl Tert Butyl Ether 45.7 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 2.7 0.50 0.13 ug/l SM 6200B
Calcium 15000 1000 50 ug/l SW846 6010D
Lead 11.7 5.0 1.1 ug/l SW846 6010D
Magnesium 4600 J 5000 35 ug/l SW846 6010D
Hardness, Total as CaCO3 a 56.4 23 0.27 mg/l SM19 2340B
Solids, Total Suspended 3.7 J 25 2.5 mg/l SM2540 D-11
pH b 6.39 su SM4500H B-11/SW9040C
FC59-3 INF
Methyl Tert Butyl Ether 30.2 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 1.7 0.50 0.13 ug/l SM 6200B
Calcium 13900 1000 50 ug/l SW846 6010D
Magnesium 4740 J 5000 35 ug/l SW846 6010D
Hardness, Total as CaCO3 a 54.2 23 0.27 mg/l SM19 2340B
pH b 6.35 su SM4500H B-11/SW9040C
FC59-4 EFF
Calcium 14500 1000 50 ug/l SW846 6010D
Magnesium 5270 5000 35 ug/l SW846 6010D
Hardness, Total as CaCO3 a 57.9 23 0.27 mg/l SM19 2340B
pH b 7.69 su SM4500H B-11/SW9040C
(a) Calculated as: (Calcium * 2.497) + (Magnesium * 4.118)
(b) Field analysis required. Received out of hold time and analyzed by request.
4 of 34
FC592
SGS North America Inc.
Sample Results
Report of Analysis
Orlando, FL
Section 3
5 of 34
FC593
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW 1
Lab Sample ID:FC59-1 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235399.D 1 11/04/22 15:10 SS n/a n/a VA3278
Run #2
Purge Volume
Run #1 10.0 ml
Run #2
Purgeable Aromatics, MTBE
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane 1.0 0.50 0.13 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 91%70-130%
17060-07-0 1,2-Dichloroethane-D4 107%70-130%
2037-26-5 Toluene-D8 102%70-130%
460-00-4 4-Bromofluorobenzene 110%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
6 of 34
FC5933.1
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW 1
Lab Sample ID:FC59-1 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Total Metals Analysis
Analyte Result RL MDL Units DF Prep Analyzed By Method Prep Method
Calcium 14600 1000 50 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
Lead ND 5.0 1.1 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
Magnesium 5270 5000 35 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA19010
(2) Prep QC Batch: MP41398
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
7 of 34
FC5933.1
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW 1
Lab Sample ID:FC59-1 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
General Chemistry
Analyte Result RL MDL Units DF Analyzed By Method
Hardness, Total as CaCO3 a 58.2 23 0.27 mg/l 1 10/28/22 17:46 LM SM19 2340B
Solids, Total Suspended ND 25 5.0 mg/l 1 10/31/22 10:40 BW SM2540 D-11
pH b 6.43 su 1 10/27/22 14:55 ST SM4500H B-11/SW9040C
(a) Calculated as: (Calcium * 2.497) + (Magnesium * 4.118)
(b) Field analysis required. Received out of hold time and analyzed by request.
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
8 of 34
FC5933.1
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW 3
Lab Sample ID:FC59-2 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235400.D 1 11/04/22 15:35 SS n/a n/a VA3278
Run #2
Purge Volume
Run #1 10.0 ml
Run #2
Purgeable Aromatics, MTBE
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
1634-04-4 Methyl Tert Butyl Ether 45.7 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane 2.7 0.50 0.13 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 93%70-130%
17060-07-0 1,2-Dichloroethane-D4 109%70-130%
2037-26-5 Toluene-D8 100%70-130%
460-00-4 4-Bromofluorobenzene 112%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
9 of 34
FC5933.2
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW 3
Lab Sample ID:FC59-2 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Total Metals Analysis
Analyte Result RL MDL Units DF Prep Analyzed By Method Prep Method
Calcium 15000 1000 50 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
Lead 11.7 5.0 1.1 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
Magnesium 4600 J 5000 35 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA19010
(2) Prep QC Batch: MP41398
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
10 of 34
FC5933.2
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW 3
Lab Sample ID:FC59-2 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
General Chemistry
Analyte Result RL MDL Units DF Analyzed By Method
Hardness, Total as CaCO3 a 56.4 23 0.27 mg/l 1 10/28/22 17:51 LM SM19 2340B
Solids, Total Suspended 3.7 J 25 2.5 mg/l 1 10/31/22 10:40 BW SM2540 D-11
pH b 6.39 su 1 10/27/22 14:55 ST SM4500H B-11/SW9040C
(a) Calculated as: (Calcium * 2.497) + (Magnesium * 4.118)
(b) Field analysis required. Received out of hold time and analyzed by request.
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
11 of 34
FC5933.2
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:INF
Lab Sample ID:FC59-3 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235401.D 1 11/04/22 16:00 SS n/a n/a VA3278
Run #2
Purge Volume
Run #1 10.0 ml
Run #2
Purgeable Aromatics, MTBE
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
1634-04-4 Methyl Tert Butyl Ether 30.2 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane 1.7 0.50 0.13 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 91%70-130%
17060-07-0 1,2-Dichloroethane-D4 107%70-130%
2037-26-5 Toluene-D8 101%70-130%
460-00-4 4-Bromofluorobenzene 111%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
12 of 34
FC5933.3
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:INF
Lab Sample ID:FC59-3 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Total Metals Analysis
Analyte Result RL MDL Units DF Prep Analyzed By Method Prep Method
Calcium 13900 1000 50 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
Lead ND 5.0 1.1 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
Magnesium 4740 J 5000 35 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA19010
(2) Prep QC Batch: MP41398
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
13 of 34
FC5933.3
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:INF
Lab Sample ID:FC59-3 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
General Chemistry
Analyte Result RL MDL Units DF Analyzed By Method
Hardness, Total as CaCO3 a 54.2 23 0.27 mg/l 1 10/28/22 17:55 LM SM19 2340B
Solids, Total Suspended ND 25 2.5 mg/l 1 10/31/22 10:40 BW SM2540 D-11
pH b 6.35 su 1 10/27/22 14:55 ST SM4500H B-11/SW9040C
(a) Calculated as: (Calcium * 2.497) + (Magnesium * 4.118)
(b) Field analysis required. Received out of hold time and analyzed by request.
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
14 of 34
FC5933.3
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:EFF
Lab Sample ID:FC59-4 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Method:SM 6200B Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
Run #1 A0235402.D 1 11/04/22 16:23 SS n/a n/a VA3278
Run #2
Purge Volume
Run #1 10.0 ml
Run #2
Purgeable Aromatics, MTBE
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane ND 0.50 0.13 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 110%70-130%
2037-26-5 Toluene-D8 102%70-130%
460-00-4 4-Bromofluorobenzene 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
15 of 34
FC5933.4
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:EFF
Lab Sample ID:FC59-4 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Total Metals Analysis
Analyte Result RL MDL Units DF Prep Analyzed By Method Prep Method
Calcium 14500 1000 50 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
Lead ND 5.0 1.1 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
Magnesium 5270 5000 35 ug/l 1 10/27/22 10/28/22 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA19010
(2) Prep QC Batch: MP41398
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
16 of 34
FC5933.4
SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:EFF
Lab Sample ID:FC59-4 Date Sampled:10/25/22
Matrix:AQ - Ground Water Date Received:10/26/22
Percent Solids:n/a
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
General Chemistry
Analyte Result RL MDL Units DF Analyzed By Method
Hardness, Total as CaCO3 a 57.9 23 0.27 mg/l 1 10/28/22 18:00 LM SM19 2340B
Solids, Total Suspended ND 25 2.5 mg/l 1 10/31/22 10:40 BW SM2540 D-11
pH b 7.69 su 1 10/27/22 14:55 ST SM4500H B-11/SW9040C
(a) Calculated as: (Calcium * 2.497) + (Magnesium * 4.118)
(b) Field analysis required. Received out of hold time and analyzed by request.
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
17 of 34
FC5933.4
SGS North America Inc.
Misc. Forms
Custody Documents and Other Forms
Includes the following where applicable:
• Chain of Custody
Orlando, FL
Section 4
18 of 34
FC594
FC59: Chain of Custody
Page 1 of 2
19 of 34
FC5944.1
Job Number:FC59 Client:ATLAS TECHNICAL CONSULTANTS - CH
Date / Time Received:10/26/2022 9:15:00 AM Delivery Method:FEDEX
Project:STARBRITE
Airbill #'s:1009 6379 8868
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: (1.2);
Cooler 1: (1.8);
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:0.6; # of Coolers:1
Y or N N/A
12. Residual Chlorine Present?
Residual Chlorine Test Strip Lot #:
Technician:Reviewer:SAMUELM Date:Date:10/26/2022 9:15:00 A
FC59: Chain of Custody
Page 2 of 2
20 of 34
FC5944.1
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
21 of 34
FC595
Method Blank Summary Page 1 of 1
Job Number:FC59
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3278-MB A0235398.D 1 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC59-1, FC59-2, FC59-3, FC59-4
CAS No.Compound Result RL MDL Units Q
71-43-2 Benzene ND 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane ND 0.50 0.13 ug/l
100-41-4 Ethylbenzene ND 0.50 0.13 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 0.50 0.13 ug/l
108-88-3 Toluene 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 90%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%70-130%
2037-26-5 Toluene-D8 101%70-130%
460-00-4 4-Bromofluorobenzene 113%70-130%
22 of 34
FC5955.1.1
Blank Spike Summary Page 1 of 1
Job Number:FC59
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
VA3278-BS A0235396.D 1 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC59-1, FC59-2, FC59-3, FC59-4
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
71-43-2 Benzene 10 10.7 107 70-130
107-06-2 1,2-Dichloroethane 10 10 100 70-130
100-41-4 Ethylbenzene 10 10.5 105 70-130
1634-04-4 Methyl Tert Butyl Ether 10 8.4 84 70-130
108-88-3 Toluene 10 10.2 102 70-130
1330-20-7 Xylene (total)30 28.6 95 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 86%70-130%
17060-07-0 1,2-Dichloroethane-D4 95%70-130%
2037-26-5 Toluene-D8 98%70-130%
460-00-4 4-Bromofluorobenzene 102%70-130%
* = Outside of Control Limits.
23 of 34
FC5955.2.1
Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 1
Job Number:FC59
Account:ATCNCC ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Sample File ID DF Analyzed By Prep Date Prep Batch Analytical Batch
FA99977-6MS A0235410.D 5 11/04/22 SS n/a n/a VA3278
FA99977-6MSD A0235411.D 5 11/04/22 SS n/a n/a VA3278
FA99977-6 a A0235418.D 5 11/04/22 SS n/a n/a VA3278
The QC reported here applies to the following samples:Method: SM 6200B
FC59-1, FC59-2, FC59-3, FC59-4
FA99977-6 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
71-43-2 Benzene ND 50 52.5 105 50 56.2 112 7 70-130/20
107-06-2 1,2-Dichloroethane 1.2 J 50 52.3 102 50 55.3 108 6 70-130/20
100-41-4 Ethylbenzene 2.4 J 50 54.1 103 50 57.9 111 7 70-130/20
1634-04-4 Methyl Tert Butyl Ether 474 E 50 537 126 50 534 120 1 70-130/20
108-88-3 Toluene ND 50 48.4 97 50 53.3 107 10 70-130/20
1330-20-7 Xylene (total)ND 150 141 94 150 155 103 9 70-130/20
CAS No.Surrogate Recoveries MS MSD FA99977-6 Limits
1868-53-7 Dibromofluoromethane 88%86%90%70-130%
17060-07-0 1,2-Dichloroethane-D4 102%99%104%70-130%
2037-26-5 Toluene-D8 97%98%104%70-130%
460-00-4 4-Bromofluorobenzene 100%104%105%70-130%
(a) Sample re-analyzed beyond hold time.
* = Outside of Control Limits.
24 of 34
FC5955.3.1
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 6
25 of 34
FC596
BLANK RESULTS SUMMARY
Part 2 - Method Blanks
Login Number: FC59
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP41398 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 10/27/22
MB
Metal RL IDL MDL raw final
Aluminum 200 14 14
Antimony 6.0 1 1
Arsenic 10 1.3 1.3
Barium 200 .5 1
Beryllium 4.0 .1 .2
Boron 100 5 10
Cadmium 5.0 .1 .2
Calcium 1000 50 50 2.0 <1000
Chromium 10 .5 1
Cobalt 50 .2 .2
Copper 25 1 1
Iron 300 15 17
Lead 5.0 1 1.1 -0.50 <5.0
Magnesium 5000 35 35 -13 <5000
Manganese 15 .25 1
Molybdenum 50 .3 .3
Nickel 40 .4 .4
Potassium 10000 100 200
Selenium 10 2 2.9
Silver 10 .5 .7
Sodium 10000 250 500
Strontium 10 .25 .5
Thallium 10 1 1.4
Tin 50 .5 1
Titanium 10 .5 1
Vanadium 50 .5 .6
Zinc 20 3 4.4
Associated samples MP41398: FC59-1, FC59-2, FC59-3, FC59-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
_________________________________________________________________________________________________________
Page 1
26 of 34
FC5966.1.1
MATRIX SPIKE AND DUPLICATE RESULTS SUMMARY
Login Number: FC59
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP41398 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 10/27/22 10/27/22
FA99857-2 QC FA99857-2 Spikelot QC
Metal Original DUP RPD Limits Original MS MPFLICP2 % Rec Limits
Aluminum anr
Antimony anr
Arsenic anr
Barium anr
Beryllium anr
Boron
Cadmium anr
Calcium 20800 20700 0.5 0-20 20800 44300 25000 94.0 80-120
Chromium anr
Cobalt anr
Copper anr
Iron anr
Lead 0.0 0.0 NC 0-20 0.0 474 500 94.8 80-120
Magnesium 810 812 0.2 0-20 810 25100 25000 97.2 80-120
Manganese anr
Molybdenum anr
Nickel anr
Potassium anr
Selenium anr
Silver anr
Sodium anr
Strontium anr
Thallium
Tin anr
Titanium anr
Vanadium anr
Zinc anr
Associated samples MP41398: FC59-1, FC59-2, FC59-3, FC59-4
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 1
27 of 34
FC5966.1.2
MATRIX SPIKE AND DUPLICATE RESULTS SUMMARY
Login Number: FC59
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP41398 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 10/27/22
FA99857-2 Spikelot MSD QC
Metal Original MSD MPFLICP2 % Rec RPD Limit
Aluminum anr
Antimony anr
Arsenic anr
Barium anr
Beryllium anr
Boron
Cadmium anr
Calcium 20800 43400 25000 90.4 2.1 20
Chromium anr
Cobalt anr
Copper anr
Iron anr
Lead 0.0 466 500 93.2 1.7 20
Magnesium 810 24300 25000 94.0 3.2 20
Manganese anr
Molybdenum anr
Nickel anr
Potassium anr
Selenium anr
Silver anr
Sodium anr
Strontium anr
Thallium
Tin anr
Titanium anr
Vanadium anr
Zinc anr
Associated samples MP41398: FC59-1, FC59-2, FC59-3, FC59-4
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
28 of 34
FC5966.1.2
SPIKE BLANK AND LAB CONTROL SAMPLE SUMMARY
Login Number: FC59
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP41398 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 10/27/22
BSP Spikelot QC
Metal Result MPFLICP2 % Rec Limits
Aluminum anr
Antimony anr
Arsenic anr
Barium anr
Beryllium anr
Boron
Cadmium anr
Calcium 24300 25000 97.2 80-120
Chromium anr
Cobalt anr
Copper anr
Iron anr
Lead 471 500 94.2 80-120
Magnesium 24300 25000 97.2 80-120
Manganese anr
Molybdenum anr
Nickel anr
Potassium anr
Selenium anr
Silver anr
Sodium anr
Strontium anr
Thallium
Tin anr
Titanium anr
Vanadium anr
Zinc anr
Associated samples MP41398: FC59-1, FC59-2, FC59-3, FC59-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
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FC5966.1.3
SERIAL DILUTION RESULTS SUMMARY
Login Number: FC59
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP41398 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 10/27/22
FA99857-2 QC
Metal Original SDL 1:5 %DIF Limits
Aluminum anr
Antimony anr
Arsenic anr
Barium anr
Beryllium anr
Boron
Cadmium anr
Calcium 20800 20700 0.5 0-10
Chromium anr
Cobalt anr
Copper anr
Iron anr
Lead 0.00 0.00 NC 0-10
Magnesium 810 791 2.3 0-10
Manganese anr
Molybdenum anr
Nickel anr
Potassium anr
Selenium anr
Silver anr
Sodium anr
Strontium anr
Thallium
Tin anr
Titanium anr
Vanadium anr
Zinc anr
Associated samples MP41398: FC59-1, FC59-2, FC59-3, FC59-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
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FC5966.1.4
POST DIGESTATE SPIKE SUMMARY
Login Number: FC59
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP41398 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 10/27/22
Sample Final FA99857-2 PS Spike Spike Spike QC
Metal ml ml Raw Corr.** ug/l ml ug/ml ug/l % Rec Limits
Aluminum
Antimony
Arsenic
Barium
Beryllium
Boron
Cadmium
Calcium 9.8 10 20820 20403.6 25150 0.2 250 5000 94.9 80-120
Chromium
Cobalt
Copper
Iron
Lead 9.8 10 46.3 0.2 2.5 50 92.6 80-120
Magnesium 9.8 10 809.9 793.702 5827 0.2 250 5000 100.7 80-120
Manganese
Molybdenum
Nickel
Potassium
Selenium
Silver
Sodium
Strontium
Thallium
Tin
Titanium
Vanadium
Zinc
Associated samples MP41398: FC59-1, FC59-2, FC59-3, FC59-4
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
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FC5966.1.5
SGS North America Inc.
General Chemistry
QC Data Summaries
Includes the following where applicable:
• Method Blank and Blank Spike Summaries
• Duplicate Summaries
• Matrix Spike Summaries
Orlando, FL
Section 7
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FC597
METHOD BLANK AND SPIKE RESULTS SUMMARY
GENERAL CHEMISTRY
Login Number: FC59
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
MB Spike BSP BSP QC
Analyte Batch ID RL Result Units Amount Result %Recov Limits
Solids, Total Suspended GN92676 2.5 0.0 mg/l
Associated Samples:
Batch GN92676: FC59-1, FC59-2, FC59-3, FC59-4
(*) Outside of QC limits
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FC5977.1
DUPLICATE RESULTS SUMMARY
GENERAL CHEMISTRY
Login Number: FC59
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Original DUP QC
Analyte Batch ID Sample Units Result Result RPD Limits
Solids, Total Suspended GN92676 FC59-1 mg/l 1.6 0.0 13.3(a) 0-5%
pH GN92653 FC59-1 su 6.43 6.39 0.6 0-10%
Associated Samples:
Batch GN92653: FC59-1, FC59-2, FC59-3, FC59-4
Batch GN92676: FC59-1, FC59-2, FC59-3, FC59-4
(*) Outside of QC limits
(a) RPD acceptable due to low duplicate and sample concentrations.
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FC5977.2