MO-4625_15635_CA_MRP_20240220

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

February 20, 2024

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. P660528017

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
June 2023 through December 2023.

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. P660528017

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]

February 20, 2024

Former Star-Brite Laundry Facility (RM No. 0528)
February 20, 2024

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: 2/20/2024
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)
February 20, 2024

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

06

/

01

/

23

to

12

/

31

/

23
Days of Operation this
Period:

212 (approx).

SYSTEM DOWNTIME SUMMARY (current reporting period only)

Month Reason

June – December 2023

Routine scheduled maintenance during bi-weekly O&M visits.
October 2023 Groundwater sampling event.

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)
February 20, 2024

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

Gallons Treated Since Last Report: 523,700 (05/23/23 – 12/19/2023)

Total Gallons Treated To Date: 10,490,531 (12/19/2023)

Parameter/Units:
Influent MTBE (RW/1/RW-3: 38.7 µg/L /47.5 µg/L) sampled 07/18/23; Influent MTBE (RW/1/RW-3: 10.9
µg/L /18.2 µg/L) sampled 10/26/23; Effluent MTBE (<0.50 µg/L) sampled 07/18/23; Effluent MTBE (<0.50
µg/L) sampled 10/26/23.

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)
February 20, 2024
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 ............................................................................................................................ 2
5.0 GROUNDWATER CHARACTERIZATION ........................................................................................... 3
5.1 GROUNDWATER LEVELS...................................................................................................................................... 3
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 ........................................................................................................................ 5
7.1 SITE ACTIVITIES ................................................................................................................................................. 5
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
Figure 3b - Deep Groundwater Elevation Contour Map
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)
February 20, 2024
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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 June 2023 through December 2023.

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 2023 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-9A, 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 2023 sampling event.

Chloroform was detected in the samples from water supply wells WSW-1, WSW-2, and WSW-6 at levels
consistent with prior detections. Methyl tertiary butyl ether (MTBE) was detected in WSW-1 and 1,2-
dichloroethane was detected in WSW-1 and WSW-2, both at concentrations below their respective 2L
Standards.

Methylene chloride and methyl chloride were both detected for the first time in sampling history in all three-
water supply well samples sampled in October 2023. Methylene chloride was also detected in the laboratory
method blank. Both compounds are common laboratory contaminants, and detections are potentially the
result of cross-contamination during laboratory analysis.

Influent samples for RW-1/RW-3 and effluent samples were collected in July and October 2023. WSW-1
was also sampled during the July 2023 sampling. 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 2023 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 2024.

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.

Former Star-Brite Laundry Facility (RM No. 0528)
February 20, 2024
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ATC Project No. P660528014 Phillips 66 Company
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.

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 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.

Former Star-Brite Laundry Facility (RM No. 0528)
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ATC Project No. P660528014 Phillips 66 Company
5.0 GROUNDWATER CHARACTERIZATION

5.1 GROUNDWATER LEVELS

On October 23, 2023, 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 23, 2023, groundwater contour map for the shallow
saprolite aquifer shows that shallow groundwater flow delineated by wells MW-1A, MW-2A, MW-3R, MW-
5A, MW-6R, MW-7, MW-8A and MW-9A has an overall groundwater flow direction to the east-southeast.
The groundwater contour 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-northwest.

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
2023 gauging data are included as Figures 3a and 3b.

5.2 GROUNDWATER QUALITY

On October 23 and 24, 2023, 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 samples were analyzed for
volatile organic compounds (VOCs), including benzene, toluene, ethylbenzene, total xylenes (BTEX),
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 October 2023 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 wells MW-9A (58.7 µg/L), RW-1 (27.0 µg/L), and RW-3 (65.6
µg/L);
 Naphthalene (2L Standard of 6 µg/L) in well MW-1A (22.5 µg/L); and
 1,2-Dichloroethane (1,2-DCA; 2L Standard of 0.4 µg/L) in wells MW-9A (1.2 µg/L), RW-1 (1.1 µg/L),
and RW-3 (3.3 µg/L).

None of the detected constituents exceeded their respective GCLs in the site monitoring or recovery wells.
Groundwater analytical results for the October 2023 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 July 18, 2023, a sample was collected from water supply well WSW-1 located at the Oakdale Nursery
property (5626 Statesville Road).

On October 24, 2023, 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
Former Star-Brite Laundry Facility (RM No. 0528)
February 20, 2024
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ATC Project No. P660528014 Phillips 66 Company
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 reports are included in Appendix A, and laboratory results
are summarized in Table 6.

Chloroform was detected in water supply wells WSW-1, WSW-2, and WSW-6 at concentrations that did not
exceed the 2L Standard and at levels consistent with prior detections. MTBE was detected in WSW-1 and
1,2-dichloroethane was detected in WSW-1 and WSW-2, both at concentrations below their respective 2L
Standards.

Methylene chloride and methyl chloride were both detected for the first time in sampling history in all three-
water supply well samples collected in October 2023. Methylene chloride was also detected in the
laboratory method blank. Both compounds are common laboratory contaminants, and detections are
potentially the result of cross-contamination during laboratory analysis. Overall, ATC concludes that the
laboratory results are usable and any exceptions do not significantly impact the conclusions presented in
this report.

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 June 1, 2023, through December 31, 2023, the remedial system operated for approximately 212 days
out of a possible 214 days. Minimal system shutdown resulted from routine scheduled maintenance
throughout the reporting period and a groundwater sampling event in October 2023. The average dissolved
VOC mass removal during the reporting period was estimated as 0.37 grams/day.

6.2 SYSTEM SAMPLING

Influent samples for RW-1/RW-3 and effluent samples were collected in July and October 2023. 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.
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ATC Project No. P660528014 Phillips 66 Company

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 Figure 6) 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 2024. 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 2024. 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
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 2023 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-9A, 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 2023 sampling event. Chloroform was detected in water supply wells WSW-1, WSW-2, and
WSW-3 at concentrations that did not exceed the 2L Standard and at levels consistent with prior detections.
MTBE was detected in WSW-1 and 1,2-dichloroethane was detected in WSW-1 and WSW-2, both at
concentrations below their respective 2L Standards.

Methylene chloride and methyl chloride were both detected for the first time in sampling history in all three-
water supply well samples sampled in October 2023. Methylene chloride was also detected in the laboratory
method blank. Both compounds are common laboratory contaminants, and detections are potentially the
result of cross-contamination during laboratory analysis.

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 2023 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 2024.

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
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ATC Project No. P660528014 Phillips 66 Company
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 NM NM
05/19/14 NM NM
10/06/14 NM NM
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
04/19/23 21.12 78.61
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
04/19/23 21.31 78.80
MW-2R
99.73
MW-2A 100.11
99.26
99.48
Groundwater
Elevation
(feet)
Monitoring Well Sample Date
Depth To
Groundwater
(feet)
TOC Elevation
(feet)
Well Abandoned
MW-1R
MW-1A
Well Abandoned
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
04/19/23 20.34 79.48
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
04/19/23 20.78 78.64
MW-4D 99.42
MW-3R 99.82
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
04/19/23 21.57 78.21
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
04/19/23 17.74 81.62
99.36MW-6R
99.02
MW-5A 99.78
Well Abandoned
MW-5R
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 ---
04/19/23 20.10 78.95
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
04/19/23 21.95 77.35
MW-8A 99.30
MW-7 99.05
MW-8
Well Abandoned
98.63
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 71.3
04/19/23 20.97 78.36
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
04/19/23 20.50 78.79
MW-9A 99.33
99.29
MW-9R
MW-10D
99.27
Well Abandoned
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
04/19/23 19.51 80.17
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
04/19/23 20.66 79.12
MW-12D 99.78
MW-11DA 99.68
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 NM 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
04/19/23 21.10 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
04/19/23 19.50 NS
04/05/18 28.18 NS
10/16/18 32.85 NS
04/22/19 NM 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
04/19/23 27.47 NS
Notes:
TOC elevations referenced to an arbitrary onsite benchmark of 100.00 feet
NS = Not surveyed
NM = Not Measured
RW-1 NS
TOC = Top of casing
RW-2 NS
RW-3 NS
All data expressed in feet
Depth to groundwater measured from 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
B
e
n
z
e
n
e
T
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l
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B
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B
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2
-
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2
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(
E
D
B
)
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 11,700 100,000 3,000 5,000 4,000,000 26,100 200 28,500 24,100 6,000,000 50
MW-1A 4/20/2023 <0.13 <0.13 0.61 2.6 3.21 <0.13 8.3 0.30 J 0.26 J <0.13 <0.20 0.27 J <0.13 <0.13 <0.13 <0.13 <1.0 0.24 J 0.19 J <0.20 <0.20 <1.0 <1.3 0.60 <0.13 5.7 2.7 4.7 J <0.0095
MW-2A 4/19/2023 <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 <0.048
MW-3R 4/19/2023 <0.13 <0.13 <0.13 <0.25 ND 0.49 J 0.18 J <0.13 <0.13 <0.13 <0.20 0.18 J <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 0.19 J 0.36 J <2.0 <0.047
MW-4D 4/20/2023 <0.13 <0.13 <0.13 <0.25 ND 0.68 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 0.15 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 <0.0096
MW-5A 4/19/2023 <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 4/19/2023 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 0.56 <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-7 4/19/2023 <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 0.37 J <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0093
MW-8A 4/20/2023 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.13 <0.13 <0.13 <0.20 0.50 <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 <0.0093
MW-9A 4/20/2023 0.53 <0.13 <0.13 <0.25 0.53 15.0 <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 1.0 <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-10D 4/19/2023 <0.13 <0.13 <0.13 <0.25 ND 0.17 J <0.13 <0.13 <0.13 <0.13 <0.20 <0.13 <0.13 <0.13 0.15 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 <0.0095
MW-11DA 4/20/2023 <0.13 <0.13 <0.13 <0.25 ND 0.16 J <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 4/20/2023 <0.13 <0.13 <0.13 <0.25 ND 0.15 J <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
RW-1 4/19/2023 <0.13 <0.13 <0.13 <0.25 ND 27.1 0.25 J <0.13 0.20 J <0.13 <0.20 0.23 J <0.13 <0.13 1.0 <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-2 4/20/2023 <0.13 <0.13 <0.13 <0.25 ND 0.29 J <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
RW-3 4/19/2023 0.17 J <0.13 <0.13 <0.25 0.17 75.0 0.98 <0.13 0.27 J <0.13 <0.20 0.34 J <0.13 <0.13 3.9 0.27 J <1.0 0.37 J <0.13 <0.20 <0.20 <1.0 <1.3 <0.13 <0.13 <0.13 <0.13 <2.0 <0.0095
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. NE = Not Established
GCL
2L Standard
Sample Method EPA 6200B
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 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 5.6 830 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 1.6 <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
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
04/20/23 <0.13 <0.13 0.61 2.6 3.21 <0.13 <0.13 <0.0095 8.3 0.30 J 0.26 J <0.13 0.24 J <0.13 0.27 J <1.0 NA 0.19 J 0.60 5.7 2.7
NS - Due to blockage in well
NS - Well Dry
NS - Blockage at 15 feet
Well Abandoned
2L Standard
GCL
MW-1
MW-1R
MW-1A
Page 1 of 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
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
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 8.7 310 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
04/19/23 <0.13 <0.13 <0.13 <0.25 ND <0.13 <0.13 <0.048 <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
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 3.3 17,000 NA ND ND NA NA NA NA NA NA NA NA NA NA NA NA
Well abandoned
MW-2A
MW-2
MW-3
MW-2R
Page 2 of 12
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 B
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n
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T
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T
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B
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IP
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B
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-
B
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1
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C
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1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
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l
o
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o
p
r
o
p
a
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e
p
-
I
s
o
p
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p
y
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n
-
P
r
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p
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b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
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t
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y
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b
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n
z
e
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e
1
,
3
,
5
-
T
r
i
m
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t
h
y
l
b
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n
z
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n
e
1 600 600 500 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 5,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
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
04/19/23 <0.13 <0.13 <0.13 <0.25 ND 0.49 J <0.13 <0.047 0.18 J <0.13 <0.13 <0.13 <0.13 <0.13 0.18 J <1.0 NA <0.13 <0.13 0.19 J 0.36 J
MW-3R
Page 3 of 12
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 B
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B
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1
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2
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C
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1
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2
-
d
i
b
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m
o
-
3
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c
h
l
o
r
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p
r
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p
a
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1
,
2
,
4
-
T
r
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t
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b
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n
z
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1
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3
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5
-
T
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t
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b
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1 600 600 500 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 5,000 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 0.11 <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 3.9 <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
04/20/23 <0.13 <0.13 <0.13 <0.25 ND 0.68 <0.13 <0.0096 <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
MW-4D
Page 4 of 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 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
04/19/23 <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-5R
Well abandoned
MW-5
Well not located
Well abandoned
Page 5 of 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 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
04/19/23 <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 0.56 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-6R
MW-6
Well not located
Not Sampled - Could Not Find Well
Page 6 of 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 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
04/19/23 <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
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 7 of 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 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
04/20/23 <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 0.50 <1.0 NA <0.13 <0.13 <0.13 <0.13
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
MW-8A
Not Sampled - Well Dry
Not Sampled - Well Dry
MW-8
Well abandoned
MW-9
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 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
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
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
04/20/23 0.53 <0.13 <0.13 <0.25 0.53 15.0 <0.13 <0.0094 <0.13 <0.13 <0.13 1.0 <0.13 <0.13 <0.13 <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-9A
Well abandoned
Not Sampled - Well Dry
MW-9R
Page 9 of 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 NE 11,700 26,100 28,500 24,100
2L Standard
GCL
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
04/19/23 <0.13 <0.13 <0.13 <0.25 ND 0.17 J <0.13 <0.0095 <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
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
04/20/23 <0.13 <0.13 <0.13 <0.25 ND 0.16 J <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-10D
MW-11DA
MW-11D
Well abandoned
Page 10 of 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 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
04/20/23 <0.13 <0.13 <0.13 <0.25 ND 0.15 J <0.13 <0.0096 <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 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
04/19/23 <0.13 <0.13 <0.13 <0.25 ND 27.1 <0.13 <0.0095 0.25 J <0.13 0.20 J 1.0 <0.13 <0.13 0.23 J <1.0 NA <0.13 <0.13 <0.13 <0.13
MW-12D
RW-1
Page 11 of 12
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
B
T
E
X
M
T
B
E
IP
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
n
-
B
u
t
y
l
b
e
n
z
e
n
e
s
e
c
-
B
u
t
y
l
b
e
n
z
e
n
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
Is
o
p
r
o
p
y
l
b
e
n
z
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
d
i
b
r
o
m
o
-
3
-
c
h
l
o
r
o
p
r
o
p
a
n
e
p
-
I
s
o
p
r
o
p
y
l
t
o
l
u
e
n
e
n
-
P
r
o
p
y
l
b
e
n
z
e
n
e
1
,
2
,
4
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1
,
3
,
5
-
T
r
i
m
e
t
h
y
l
b
e
n
z
e
n
e
1 600 600 500 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 5,000 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
04/20/23 <0.13 <0.13 <0.13 <0.25 ND 0.29 J <0.13 <0.0096 <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
04/19/23 0.17 J <0.13 <0.13 <0.25 0.17 75.0 0.27 J <0.0095 0.98 <0.13 0.27 J 3.9 0.37 J <0.13 0.34 J <1.0 NA <0.13 <0.13 <0.13 <0.13
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. EDB* = 1,2-Dibromoethane; 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
RW-2
RW-3
NS - Not Sampled - Pump Not Operational
Page 12 of 12
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
City Water
Connection?
Well Status/
Comments
2732 Boulder Lane 1,370 Up gradient No
2733 Boulder Lane 1,380 Up gradient No
2740 Boulder Lane 1,260 Up gradient No
2741 Boulder Lane 1,270 Up gradient No
6101 Burmith Avenue 1,050 Up gradient No
6116 Burmith Avenue 900 Up gradient No
6117 Burmith Avenue 900 Up gradient No
6217 Burmith Avenue 470 Up gradient No
6220 Burmith Avenue 500 Up gradient No
6240 Burmith Avenue
WSW-7 300*Up gradient Yes WSW Pump has
no power
6249 Burmith Avenue
WSW-4 200*Up gradient Yes WSW Pump has
no power
6308 Burmith Avenue
WSW-5 110*Up gradient Yes WSW Pump has
no power
6325 BurmithAvenue
WSW-6 110*Up gradient No
5517 Collins Street 1,430 Down gradient No
5453 Datha Avenue 1,010 Down gradient No
5600 Datha Avenue 640 Down gradient No
5028 Milhaven Lane 1,260 Upgradient No
5312 Milhaven Lane 1,340 Up gradient No
5505 Milhaven Lane 1,330 Up gradient No
5521 Milhaven Lane 1,270 Up gradient No
5721 Milhaven Lane 1,450 Up gradient 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
City Water
Connection?
Well Status/
Comments
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
3310 Orr Street 500 Down gradient No
3415 Orr Street 680 Down gradient No
3421 Orr Street 790 Down gradient No
3426 Orr Street 900 Down gradient No
5407 Statesville Road 1,200 Down gradient No
5432 Statesville Road 1,090 Down gradient No
5440 Statesville Road 1,000 Down gradient No
5441 Statesville Road 560 Down gradient No
5524 Statesville Road 520 Down gradient No
5626 Statesville Road
WSW-1, WSW-2 200*Down gradient No
5700 Statesville Road
WSW-3 230*Cross Gradient Yes WSW Pump has
no power
5724 Statesville Road 360 Up gradient No
5800 Statesville Road 570 Up gradient No
5915 Statesville Road 1,090 Up gradient No
* Shaded Properties Represent Locations Designated for Sampling by NCDEQ
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 B
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B
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D
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o
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1 600 600 500 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
4/20/2023 <0.13 <0.13 <0.13 <0.25 0.57 <0.13 <0.0094 <0.13 <0.13 0.28 J <1.0 <0.13 <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
4/20/2023 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <0.0094 <0.13 <0.13 0.17 J <1.0 0.13 J <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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
M
T
B
E
I
P
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
T
e
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
D
i
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
1 600 600 500 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 - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable Pump Due to Lack of Power
Not Available for Sampling - Inoperable pump
Not Available for Sampling - Inoperable pump
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/missing 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
WSW-3
Wingate
5700 Statesville Road
Not Available for Sampling
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
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
M
T
B
E
I
P
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
T
e
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
D
i
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
1 600 600 500 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 <0.13
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
4/20/2023 <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
Not Available for Sampling - Inoperable Pump Due to Lack of Power
WSW - 6
Wallace
6325 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 (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
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
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
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 B
e
n
z
e
n
e
T
o
l
u
e
n
e
E
t
h
y
l
b
e
n
z
e
n
e

T
o
t
a
l

Xy
l
e
n
e
s
M
T
B
E
I
P
E
E
D
B
*
N
a
p
h
t
h
a
l
e
n
e
B
r
o
m
o
d
i
c
h
l
o
r
o
m
e
t
h
a
n
e
C
h
l
o
r
o
f
o
r
m
M
e
t
h
y
l
e
n
e

C
h
l
o
r
i
d
e
1
,
2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e
T
e
t
r
a
c
h
l
o
r
o
e
t
h
e
n
e
D
i
b
r
o
m
o
c
h
l
o
r
o
m
e
t
h
a
n
e
1 600 600 500 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
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 - 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
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 - Inoperable Pump Due to Lack of Power (property is connected to city water)
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
Be
n
z
e
n
e

(
u
g
/
L
)
To
l
u
e
n
e

(
u
g
/
L
)
Eth
y
l
b
e
n
z
e
n
e

(u
g
/
L
)
To
t
a
l

X
y
l
e
n
e
s

(u
g
/
L
)
MT
B
E

(
u
g
/
L
)
1,2
-
D
i
c
h
l
o
r
o
e
t
h
a
n
e

(u
g
/
L
)
Le
a
d

(
u
g
/
L
)
Na
p
h
t
h
a
l
e
n
e

(
u
g
/
L
)
To
t
a
l

S
u
s
p
e
n
d
e
d

So
l
i
d
s

(
m
g
/
L
)

p
H
10/19/2016 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
07/18/22 <0.13 <0.13 <0.13 <0.25 36.3 2.7 5.4 NA <2.5 6.15
10/25/22 <0.13 <0.13 <0.13 <0.25 30.2 1.7 <1.1 NA <2.5 6.35
01/16/23 <0.13 <0.13 <0.13 <0.25 30.3 1.9 <1.1 NA <2.5 5.58
04/11/23 <0.13 <0.13 <0.13 <0.25 25.1 1.6 <1.1 NA <2.0 6.05
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
07/18/22 <0.13 <0.13 <0.13 <0.25 20.1 1.3 7.9 NA <5.0 5.90
10/25/22 <0.13 <0.13 <0.13 <0.25 <0.13 1 <1.1 NA <5.0 6.43
01/16/23 <0.13 <0.13 <0.13 <0.25 23.5 0.99 <1.1 NA <2.5 5.54
04/11/23 <0.13 <0.13 <0.13 <0.25 15.6 0.65 <1.1 NA <4.0 6.41
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
07/18/22 <0.13 <0.13 <0.13 <0.25 43.3 3.5 4.8 J NA 4.7 J 6.19
10/25/22 <0.13 <0.13 <0.13 <0.25 45.7 2.7 11.7 NA 3.7 J 6.39
01/16/23 <0.13 <0.13 <0.13 <0.25 44.9 3.0 12.5 NA <2.5 5.50
04/11/23 <0.13 <0.13 <0.13 <0.25 37.8 2.7 6.3 NA <2.0 6.16
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
7/18/2023 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <1.1 NA <2.5 7.55
10/25/22 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 <1.1 NA <2.5 7.69
01/16/23 <0.13 <0.13 <0.13 <0.25 0.77 <0.13 <1.1 NA <5.0 6.86
04/11/23 <0.13 <0.13 <0.13 <0.25 0.67 <0.13 <1.1 NA <2.0 7.54
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:
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2
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06/19/2020
SEE LOWER LEFT
FORMER STAR-BRITE LAUNDRY FACILITY (RM 0528)
5639 STATESVILLE ROAD
CHARLOTTE, NORTH CAROLINA
P660528013 DH
SB
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MW-7
MW-12D
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RW-3
MW-4D
MW-10D
RW-1
MW-1A MW-9A
MW-3R
MW-2A
MW-5A MW-11DA
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PELICAN SNOBALL
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LEGEND:
SITE PROPERTY LINE
NOTE: ALL LOCATIONS ARE APPROXIMATE
PARCEL LINE
MONITORING WELL (TYPE II)
Well Identification
MW-1A
ST STORM SEWER
DISCHARGE LINEDD
MONITORING WELL (TYPE III)
Well Identification
MW-4D
SCALE: 1" = 20'
20 0 5 10 15 20
N
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RECOVERY WELLRW-1
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X X FENCE
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79.48
78.80
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78.95
SCALE: 1" = 20'
0 5 10 15 20
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LEGEND:
SITE PROPERTY LINE
NOTE: ALL LOCATIONS ARE APPROXIMATE
PARCEL LINE
ST STORM SEWER
DISCHARGE LINEDD
MONITORING WELL (TYPE III)
Well Identification
MW-4D
RECOVERY WELLRW-1
Well Identification
X X FENCE
CATCH BASINCB
MW-1A
78.61 MONITORING WELL (TYPE II)
Well Identification
Relative Groundwater Elevation (ft)
81.00 GROUNDWATER ELEVATION CONTOUR
(DASHED WHERE INFERRED)
GROUNDWATER FLOW DIRECTION
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0
2
3
.
3.
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=

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d
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9
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2
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D
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D
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ST
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ST
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ST
ST
ST
ST
ST
ST
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STSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTST
MW-7
MW-12D
RW-2
MW-8A
RW-3
*MW-4D
MW-10D
RW-1
MW-1A MW-9A
MW-3R
MW-2A
MW-5A MW-11DA
MW-6R
PELICAN SNOBALL
TR
E
A
T
M
E
N
T
SY
S
T
E
M
EN
C
L
O
S
U
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E
DISCHARGE
CONNECTION
POINT
BURMITH AVENUE
ST
A
T
E
S
V
I
L
L
E

R
O
A
D
LEGEND:
SITE PROPERTY LINE
NOTE: ALL LOCATIONS ARE APPROXIMATE
PARCEL LINE
ST STORM SEWER
DISCHARGE LINEDD
MONITORING WELL (TYPE II)
Well Identification
MW-1A
CB
CB
CB
CB
RECOVERY WELLRW-1
Well Identification
X X FENCE
CATCH BASINCB
80.17
79.12
MW-4D
78.64 MONITORING WELL (TYPE III)
Well Identification
Relative Groundwater Elevation (ft)
79.00 GROUNDWATER ELEVATION CONTOUR
(DASHED WHERE INFERRED)
GROUNDWATER FLOW DIRECTION
SCALE: 1" = 20'
0 5 10 15 20
N
78.79
78.64
79
.
0
0
79
.
5
0
80
.
0
0
Figure:
Dr
a
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n
g

F
i
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:
Pr
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c
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:
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d
.

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:
Drn
.

B
y
:
Ap
p
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d

B
y
:
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D
a
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e
:
Scale:
Date:
H:
\
2
0
2
3
\
1

O
T
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F
F
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A
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05/19/2023
SE
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5
2
8
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AS SHOWN
MS DH
3b
NO
T
E
S
:
1.
Fe
a
t
u
r
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s

s
h
o
w
n

a
r
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n
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a
n

a
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t
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t
a
t
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2.
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4
D

n
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u
s
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d

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c
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3

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,

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X
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XXXX
DDDDDDDD
D
D
D
D
D
D
D
D
D
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
STSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTST
MW-7
MW-12D
RW-2 MW-8A
RW-3
MW-4D
MW-10D
RW-1
MW-1A MW-9A
MW-3R
MW-2A
MW-5A MW-11DA
MW-6R
PELICAN SNOBALL
TR
E
A
T
M
E
N
T
SY
S
T
E
M
EN
C
L
O
S
U
R
E
DISCHARGE
CONNECTION
POINT
BURMITH AVENUE
ST
A
T
E
S
V
I
L
L
E

R
O
A
D
LEGEND:
SITE PROPERTY LINE
NOTE: ALL LOCATIONS ARE APPROXIMATE
PARCEL LINE
ST STORM SEWER
DISCHARGE LINEDD
MONITORING WELL (TYPE III)
Well Identification
MW-4D
CB
CB
CB
CB
RECOVERY WELLRW-1
Well Identification
X X FENCE
CATCH BASINCB
MW-1A
<0.13 MONITORING WELL (TYPE II)
Well Identification
MTBE Concentration (µg/L).
20 MTBE ISOCONCENTRATION CONTOUR
(DASHED WHERE INFERRED)(µg/L)
SCALE: 1" = 20'
0 5 10 15 20
N
0.63
<0.13
<0.13
<0.13
<0.13 <0.13
<0.13<0.13
<0.13
38.8
<0.13<0.13
<0.13
NS
29.1
20
Figure:
Dr
a
w
i
n
g

F
i
l
e
:
Pr
o
j
e
c
t

N
u
m
b
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r
:
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d
.

B
y
:
Drn
.

B
y
:
Ap
p
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d

B
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:
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D
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e
:
Scale:
Date:
H:
\
2
0
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3
\
1

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01/05/2023
SE
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A
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6
0
5
2
8
0
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6
AS SHOWN
BM BB
4
NO
T
E
S
:
1.
Fe
a
t
u
r
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s

s
h
o
w
n

a
r
e

n
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t

a
n

a
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t
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a
t
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v
e

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c
a
t
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n
,

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o
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c
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2.
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w
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,

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0
2
2
.
3.
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u
n
d
w
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a
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m
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c
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o
g
r
a
m
s

p
e
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l
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t
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r

(
µ
g
/
L
)
.
4.
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=

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o
t

S
a
m
p
l
e
d
.
CO
O
R
D
I
N
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T
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S
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:
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1
9
8
3

N
O
R
T
H

C
A
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I
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T
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P
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3
2
0
0
,

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S

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U
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V
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F
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X
X
X
X
X
X
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X X X X
X
X
X
X
X
X
X
XXXX
DDDDDDDD
D
D
D
D
D
D
D
D
D
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
ST
STSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTSTST
MW-7
MW-12D
RW-2 MW-8A
RW-3
MW-4D
MW-10D
RW-1
MW-1A MW-9A
MW-3R
MW-2A
MW-5A MW-11DA
MW-6R
PELICAN SNOBALL
TR
E
A
T
M
E
N
T
SY
S
T
E
M
EN
C
L
O
S
U
R
E
DISCHARGE
CONNECTION
POINT
BURMITH AVENUE
ST
A
T
E
S
V
I
L
L
E

R
O
A
D
LEGEND:
SITE PROPERTY LINE
NOTE: ALL LOCATIONS ARE APPROXIMATE
PARCEL LINE
ST STORM SEWER
DISCHARGE LINEDD
MONITORING WELL (TYPE III)
Well Identification
MW-4D
CB
CB
CB
CB
RECOVERY WELLRW-1
Well Identification
X X FENCE
CATCH BASINCB
MW-1A
<0.13 MONITORING WELL (TYPE II)
Well Identification
1,2-DCE Concentration (µg/L).
0.4 1,2-DCE ISOCONCENTRATION CONTOUR
(DASHED WHERE INFERRED)(µg/L)
SCALE: 1" = 20'
0 5 10 15 20
N
0.43J
<0.13
<0.13
<0.13
<0.13 <0.13
0.34J<0.13
0.20J
2.2
<0.13<0.13
<0.13
NS
1.2
0.4
Figure:
Dr
a
w
i
n
g

F
i
l
e
:
Pr
o
j
e
c
t

N
u
m
b
e
r
:
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d
.

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y
:
Drn
.

B
y
:
Ap
p
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d

B
y
:
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.

D
a
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e
:
Scale:
Date:
H:
\
2
0
2
3
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1

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01/05/2023
SE
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P6
6
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2
8
0
1
6
AS SHOWN
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5
NO
T
E
S
:
1.
Fe
a
t
u
r
e
s

s
h
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w
n

a
r
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a
n

a
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t
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a
t
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,

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t
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c
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2.
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s

w
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m
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a
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2
.
3.
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m
s

p
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(
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g
/
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4.
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=

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a
m
p
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d
.
5.
J
=

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s
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v
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2
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B
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Y
CA
D

F
I
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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
Mi
c
o
g
r
a
m
s

p
e
r

l
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t
e
r

(
µ
g/
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)

11/02/23
Technical Report for
ATC Group Services LLC
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
RM0528
SGS Job Number: FC10706
Sampling Dates: 10/23/23 - 10/24/23
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] 
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 unless noted
in the narrative, comments or footnotes.
Client Service contact: Muna Mohammed 407-425-6700
Norm Farmer
Technical Director
Orlando, FL 11/02/23
e-Hardcopy 2.0
Automated Report
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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.
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Table of Contents
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Sections:
Section 1: Sample Summary ...................................................................................................3
Section 2: Summary of Hits ....................................................................................................5
Section 3: Sample Results ........................................................................................................8
3.1: FC10706-1: MW 1A .....................................................................................................9
3.2: FC10706-2: MW 2A .....................................................................................................13
3.3: FC10706-3: MW 3R .....................................................................................................17
3.4: FC10706-4: MW 4D .....................................................................................................21
3.5: FC10706-5: MW 5A .....................................................................................................25
3.6: FC10706-6: MW 6R .....................................................................................................29
3.7: FC10706-7: MW 8A .....................................................................................................33
3.8: FC10706-8: MW 9A .....................................................................................................37
3.9: FC10706-9: MW 10D ...................................................................................................41
3.10: FC10706-10: MW 11DA ............................................................................................45
3.11: FC10706-11: MW 12D ...............................................................................................49
3.12: FC10706-12: RW 1 .....................................................................................................53
3.13: FC10706-13: RW 2 .....................................................................................................57
3.14: FC10706-14: RW 3 .....................................................................................................61
3.15: FC10706-15: WSW 1 .................................................................................................65
3.16: FC10706-16: WSW 2 .................................................................................................69
3.17: FC10706-17: WSW 6 .................................................................................................73
Section 4: Misc. Forms ............................................................................................................77
4.1: Chain of Custody ...........................................................................................................78
Section 5: MS Volatiles - QC Data Summaries .....................................................................81
5.1: Method Blank Summary ................................................................................................82
5.2: Blank Spike Summary ...................................................................................................86
5.3: Matrix Spike/Matrix Spike Duplicate Summary ...........................................................90
Section 6: GC Volatiles - QC Data Summaries .....................................................................94
6.1: Method Blank Summary ................................................................................................95
6.2: Blank Spike Summary ...................................................................................................98
6.3: Blank Spike/Blank Spike Duplicate Summary ..............................................................99
6.4: Matrix Spike/Matrix Spike Duplicate Summary ...........................................................100
6.5: Duplicate Summary .......................................................................................................101
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Sample Summary
ATC Group Services LLC
Job No:FC10706
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
FC10706-1 10/24/23 13:15 NRBP 10/25/23 AQ Ground Water MW 1A
FC10706-2 10/23/23 12:45 NRBP 10/25/23 AQ Ground Water MW 2A
FC10706-3 10/23/23 11:45 NRBP 10/25/23 AQ Ground Water MW 3R
FC10706-4 10/24/23 11:45 NRBP 10/25/23 AQ Ground Water MW 4D
FC10706-5 10/23/23 13:15 NRBP 10/25/23 AQ Ground Water MW 5A
FC10706-6 10/23/23 11:00 NRBP 10/25/23 AQ Ground Water MW 6R
FC10706-7 10/24/23 09:15 NRBP 10/25/23 AQ Ground Water MW 8A
FC10706-8 10/24/23 09:45 NRBP 10/25/23 AQ Ground Water MW 9A
FC10706-9 10/24/23 12:45 NRBP 10/25/23 AQ Ground Water MW 10D
FC10706-10 10/24/23 10:45 NRBP 10/25/23 AQ Ground Water MW 11DA
FC10706-11 10/24/23 07:40 NRBP 10/25/23 AQ Ground Water MW 12D
FC10706-12 10/23/23 13:45 NRBP 10/25/23 AQ Ground Water RW 1
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Sample Summary
(continued)
ATC Group Services LLC
Job No:FC10706
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Project No: RM0528
Sample Collected Matrix Client
Number Date Time By Received Code Type Sample ID
FC10706-13 10/24/23 08:40 NRBP 10/25/23 AQ Ground Water RW 2
FC10706-14 10/23/23 14:15 NRBP 10/25/23 AQ Ground Water RW 3
FC10706-15 10/24/23 14:15 NRBP 10/25/23 AQ Ground Water WSW 1
FC10706-16 10/24/23 14:45 NRBP 10/25/23 AQ Ground Water WSW 2
FC10706-17 10/24/23 13:45 NRBP 10/25/23 AQ Ground Water WSW 6
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Summary of Hits Page 1 of 3
Job Number:FC10706
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:10/23/23 thru 10/24/23
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FC10706-1 MW 1A
Benzene 0.18 J 0.50 0.13 ug/l SM 6200B
n-Butylbenzene 1.1 0.50 0.13 ug/l SM 6200B
sec-Butylbenzene 0.76 0.50 0.13 ug/l SM 6200B
Chloroform 0.28 J 0.50 0.13 ug/l SM 6200B
Ethylbenzene 1.9 0.50 0.13 ug/l SM 6200B
Isopropylbenzene 1.4 0.50 0.13 ug/l SM 6200B
p-Isopropyltoluene 0.56 0.50 0.13 ug/l SM 6200B
Methylene Chloride a 1.2 JB 2.0 1.0 ug/l SM 6200B
Naphthalene 22.5 0.50 0.13 ug/l SM 6200B
n-Propylbenzene 3.2 0.50 0.13 ug/l SM 6200B
1,2,4-Trimethylbenzene 34.7 0.50 0.13 ug/l SM 6200B
1,3,5-Trimethylbenzene 14.4 0.50 0.13 ug/l SM 6200B
m,p-Xylene 2.9 1.0 0.13 ug/l SM 6200B
o-Xylene 1.1 0.50 0.13 ug/l SM 6200B
Xylene (total)4.0 1.5 0.25 ug/l SM 6200B
FC10706-2 MW 2A
No hits reported in this sample.
FC10706-3 MW 3R
Chloroform 0.26 J 0.50 0.13 ug/l SM 6200B
Methyl Bromide 0.47 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.4 JB 2.0 1.0 ug/l SM 6200B
Naphthalene 0.26 J 0.50 0.13 ug/l SM 6200B
1,2,4-Trimethylbenzene 0.22 J 0.50 0.13 ug/l SM 6200B
1,3,5-Trimethylbenzene 0.70 0.50 0.13 ug/l SM 6200B
FC10706-4 MW 4D
1,2-Dichloroethane 0.33 J 0.50 0.13 ug/l SM 6200B
Methyl Bromide 0.45 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.3 JB 2.0 1.0 ug/l SM 6200B
Methyl Tert Butyl Ether 0.28 J 0.50 0.13 ug/l SM 6200B
1,2-Dibromoethane b 0.031 0.019 0.0094 ug/l EPA 504.1
FC10706-5 MW 5A
Methyl Bromide 0.39 J 0.50 0.20 ug/l SM 6200B
Methyl Chloride 0.26 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.3 JB 2.0 1.0 ug/l SM 6200B
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Summary of Hits Page 2 of 3
Job Number:FC10706
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:10/23/23 thru 10/24/23
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FC10706-6 MW 6R
Methyl Chloride 0.27 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.4 JB 2.0 1.0 ug/l SM 6200B
FC10706-7 MW 8A
Chloroform 0.49 J 0.50 0.13 ug/l SM 6200B
Methyl Chloride 0.21 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.4 JB 2.0 1.0 ug/l SM 6200B
FC10706-8 MW 9A
Benzene 0.17 J 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 1.2 0.50 0.13 ug/l SM 6200B
Di-Isopropyl Ether 0.16 J 0.50 0.13 ug/l SM 6200B
Methyl Chloride 0.20 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.5 JB 2.0 1.0 ug/l SM 6200B
Methyl Tert Butyl Ether 58.7 0.50 0.13 ug/l SM 6200B
FC10706-9 MW 10D
Methylene Chloride a 1.4 JB 2.0 1.0 ug/l SM 6200B
Methyl Tert Butyl Ether 0.18 J 0.50 0.13 ug/l SM 6200B
FC10706-10 MW 11DA
Methyl Bromide 0.33 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.4 JB 2.0 1.0 ug/l SM 6200B
Methyl Tert Butyl Ether 0.16 J 0.50 0.13 ug/l SM 6200B
FC10706-11 MW 12D
Methylene Chloride a 1.4 JB 2.0 1.0 ug/l SM 6200B
FC10706-12 RW 1
sec-Butylbenzene 0.24 J 0.50 0.13 ug/l SM 6200B
Chloroform 0.23 J 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 1.1 0.50 0.13 ug/l SM 6200B
Di-Isopropyl Ether 0.16 J 0.50 0.13 ug/l SM 6200B
Methylene Chloride a 1.3 JB 2.0 1.0 ug/l SM 6200B
Methyl Tert Butyl Ether 27.0 0.50 0.13 ug/l SM 6200B
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Summary of Hits Page 3 of 3
Job Number:FC10706
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:10/23/23 thru 10/24/23
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FC10706-13 RW 2
Chloroform 0.15 J 0.50 0.13 ug/l SM 6200B
Methylene Chloride a 1.4 JB 2.0 1.0 ug/l SM 6200B
Methyl Tert Butyl Ether 0.13 J 0.50 0.13 ug/l SM 6200B
FC10706-14 RW 3
Benzene 0.18 J 0.50 0.13 ug/l SM 6200B
sec-Butylbenzene 0.40 J 0.50 0.13 ug/l SM 6200B
Chloroform 0.18 J 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 3.3 0.50 0.13 ug/l SM 6200B
Di-Isopropyl Ether 0.31 J 0.50 0.13 ug/l SM 6200B
Isopropylbenzene 0.41 J 0.50 0.13 ug/l SM 6200B
Methylene Chloride a 1.3 JB 2.0 1.0 ug/l SM 6200B
Methyl Tert Butyl Ether 65.6 0.50 0.13 ug/l SM 6200B
FC10706-15 WSW 1
Chloroform 0.24 J 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 0.18 J 0.50 0.13 ug/l SM 6200B
Methyl Chloride 0.25 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.3 JB 2.0 1.0 ug/l SM 6200B
Methyl Tert Butyl Ether 0.16 J 0.50 0.13 ug/l SM 6200B
FC10706-16 WSW 2
Chloroform 0.13 J 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 0.14 J 0.50 0.13 ug/l SM 6200B
Methyl Chloride 0.38 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.3 JB 2.0 1.0 ug/l SM 6200B
FC10706-17 WSW 6
Chloroform 1.5 0.50 0.13 ug/l SM 6200B
Methyl Chloride 0.25 J 0.50 0.20 ug/l SM 6200B
Methylene Chloride a 1.3 JB 2.0 1.0 ug/l SM 6200B
(a) Associated BS recovery outside control limits high. Suspected laboratory contaminant.
(b) All hits confirmed by dual column analysis.
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Sample Results
Report of Analysis
Orlando, FL
Section 3
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Report of Analysis Page 1 of 3
Client Sample ID:MW 1A
Lab Sample ID:FC10706-1 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3817.D 1 10/31/23 00:06 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 0.18 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 1.1 0.50 0.13 ug/l
135-98-8 sec-Butylbenzene 0.76 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
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
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Client Sample ID:MW 1A
Lab Sample ID:FC10706-1 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 1.9 0.50 0.13 ug/l
591-78-6 2-Hexanone ND 5.0 1.0 ug/l
98-82-8 Isopropylbenzene 1.4 0.50 0.13 ug/l
99-87-6 p-Isopropyltoluene 0.56 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 a 1.2 2.0 1.0 ug/l JB
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 22.5 0.50 0.13 ug/l
103-65-1 n-Propylbenzene 3.2 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 34.7 0.50 0.13 ug/l
108-67-8 1,3,5-Trimethylbenzene 14.4 0.50 0.13 ug/l
108-05-4 Vinyl Acetate ND 5.0 1.0 ug/l
75-01-4 Vinyl Chloride b ND 0.50 0.13 ug/l
m,p-Xylene 2.9 1.0 0.13 ug/l
95-47-6 o-Xylene 1.1 0.50 0.13 ug/l
1330-20-7 Xylene (total)4.0 1.5 0.25 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 104%70-130%
2037-26-5 Toluene-D8 97%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
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Client Sample ID:MW 1A
Lab Sample ID:FC10706-1 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
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Client Sample ID:MW 1A
Lab Sample ID:FC10706-1 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093801.D 1 10/31/23 01:32 AF 10/30/23 12:05 OP99798 GCC2466
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 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
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Client Sample ID:MW 2A
Lab Sample ID:FC10706-2 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3818.D 1 10/31/23 00:30 TD n/a n/a V3A187
Run #2 3A3882.D 1 11/01/23 03:33 TD n/a n/a V3A189
Purge Volume
Run #1 5.0 ml
Run #2 5.0 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
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Report of Analysis Page 2 of 3
Client Sample ID:MW 2A
Lab Sample ID:FC10706-2 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 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 a 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 a 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 a 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 b 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 96%93%70-130%
17060-07-0 1,2-Dichloroethane-D4 103%106%70-130%
2037-26-5 Toluene-D8 99%103%70-130%
460-00-4 4-Bromofluorobenzene 104%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
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Client Sample ID:MW 2A
Lab Sample ID:FC10706-2 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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) Result is from Run# 2
(b) Associated CCV outside of control limits high, sample was 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
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Client Sample ID:MW 2A
Lab Sample ID:FC10706-2 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093802.D 1 10/31/23 01:51 AF 10/30/23 12:05 OP99798 GCC2466
Run #2
Initial Volume Final Volume
Run #1 37.5 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0093 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 96%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
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Client Sample ID:MW 3R
Lab Sample ID:FC10706-3 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3819.D 1 10/31/23 00:54 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 0.26 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
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Client Sample ID:MW 3R
Lab Sample ID:FC10706-3 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 0.47 0.50 0.20 ug/l J
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride a 1.4 2.0 1.0 ug/l JB
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 0.26 0.50 0.13 ug/l J
103-65-1 n-Propylbenzene ND 0.50 0.13 ug/l
100-42-5 Styrene ND 0.50 0.13 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 0.50 0.13 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 0.50 0.13 ug/l
127-18-4 Tetrachloroethylene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 0.50 0.13 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 0.50 0.13 ug/l
71-55-6 1,1,1-Trichloroethane ND 0.50 0.13 ug/l
79-00-5 1,1,2-Trichloroethane ND 0.50 0.13 ug/l
79-01-6 Trichloroethylene ND 0.50 0.13 ug/l
75-69-4 Trichlorofluoromethane ND 0.50 0.20 ug/l
96-18-4 1,2,3-Trichloropropane ND 0.50 0.13 ug/l
95-63-6 1,2,4-Trimethylbenzene 0.22 0.50 0.13 ug/l J
108-67-8 1,3,5-Trimethylbenzene 0.70 0.50 0.13 ug/l
108-05-4 Vinyl Acetate ND 5.0 1.0 ug/l
75-01-4 Vinyl Chloride b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%70-130%
2037-26-5 Toluene-D8 115%70-130%
460-00-4 4-Bromofluorobenzene 99%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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Client Sample ID:MW 3R
Lab Sample ID:FC10706-3 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
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Report of Analysis Page 1 of 1
Client Sample ID:MW 3R
Lab Sample ID:FC10706-3 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093847.D 4 10/31/23 23:08 AF 10/30/23 12:05 OP99798 GCC2467
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 0.076 0.038 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 267% b 63-137%
(a) Dilution required due to matrix interference.
(b) Outside control limits, 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
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Client Sample ID:MW 4D
Lab Sample ID:FC10706-4 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3820.D 1 10/31/23 01:17 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 0.33 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
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Client Sample ID:MW 4D
Lab Sample ID:FC10706-4 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 0.45 0.50 0.20 ug/l J
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride a 1.3 2.0 1.0 ug/l JB
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 0.28 0.50 0.13 ug/l J
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 b 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 105%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
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Client Sample ID:MW 4D
Lab Sample ID:FC10706-4 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
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Report of Analysis Page 1 of 1
Client Sample ID:MW 4D
Lab Sample ID:FC10706-4 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093804.D 1 10/31/23 02:28 AF 10/30/23 12:05 OP99798 GCC2466
Run #2
Initial Volume Final Volume
Run #1 37.2 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane 0.031 0.019 0.0094 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 93%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
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Client Sample ID:MW 5A
Lab Sample ID:FC10706-5 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3821.D 1 10/31/23 01:41 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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
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Report of Analysis Page 2 of 3
Client Sample ID:MW 5A
Lab Sample ID:FC10706-5 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 0.39 0.50 0.20 ug/l J
74-87-3 Methyl Chloride 0.26 0.50 0.20 ug/l J
75-09-2 Methylene Chloride a 1.3 2.0 1.0 ug/l JB
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 b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 107%70-130%
2037-26-5 Toluene-D8 97%70-130%
460-00-4 4-Bromofluorobenzene 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
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Client Sample ID:MW 5A
Lab Sample ID:FC10706-5 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
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Report of Analysis Page 1 of 1
Client Sample ID:MW 5A
Lab Sample ID:FC10706-5 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093806.D 1 10/31/23 03:06 AF 10/30/23 12:05 OP99798 GCC2466
Run #2
Initial Volume Final Volume
Run #1 37.7 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0093 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 96%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
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Client Sample ID:MW 6R
Lab Sample ID:FC10706-6 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3822.D 1 10/31/23 02:04 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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
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Client Sample ID:MW 6R
Lab Sample ID:FC10706-6 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride 0.27 0.50 0.20 ug/l J
75-09-2 Methylene Chloride a 1.4 2.0 1.0 ug/l JB
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 b 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 107%70-130%
2037-26-5 Toluene-D8 96%70-130%
460-00-4 4-Bromofluorobenzene 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
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Report of Analysis Page 3 of 3
Client Sample ID:MW 6R
Lab Sample ID:FC10706-6 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
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Report of Analysis Page 1 of 1
Client Sample ID:MW 6R
Lab Sample ID:FC10706-6 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093807.D 1 10/31/23 03:24 AF 10/30/23 12:05 OP99798 GCC2466
Run #2
Initial Volume Final Volume
Run #1 37.2 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0094 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 110%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
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Client Sample ID:MW 8A
Lab Sample ID:FC10706-7 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3823.D 1 10/31/23 02:28 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 0.49 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
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Report of Analysis Page 2 of 3
Client Sample ID:MW 8A
Lab Sample ID:FC10706-7 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride 0.21 0.50 0.20 ug/l J
75-09-2 Methylene Chloride a 1.4 2.0 1.0 ug/l JB
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 b 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 107%70-130%
2037-26-5 Toluene-D8 96%70-130%
460-00-4 4-Bromofluorobenzene 99%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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Client Sample ID:MW 8A
Lab Sample ID:FC10706-7 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
35 of 101
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Report of Analysis Page 1 of 1
Client Sample ID:MW 8A
Lab Sample ID:FC10706-7 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093808.D 1 10/31/23 03:43 AF 10/30/23 12:05 OP99798 GCC2466
Run #2
Initial Volume Final Volume
Run #1 37.7 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0093 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 93%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
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Report of Analysis Page 1 of 3
Client Sample ID:MW 9A
Lab Sample ID:FC10706-8 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3824.D 1 10/31/23 02:51 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 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
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Report of Analysis Page 2 of 3
Client Sample ID:MW 9A
Lab Sample ID:FC10706-8 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 0.16 0.50 0.13 ug/l J
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride 0.20 0.50 0.20 ug/l J
75-09-2 Methylene Chloride a 1.5 2.0 1.0 ug/l JB
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 58.7 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 b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%70-130%
2037-26-5 Toluene-D8 97%70-130%
460-00-4 4-Bromofluorobenzene 95%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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Client Sample ID:MW 9A
Lab Sample ID:FC10706-8 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
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Report of Analysis Page 1 of 1
Client Sample ID:MW 9A
Lab Sample ID:FC10706-8 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093833.D 1 10/31/23 18:47 AF 10/31/23 09:40 OP99821 GCC2467
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 96%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
40 of 101
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Report of Analysis Page 1 of 3
Client Sample ID:MW 10D
Lab Sample ID:FC10706-9 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3825.D 1 10/31/23 03:15 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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
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Report of Analysis Page 2 of 3
Client Sample ID:MW 10D
Lab Sample ID:FC10706-9 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride a 1.4 2.0 1.0 ug/l JB
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 0.18 0.50 0.13 ug/l J
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 b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%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
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Report of Analysis Page 3 of 3
Client Sample ID:MW 10D
Lab Sample ID:FC10706-9 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
43 of 101
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SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW 10D
Lab Sample ID:FC10706-9 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093834.D 1 10/31/23 19:05 AF 10/31/23 09:40 OP99821 GCC2467
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 92%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 101
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Report of Analysis Page 1 of 3
Client Sample ID:MW 11DA
Lab Sample ID:FC10706-10 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3826.D 1 10/31/23 03:38 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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
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Report of Analysis Page 2 of 3
Client Sample ID:MW 11DA
Lab Sample ID:FC10706-10 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 0.33 0.50 0.20 ug/l J
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride a 1.4 2.0 1.0 ug/l JB
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 0.16 0.50 0.13 ug/l J
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 b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 103%70-130%
2037-26-5 Toluene-D8 97%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
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Report of Analysis Page 3 of 3
Client Sample ID:MW 11DA
Lab Sample ID:FC10706-10 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
47 of 101
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SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:MW 11DA
Lab Sample ID:FC10706-10 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093835.D 1 10/31/23 19:24 AF 10/31/23 09:40 OP99821 GCC2467
Run #2
Initial Volume Final Volume
Run #1 36.9 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0095 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 83%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 101
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SGS North America Inc.
Report of Analysis Page 1 of 3
Client Sample ID:MW 12D
Lab Sample ID:FC10706-11 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3827.D 1 10/31/23 04:02 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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
49 of 101
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SGS North America Inc.
Report of Analysis Page 2 of 3
Client Sample ID:MW 12D
Lab Sample ID:FC10706-11 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride a 1.4 2.0 1.0 ug/l JB
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 b 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 103%70-130%
2037-26-5 Toluene-D8 98%70-130%
460-00-4 4-Bromofluorobenzene 113%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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Client Sample ID:MW 12D
Lab Sample ID:FC10706-11 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
51 of 101
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Report of Analysis Page 1 of 1
Client Sample ID:MW 12D
Lab Sample ID:FC10706-11 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093836.D 1 10/31/23 19:43 AF 10/31/23 09:40 OP99821 GCC2467
Run #2
Initial Volume Final Volume
Run #1 36.9 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0095 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 126%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 101
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Report of Analysis Page 1 of 3
Client Sample ID:RW 1
Lab Sample ID:FC10706-12 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3828.D 1 10/31/23 04:25 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 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 ND 0.50 0.20 ug/l
67-66-3 Chloroform 0.23 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 1.1 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
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Report of Analysis Page 2 of 3
Client Sample ID:RW 1
Lab Sample ID:FC10706-12 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 0.16 0.50 0.13 ug/l J
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride a 1.3 2.0 1.0 ug/l JB
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 27.0 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 b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%70-130%
2037-26-5 Toluene-D8 105%70-130%
460-00-4 4-Bromofluorobenzene 103%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 101
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Report of Analysis Page 3 of 3
Client Sample ID:RW 1
Lab Sample ID:FC10706-12 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
55 of 101
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Report of Analysis Page 1 of 1
Client Sample ID:RW 1
Lab Sample ID:FC10706-12 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093809.D 1 10/31/23 04:02 AF 10/30/23 12:05 OP99798 GCC2466
Run #2
Initial Volume Final Volume
Run #1 37.4 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 108%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 101
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Report of Analysis Page 1 of 3
Client Sample ID:RW 2
Lab Sample ID:FC10706-13 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3829.D 1 10/31/23 04:49 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 0.15 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
57 of 101
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Report of Analysis Page 2 of 3
Client Sample ID:RW 2
Lab Sample ID:FC10706-13 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride ND 0.50 0.20 ug/l
75-09-2 Methylene Chloride a 1.4 2.0 1.0 ug/l JB
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 0.13 0.50 0.13 ug/l J
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 b 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 107%70-130%
2037-26-5 Toluene-D8 103%70-130%
460-00-4 4-Bromofluorobenzene 96%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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Report of Analysis Page 3 of 3
Client Sample ID:RW 2
Lab Sample ID:FC10706-13 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
59 of 101
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SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:RW 2
Lab Sample ID:FC10706-13 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093837.D 1 10/31/23 20:02 AF 10/31/23 09:40 OP99821 GCC2467
Run #2
Initial Volume Final Volume
Run #1 35.8 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.020 0.0098 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 101
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Report of Analysis Page 1 of 3
Client Sample ID:RW 3
Lab Sample ID:FC10706-14 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3830.D 1 10/31/23 05:13 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 0.18 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 0.40 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 ND 0.50 0.20 ug/l
67-66-3 Chloroform 0.18 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 3.3 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
61 of 101
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Report of Analysis Page 2 of 3
Client Sample ID:RW 3
Lab Sample ID:FC10706-14 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 0.31 0.50 0.13 ug/l J
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 0.41 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 a 1.3 2.0 1.0 ug/l JB
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 65.6 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 b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 107%70-130%
2037-26-5 Toluene-D8 107%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
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Client Sample ID:RW 3
Lab Sample ID:FC10706-14 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
63 of 101
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Report of Analysis Page 1 of 1
Client Sample ID:RW 3
Lab Sample ID:FC10706-14 Date Sampled:10/23/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093810.D 1 10/31/23 04:20 AF 10/30/23 12:05 OP99798 GCC2466
Run #2
Initial Volume Final Volume
Run #1 37.6 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0093 ug/l
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
460-00-4 4-Bromofluorobenzene 74%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 101
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Report of Analysis Page 1 of 3
Client Sample ID:WSW 1
Lab Sample ID:FC10706-15 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3831.D 1 10/31/23 05:36 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 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 0.18 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
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Report of Analysis Page 2 of 3
Client Sample ID:WSW 1
Lab Sample ID:FC10706-15 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride 0.25 0.50 0.20 ug/l J
75-09-2 Methylene Chloride a 1.3 2.0 1.0 ug/l JB
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether 0.16 0.50 0.13 ug/l J
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 b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%70-130%
2037-26-5 Toluene-D8 97%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
66 of 101
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Report of Analysis Page 3 of 3
Client Sample ID:WSW 1
Lab Sample ID:FC10706-15 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
67 of 101
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SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:WSW 1
Lab Sample ID:FC10706-15 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093838.D 1 10/31/23 20:20 AF 10/31/23 09:40 OP99821 GCC2467
Run #2
Initial Volume Final Volume
Run #1 36.6 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 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
68 of 101
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Report of Analysis Page 1 of 3
Client Sample ID:WSW 2
Lab Sample ID:FC10706-16 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3832.D 1 10/31/23 06:00 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 0.13 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 0.14 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
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Report of Analysis Page 2 of 3
Client Sample ID:WSW 2
Lab Sample ID:FC10706-16 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride 0.38 0.50 0.20 ug/l J
75-09-2 Methylene Chloride a 1.3 2.0 1.0 ug/l JB
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 b 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 106%70-130%
2037-26-5 Toluene-D8 113%70-130%
460-00-4 4-Bromofluorobenzene 99%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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Report of Analysis Page 3 of 3
Client Sample ID:WSW 2
Lab Sample ID:FC10706-16 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
71 of 101
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SGS North America Inc.
Report of Analysis Page 1 of 1
Client Sample ID:WSW 2
Lab Sample ID:FC10706-16 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093839.D 1 10/31/23 20:39 AF 10/31/23 09:40 OP99821 GCC2467
Run #2
Initial Volume Final Volume
Run #1 37.9 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.018 0.0092 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
72 of 101
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Report of Analysis Page 1 of 3
Client Sample ID:WSW 6
Lab Sample ID:FC10706-17 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 3A3833.D 1 10/31/23 06:23 TD n/a n/a V3A187
Run #2
Purge Volume
Run #1 5.0 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 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
73 of 101
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Report of Analysis Page 2 of 3
Client Sample ID:WSW 6
Lab Sample ID:FC10706-17 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 ND 0.50 0.20 ug/l
74-87-3 Methyl Chloride 0.25 0.50 0.20 ug/l J
75-09-2 Methylene Chloride a 1.3 2.0 1.0 ug/l JB
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 b 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 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 106%70-130%
2037-26-5 Toluene-D8 99%70-130%
460-00-4 4-Bromofluorobenzene 103%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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Report of Analysis Page 3 of 3
Client Sample ID:WSW 6
Lab Sample ID:FC10706-17 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 BS recovery outside control limits high. Suspected laboratory contaminant.
(b) Associated CCV outside of control limits high, sample was 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
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Report of Analysis Page 1 of 1
Client Sample ID:WSW 6
Lab Sample ID:FC10706-17 Date Sampled:10/24/23
Matrix:AQ - Ground Water Date Received:10/25/23
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 CC093841.D 1 10/31/23 21:16 AF 10/31/23 09:40 OP99821 GCC2467
Run #2
Initial Volume Final Volume
Run #1 36.9 ml 2.0 ml
Run #2
CAS No.Compound Result RL MDL Units Q
106-93-4 1,2-Dibromoethane ND 0.019 0.0095 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
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Misc. Forms
Custody Documents and Other Forms
Includes the following where applicable:
 Chain of Custody
Orlando, FL
Section 4
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FC10706: Chain of Custody
Page 1 of 3
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FC10706: Chain of Custody
Page 2 of 3
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Job Number:fc10706 Client:ATLAS-CHARLOTTE,NC
Date / Time Received:10/25/2023 9:15:00 AM Delivery Method:FED EX
Project:STARBRITE RM 0528
Airbill #'s:6840 3320 0198
Cooler Information
1. Custody Seals Present:
Y or N
2. Custody Seals Intact:
4. Cooler temp verification:
3. Temp criteria achieved:
5. Cooler media:
IR Gun
Ice (Bag)
Trip Blank Information Y or N N/A
1. Trip Blank present / cooler:
2. Trip Blank listed on COC:
Sample Information
1. Sample labels present on bottles:
2. Samples presented properly
3. Suffiient volume/containers recv'd for analysis
4. Condition of sample:
5. Sample recv'd within HT
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?
Intact
Comments
Cooler Temps (Raw Measured) °C:
Cooler Temps (Corrected) °C:
Cooler 1: (3.4);
Cooler 1: (3.8);
SM001Rev. Date 05/04/17
SGS Sample Receipt Summary
Test Strip Lot #s:pH 0-3:226422 pH 10-12:Other: (Specify)pH 1.0 - 12.0 222221
3. Type of TB Received
W or S N/A
Y or N N/A
11. % Solids Jar Received?
12. Residual Chlorine Present?
Misc Information
Number of Encores:25 Gram 5 Gram
Residual Chlorine Test Strip Lot #
Number of Lab Filtered Metals:
Technician:SHAYLAP Date:10/25/2023 4:13:28 PM Reviewer:Date:
FC10706: Chain of Custody
Page 3 of 3
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MS Volatiles
QC Data Summaries
Includes the following where applicable:
 Method Blank Summaries
 Blank Spike Summaries
 Matrix Spike and Duplicate Summaries
Orlando, FL
Section 5
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Method Blank Summary Page 1 of 3
Job Number:FC10706
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
V3A187-MB 3A3815.D 1 10/30/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
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
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Method Blank Summary Page 2 of 3
Job Number:FC10706
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
V3A187-MB 3A3815.D 1 10/30/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
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 2.0 2.0 1.0 ug/l
108-10-1 4-Methyl-2-pentanone (MIBK)ND 2.5 1.3 ug/l
1634-04-4 Methyl Tert Butyl Ether ND 0.50 0.13 ug/l
91-20-3 Naphthalene ND 0.50 0.13 ug/l
103-65-1 n-Propylbenzene ND 0.50 0.13 ug/l
100-42-5 Styrene ND 0.50 0.13 ug/l
630-20-6 1,1,1,2-Tetrachloroethane ND 0.50 0.13 ug/l
79-34-5 1,1,2,2-Tetrachloroethane ND 0.50 0.13 ug/l
127-18-4 Tetrachloroethylene ND 0.50 0.13 ug/l
108-88-3 Toluene ND 0.50 0.13 ug/l
87-61-6 1,2,3-Trichlorobenzene ND 0.50 0.13 ug/l
120-82-1 1,2,4-Trichlorobenzene ND 0.50 0.13 ug/l
71-55-6 1,1,1-Trichloroethane ND 0.50 0.13 ug/l
79-00-5 1,1,2-Trichloroethane ND 0.50 0.13 ug/l
79-01-6 Trichloroethylene ND 0.50 0.13 ug/l
75-69-4 Trichlorofluoromethane ND 0.50 0.20 ug/l
96-18-4 1,2,3-Trichloropropane ND 0.50 0.13 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 0.50 0.13 ug/l
108-67-8 1,3,5-Trimethylbenzene ND 0.50 0.13 ug/l
108-05-4 Vinyl Acetate ND 5.0 1.0 ug/l
75-01-4 Vinyl Chloride ND 0.50 0.13 ug/l
m,p-Xylene ND 1.0 0.13 ug/l
95-47-6 o-Xylene ND 0.50 0.13 ug/l
1330-20-7 Xylene (total)ND 1.5 0.25 ug/l
CAS No.Surrogate Recoveries Limits
1868-53-7 Dibromofluoromethane 97%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%70-130%
2037-26-5 Toluene-D8 100%70-130%
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Method Blank Summary Page 3 of 3
Job Number:FC10706
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
V3A187-MB 3A3815.D 1 10/30/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
CAS No.Surrogate Recoveries Limits
460-00-4 4-Bromofluorobenzene 104%70-130%
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Method Blank Summary Page 1 of 1
Job Number:FC10706
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
V3A189-MB 3A3872.D 1 10/31/23 TD n/a n/a V3A189
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-2
CAS No.Compound Result RL MDL Units Q
75-09-2 Methylene Chloride 1.6 2.0 1.0 ug/l J
91-20-3 Naphthalene ND 0.50 0.13 ug/l
95-63-6 1,2,4-Trimethylbenzene ND 0.50 0.13 ug/l
CAS No.Surrogate Recoveries Limits
1868-53-7 Dibromofluoromethane 94%70-130%
17060-07-0 1,2-Dichloroethane-D4 106%70-130%
2037-26-5 Toluene-D8 104%70-130%
460-00-4 4-Bromofluorobenzene 104%70-130%
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Blank Spike Summary Page 1 of 3
Job Number:FC10706
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
V3A187-BS 3A3813.D 1 10/30/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
67-64-1 Acetone 50 63.7 127 70-130
71-43-2 Benzene 10 10.8 108 70-130
108-86-1 Bromobenzene 10 10.5 105 70-130
74-97-5 Bromochloromethane 10 10.1 101 70-130
75-27-4 Bromodichloromethane 10 9.1 91 70-130
75-25-2 Bromoform 10 10 100 70-130
78-93-3 2-Butanone (MEK)50 60.4 121 70-130
104-51-8 n-Butylbenzene 10 10.6 106 70-130
135-98-8 sec-Butylbenzene 10 10.1 101 70-130
98-06-6 tert-Butylbenzene 10 10.3 103 70-130
56-23-5 Carbon Tetrachloride 10 11.6 116 70-130
108-90-7 Chlorobenzene 10 10.2 102 70-130
75-00-3 Chloroethane 10 11.3 113 60-140
67-66-3 Chloroform 10 10.4 104 70-130
95-49-8 o-Chlorotoluene 10 10.7 107 70-130
106-43-4 p-Chlorotoluene 10 10.8 108 70-130
124-48-1 Dibromochloromethane 10 9.4 94 70-130
106-93-4 1,2-Dibromoethane 10 8.7 87 70-130
75-71-8 Dichlorodifluoromethane 10 12.4 124 60-140
95-50-1 1,2-Dichlorobenzene 10 10.2 102 70-130
541-73-1 1,3-Dichlorobenzene 10 9.9 99 70-130
106-46-7 1,4-Dichlorobenzene 10 10 100 70-130
75-34-3 1,1-Dichloroethane 10 10.3 103 70-130
107-06-2 1,2-Dichloroethane 10 10.6 106 70-130
75-35-4 1,1-Dichloroethylene 10 10.2 102 70-130
156-59-2 cis-1,2-Dichloroethylene 10 10.2 102 70-130
156-60-5 trans-1,2-Dichloroethylene 10 10.6 106 70-130
78-87-5 1,2-Dichloropropane 10 11.5 115 70-130
142-28-9 1,3-Dichloropropane 10 10.0 100 70-130
594-20-7 2,2-Dichloropropane 10 10.8 108 70-130
563-58-6 1,1-Dichloropropene 10 10.9 109 70-130
10061-01-5 cis-1,3-Dichloropropene 10 10 100 70-130
10061-02-6 trans-1,3-Dichloropropene 10 8.6 86 70-130
108-20-3 Di-Isopropyl Ether 10 11.9 119 70-130
64-17-5 Ethyl Alcohol 500 490 98 70-130
100-41-4 Ethylbenzene 10 10.4 104 70-130
* = Outside of Control Limits.
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Blank Spike Summary Page 2 of 3
Job Number:FC10706
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
V3A187-BS 3A3813.D 1 10/30/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
591-78-6 2-Hexanone 50 55.6 111 70-130
98-82-8 Isopropylbenzene 10 9.9 99 70-130
99-87-6 p-Isopropyltoluene 10 10.2 102 70-130
74-83-9 Methyl Bromide 10 10.1 101 60-140
74-87-3 Methyl Chloride 10 12.1 121 60-140
75-09-2 Methylene Chloride 10 16.5 165*70-130
108-10-1 4-Methyl-2-pentanone (MIBK)50 54.2 108 70-130
1634-04-4 Methyl Tert Butyl Ether 10 11.3 113 70-130
91-20-3 Naphthalene 10 9.8 98 70-130
103-65-1 n-Propylbenzene 10 10.9 109 70-130
100-42-5 Styrene 10 9.7 97 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 9.9 99 70-130
127-18-4 Tetrachloroethylene 10 9.2 92 70-130
108-88-3 Toluene 10 9.8 98 70-130
87-61-6 1,2,3-Trichlorobenzene 10 10.1 101 70-130
120-82-1 1,2,4-Trichlorobenzene 10 10.1 101 70-130
71-55-6 1,1,1-Trichloroethane 10 10.6 106 70-130
79-00-5 1,1,2-Trichloroethane 10 10.6 106 70-130
79-01-6 Trichloroethylene 10 10.4 104 70-130
75-69-4 Trichlorofluoromethane 10 10.1 101 60-140
96-18-4 1,2,3-Trichloropropane 10 11.3 113 70-130
95-63-6 1,2,4-Trimethylbenzene 10 10.4 104 70-130
108-67-8 1,3,5-Trimethylbenzene 10 10.3 103 70-130
108-05-4 Vinyl Acetate 50 58.2 116 70-130
75-01-4 Vinyl Chloride 10 12.1 121 60-140
m,p-Xylene 20 21.7 109 70-130
95-47-6 o-Xylene 10 9.8 98 70-130
1330-20-7 Xylene (total)30 31.5 105 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 97%70-130%
17060-07-0 1,2-Dichloroethane-D4 100%70-130%
2037-26-5 Toluene-D8 92%70-130%
* = Outside of Control Limits.
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Job Number:FC10706
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
V3A187-BS 3A3813.D 1 10/30/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 104%70-130%
* = Outside of Control Limits.
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Job Number:FC10706
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
V3A189-BS 3A3870.D 1 10/31/23 TD n/a n/a V3A189
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-2
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
75-09-2 Methylene Chloride 10 14.1 141*70-130
91-20-3 Naphthalene 10 8.5 85 70-130
95-63-6 1,2,4-Trimethylbenzene 10 9.1 91 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 95%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%70-130%
2037-26-5 Toluene-D8 104%70-130%
460-00-4 4-Bromofluorobenzene 104%70-130%
* = Outside of Control Limits.
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Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 3
Job Number:FC10706
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
FC10706-2MS 3A3834.D 5 10/31/23 TD n/a n/a V3A187
FC10706-2MSD 3A3835.D 5 10/31/23 TD n/a n/a V3A187
FC10706-2 3A3818.D 1 10/31/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
FC10706-2 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
67-64-1 Acetone ND 250 262 105 250 268 107 2 70-130/20
71-43-2 Benzene ND 50 54.0 108 50 52.6 105 3 70-130/20
108-86-1 Bromobenzene ND 50 50.2 100 50 49.4 99 2 70-130/20
74-97-5 Bromochloromethane ND 50 48.1 96 50 48.0 96 0 70-130/20
75-27-4 Bromodichloromethane ND 50 44.7 89 50 44.2 88 1 70-130/20
75-25-2 Bromoform ND 50 41.4 83 50 41.2 82 0 70-130/20
78-93-3 2-Butanone (MEK)ND 250 264 106 250 277 111 5 70-130/20
104-51-8 n-Butylbenzene ND 50 48.6 97 50 48.9 98 1 70-130/20
135-98-8 sec-Butylbenzene ND 50 48.0 96 50 48.4 97 1 70-130/20
98-06-6 tert-Butylbenzene ND 50 50.8 102 50 50.1 100 1 70-130/20
56-23-5 Carbon Tetrachloride ND 50 54.1 108 50 54.0 108 0 70-130/20
108-90-7 Chlorobenzene ND 50 48.8 98 50 49.2 98 1 70-130/20
75-00-3 Chloroethane ND 50 57.0 114 50 49.6 99 14 60-140/20
67-66-3 Chloroform ND 50 50.9 102 50 50.0 100 2 70-130/20
95-49-8 o-Chlorotoluene ND 50 52.1 104 50 52.1 104 0 70-130/20
106-43-4 p-Chlorotoluene ND 50 51.1 102 50 51.4 103 1 70-130/20
124-48-1 Dibromochloromethane ND 50 43.3 87 50 43.8 88 1 70-130/20
106-93-4 1,2-Dibromoethane ND 50 42.9 86 50 42.0 84 2 70-130/20
75-71-8 Dichlorodifluoromethane ND 50 60.4 121 50 52.6 105 14 60-140/20
95-50-1 1,2-Dichlorobenzene ND 50 48.8 98 50 47.5 95 3 70-130/20
541-73-1 1,3-Dichlorobenzene ND 50 47.9 96 50 46.9 94 2 70-130/20
106-46-7 1,4-Dichlorobenzene ND 50 47.3 95 50 47.1 94 0 70-130/20
75-34-3 1,1-Dichloroethane ND 50 51.6 103 50 50.7 101 2 70-130/20
107-06-2 1,2-Dichloroethane ND 50 51.5 103 50 49.9 100 3 70-130/20
75-35-4 1,1-Dichloroethylene ND 50 51.8 104 50 51.4 103 1 70-130/20
156-59-2 cis-1,2-Dichloroethylene ND 50 51.9 104 50 50.6 101 3 70-130/20
156-60-5 trans-1,2-Dichloroethylene ND 50 53.8 108 50 52.7 105 2 70-130/20
78-87-5 1,2-Dichloropropane ND 50 55.7 111 50 55.6 111 0 70-130/20
142-28-9 1,3-Dichloropropane ND 50 53.5 107 50 52.3 105 2 70-130/20
594-20-7 2,2-Dichloropropane ND 50 43.7 87 50 42.7 85 2 70-130/20
563-58-6 1,1-Dichloropropene ND 50 55.5 111 50 54.6 109 2 70-130/20
10061-01-5 cis-1,3-Dichloropropene ND 50 44.4 89 50 43.8 88 1 70-130/20
10061-02-6 trans-1,3-Dichloropropene ND 50 40.2 80 50 40.1 80 0 70-130/20
108-20-3 Di-Isopropyl Ether ND 50 57.6 115 50 57.1 114 1 70-130/20
64-17-5 Ethyl Alcohol ND 2500 2450 98 2500 4160 166*52*70-130/20
100-41-4 Ethylbenzene ND 50 50.8 102 50 50.9 102 0 70-130/20
* = Outside of Control Limits.
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Matrix Spike/Matrix Spike Duplicate Summary Page 2 of 3
Job Number:FC10706
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
FC10706-2MS 3A3834.D 5 10/31/23 TD n/a n/a V3A187
FC10706-2MSD 3A3835.D 5 10/31/23 TD n/a n/a V3A187
FC10706-2 3A3818.D 1 10/31/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
FC10706-2 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
591-78-6 2-Hexanone ND 250 297 119 250 309 124 4 70-130/20
98-82-8 Isopropylbenzene ND 50 49.5 99 50 49.0 98 1 70-130/20
99-87-6 p-Isopropyltoluene ND 50 48.4 97 50 48.0 96 1 70-130/20
74-83-9 Methyl Bromide ND 50 44.6 89 50 41.9 84 6 60-140/20
74-87-3 Methyl Chloride ND 50 57.5 115 50 50.3 101 13 60-140/20
75-09-2 Methylene Chloride 1.4 JB 50 70.3 138*50 71.4 140*2 70-130/20
108-10-1 4-Methyl-2-pentanone (MIBK)ND 250 262 105 250 271 108 3 70-130/20
1634-04-4 Methyl Tert Butyl Ether ND 50 51.0 102 50 51.2 102 0 70-130/20
91-20-3 Naphthalene 0.24 J 50 44.7 89 50 41.1 82 8 70-130/20
103-65-1 n-Propylbenzene ND 50 52.5 105 50 52.8 106 1 70-130/20
100-42-5 Styrene ND 50 46.7 93 50 44.8 90 4 70-130/20
630-20-6 1,1,1,2-Tetrachloroethane ND 50 43.8 88 50 44.4 89 1 70-130/20
79-34-5 1,1,2,2-Tetrachloroethane ND 50 45.1 90 50 46.6 93 3 70-130/20
127-18-4 Tetrachloroethylene ND 50 48.6 97 50 49.2 98 1 70-130/20
108-88-3 Toluene ND 50 51.2 102 50 50.6 101 1 70-130/20
87-61-6 1,2,3-Trichlorobenzene ND 50 49.1 98 50 46.3 93 6 70-130/20
120-82-1 1,2,4-Trichlorobenzene ND 50 49.0 98 50 46.0 92 6 70-130/20
71-55-6 1,1,1-Trichloroethane ND 50 52.5 105 50 52.7 105 0 70-130/20
79-00-5 1,1,2-Trichloroethane ND 50 48.2 96 50 48.1 96 0 70-130/20
79-01-6 Trichloroethylene ND 50 50.5 101 50 49.3 99 2 70-130/20
75-69-4 Trichlorofluoromethane ND 50 49.5 99 50 41.9 84 17 60-140/20
96-18-4 1,2,3-Trichloropropane ND 50 51.1 102 50 51.3 103 0 70-130/20
95-63-6 1,2,4-Trimethylbenzene 0.27 J 50 48.8 97 50 48.5 96 1 70-130/20
108-67-8 1,3,5-Trimethylbenzene ND 50 50.1 100 50 49.2 98 2 70-130/20
108-05-4 Vinyl Acetate ND 250 339 136*250 331 132*2 70-130/20
75-01-4 Vinyl Chloride ND 50 59.2 118 50 51.6 103 14 60-140/20
m,p-Xylene ND 100 103 103 100 105 105 2 70-130/20
95-47-6 o-Xylene ND 50 47.3 95 50 46.9 94 1 70-130/20
1330-20-7 Xylene (total)ND 150 151 101 150 152 101 1 70-130/20
CAS No.Surrogate Recoveries MS MSD FC10706-2 Limits
1868-53-7 Dibromofluoromethane 98%97%96%70-130%
17060-07-0 1,2-Dichloroethane-D4 103%101%103%70-130%
2037-26-5 Toluene-D8 99%99%99%70-130%
* = Outside of Control Limits.
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Matrix Spike/Matrix Spike Duplicate Summary Page 3 of 3
Job Number:FC10706
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
FC10706-2MS 3A3834.D 5 10/31/23 TD n/a n/a V3A187
FC10706-2MSD 3A3835.D 5 10/31/23 TD n/a n/a V3A187
FC10706-2 3A3818.D 1 10/31/23 TD n/a n/a V3A187
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-8, FC10706-9,
FC10706-10, FC10706-11, FC10706-12, FC10706-13, FC10706-14, FC10706-15, FC10706-16, FC10706-17
CAS No.Surrogate Recoveries MS MSD FC10706-2 Limits
460-00-4 4-Bromofluorobenzene 103%105%104%70-130%
* = Outside of Control Limits.
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Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 1
Job Number:FC10706
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
FC10730-2MS 3A3893.D 10 11/01/23 TD n/a n/a V3A189
FC10730-2MSD 3A3894.D 10 11/01/23 TD n/a n/a V3A189
FC10730-2 a 3A3884.D 10 11/01/23 TD n/a n/a V3A189
The QC reported here applies to the following samples:Method: SM 6200B
FC10706-2
FC10730-2 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
75-09-2 Methylene Chloride 17.7 J 100 122 104 100 114 96 7 70-130/20
91-20-3 Naphthalene ND 100 90.6 91 100 87.3 87 4 70-130/20
95-63-6 1,2,4-Trimethylbenzene 8.8 100 105 96 100 101 92 4 70-130/20
CAS No.Surrogate Recoveries MS MSD FC10730-2 Limits
1868-53-7 Dibromofluoromethane 95%95%94%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%104%107%70-130%
2037-26-5 Toluene-D8 102%104%104%70-130%
460-00-4 4-Bromofluorobenzene 108%106%103%70-130%
(a) Confirmation run.
* = Outside of Control Limits.
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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
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Method Blank Summary Page 1 of 1
Job Number:FC10706
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
OP99798-MB CC093784.D 1 10/30/23 AF 10/30/23 OP99798 GCC2466
The QC reported here applies to the following samples:Method: EPA 504.1
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-12, FC10706-14
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 96%63-137%
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Method Blank Summary Page 1 of 1
Job Number:FC10706
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
OP99798-MB CC093844.D 1 10/31/23 AF 10/30/23 OP99798 GCC2467
The QC reported here applies to the following samples:Method: EPA 504.1
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-12, FC10706-14
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 92%63-137%
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Method Blank Summary Page 1 of 1
Job Number:FC10706
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
OP99821-MB CC093830.D 1 10/31/23 AF 10/31/23 OP99821 GCC2467
The QC reported here applies to the following samples:Method: EPA 504.1
FC10706-8, FC10706-9, FC10706-10, FC10706-11, FC10706-13, FC10706-15, FC10706-16, FC10706-17
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 92%63-137%
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Blank Spike Summary Page 1 of 1
Job Number:FC10706
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
OP99821-BS CC093831.D 1 10/31/23 AF 10/31/23 OP99821 GCC2467
The QC reported here applies to the following samples:Method: EPA 504.1
FC10706-8, FC10706-9, FC10706-10, FC10706-11, FC10706-13, FC10706-15, FC10706-16, FC10706-17
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
106-93-4 1,2-Dibromoethane 0.25 0.26 104 70-130
CAS No.Surrogate Recoveries BSP Limits
460-00-4 4-Bromofluorobenzene 92%63-137%
* = Outside of Control Limits.
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Blank Spike/Blank Spike Duplicate Summary Page 1 of 1
Job Number:FC10706
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
OP99798-BS CC093785.D 1 10/30/23 AF 10/30/23 OP99798 GCC2466
OP99798-BSD CC093786.D 1 10/30/23 AF 10/30/23 OP99798 GCC2466
The QC reported here applies to the following samples:Method: EPA 504.1
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-12, FC10706-14
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 0.27 108 0.27 108 0 70-130/25
CAS No.Surrogate Recoveries BSP BSD Limits
460-00-4 4-Bromofluorobenzene 98%100%63-137%
* = Outside of Control Limits.
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Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 1
Job Number:FC10706
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
OP99798-MS CC093787.D 1 10/30/23 AF 10/30/23 OP99798 GCC2466
OP99798-MSD CC093788.D 1 10/30/23 AF 10/30/23 OP99798 GCC2466
FC10624-1 CC093800.D 1 10/31/23 AF 10/30/23 OP99798 GCC2466
The QC reported here applies to the following samples:Method: EPA 504.1
FC10706-1, FC10706-2, FC10706-3, FC10706-4, FC10706-5, FC10706-6, FC10706-7, FC10706-12, FC10706-14
FC10624-1 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 0.236 0.20 85 0.24 0.22 92 10 70-130/25
CAS No.Surrogate Recoveries MS MSD FC10624-1 Limits
460-00-4 4-Bromofluorobenzene 83%89%93%63-137%
* = Outside of Control Limits.
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Duplicate Summary Page 1 of 1
Job Number:FC10706
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
OP99821-DUP CC093832.D 1 10/31/23 AF 10/31/23 OP99821 GCC2467
FC10706-13 CC093837.D 1 10/31/23 AF 10/31/23 OP99821 GCC2467
The QC reported here applies to the following samples:Method: EPA 504.1
FC10706-8, FC10706-9, FC10706-10, FC10706-11, FC10706-13, FC10706-15, FC10706-16, FC10706-17
FC10706-13 DUP
CAS No.Compound ug/l Q ug/l Q RPD Limits
106-93-4 1,2-Dibromoethane ND ND nc 25
CAS No.Surrogate Recoveries DUP FC10706-13 Limits
460-00-4 4-Bromofluorobenzene 87%89%63-137%
* = Outside of Control Limits.
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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)

11/06/23
Technical Report for
ATC Group Services LLC
RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
RM0528
SGS Job Number: FC10770
Sampling Date: 10/26/23
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] 
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 unless noted
in the narrative, comments or footnotes.
Client Service contact: Muna Mohammed 407-425-6700
Norm Farmer
Technical Director
Orlando, FL 11/06/23
e-Hardcopy 2.0
Automated Report
37
SGS is the sole authority for authorizing edits or modifications to this document.
Unauthorized modification of this report is strictly prohibited.
Review standard terms at: http://www.sgs.com/en/terms-and-conditions
The results set forth herein are provided by SGS North America Inc.
Please share your ideas about
how we can serve you better at:
[e-mail]
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FC10770
Table of Contents
-1-
Sections:
Section 1: Sample Summary ...................................................................................................3
Section 2: Summary of Hits ....................................................................................................4
Section 3: Sample Results ........................................................................................................5
3.1: FC10770-1: RW 1 .........................................................................................................6
3.2: FC10770-2: RW 3 .........................................................................................................9
3.3: FC10770-3: INF ............................................................................................................12
3.4: FC10770-4: 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 ...................................................................................................24
5.3: Matrix Spike/Matrix Spike Duplicate Summary ...........................................................26
Section 6: Metals Analysis - QC Data Summaries ................................................................28
6.1: Prep QC MP43067: Ca,Pb,Mg ......................................................................................29
Section 7: General Chemistry - QC Data Summaries ..........................................................35
7.1: Method Blank and Spike Results Summary ..................................................................36
7.2: Duplicate Results Summary ..........................................................................................37
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Sample Summary
ATC Group Services LLC
Job No:FC10770
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
FC10770-1 10/26/23 10:30 BP 10/27/23 AQ Ground Water RW 1
FC10770-2 10/26/23 11:00 BP 10/27/23 AQ Ground Water RW 3
FC10770-3 10/26/23 12:00 BP 10/27/23 AQ Ground Water INF
FC10770-4 10/26/23 12:30 BP 10/27/23 AQ Ground Water EFF
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Summary of Hits Page 1 of 1
Job Number:FC10770
Account:ATC Group Services LLC
Project:RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
Collected:10/26/23
Lab Sample ID Client Sample ID Result/
Analyte Qual RL MDL Units Method
FC10770-1 RW 1
Methyl Tert Butyl Ether 10.9 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 0.47 J 0.50 0.13 ug/l SM 6200B
Calcium 14100 1000 50 ug/l SW846 6010D
Lead 5.2 5.0 1.1 ug/l SW846 6010D
Magnesium 4900 J 5000 35 ug/l SW846 6010D
Hardness, Total as CaCO3 a 55.4 23 0.27 mg/l SM19 2340B
pH b 6.61 su SM4500H B-11/SW9040C
FC10770-2 RW 3
Methyl Tert Butyl Ether 18.2 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 1.7 0.50 0.13 ug/l SM 6200B
Calcium 14300 1000 50 ug/l SW846 6010D
Lead 24.8 5.0 1.1 ug/l SW846 6010D
Magnesium 4230 J 5000 35 ug/l SW846 6010D
Hardness, Total as CaCO3 a 53.1 23 0.27 mg/l SM19 2340B
pH c 6.42 su SM4500H B-11/SW9040C
FC10770-3 INF
Methyl Tert Butyl Ether 16.0 0.50 0.13 ug/l SM 6200B
1,2-Dichloroethane 1.1 0.50 0.13 ug/l SM 6200B
Calcium 14100 1000 50 ug/l SW846 6010D
Lead 2.1 J 5.0 1.1 ug/l SW846 6010D
Magnesium 4600 J 5000 35 ug/l SW846 6010D
Hardness, Total as CaCO3 a 54.2 23 0.27 mg/l SM19 2340B
pH d 6.37 su SM4500H B-11/SW9040C
FC10770-4 EFF
Calcium 14300 1000 50 ug/l SW846 6010D
Magnesium 5120 5000 35 ug/l SW846 6010D
Hardness, Total as CaCO3 a 56.8 23 0.27 mg/l SM19 2340B
pH e 7.98 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. Temp of pH Reading: 19.1 Deg. C
(c) Field analysis required. Received out of hold time and analyzed by request. Temp of pH Reading: 19.2 Deg. C
(d) Field analysis required. Received out of hold time and analyzed by request. Temp of pH Reading: 19.5 Deg. C
(e) Field analysis required. Received out of hold time and analyzed by request. Temp of pH Reading: 19.6 Deg. C
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Sample Results
Report of Analysis
Orlando, FL
Section 3
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Report of Analysis Page 1 of 1
Client Sample ID:RW 1
Lab Sample ID:FC10770-1 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 3A3921.D 1 11/01/23 19:26 TD n/a n/a V3A190
Run #2
Purge Volume
Run #1 5.0 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 10.9 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane 0.47 0.50 0.13 ug/l J
CAS No.Surrogate Recoveries Run# 1 Run# 2 Limits
1868-53-7 Dibromofluoromethane 94%70-130%
17060-07-0 1,2-Dichloroethane-D4 107%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
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Report of Analysis Page 1 of 1
Client Sample ID:RW 1
Lab Sample ID:FC10770-1 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 14100 1000 50 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
Lead 5.2 5.0 1.1 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
Magnesium 4900 J 5000 35 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA19800
(2) Prep QC Batch: MP43067
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
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Report of Analysis Page 1 of 1
Client Sample ID:RW 1
Lab Sample ID:FC10770-1 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 55.4 23 0.27 mg/l 1 11/02/23 15:24 LM SM19 2340B
Solids, Total Suspended ND 25 2.1 mg/l 1 10/30/23 10:05 SS SM2540 D-15
pH b 6.61 su 1 10/30/23 11:45 CC 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. Temp of pH Reading: 19.1 Deg. C
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
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Client Sample ID:RW 3
Lab Sample ID:FC10770-2 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 3A3922.D 1 11/01/23 19:50 TD n/a n/a V3A190
Run #2
Purge Volume
Run #1 5.0 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 18.2 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 93%70-130%
17060-07-0 1,2-Dichloroethane-D4 107%70-130%
2037-26-5 Toluene-D8 103%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
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Report of Analysis Page 1 of 1
Client Sample ID:RW 3
Lab Sample ID:FC10770-2 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 14300 1000 50 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
Lead 24.8 5.0 1.1 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
Magnesium 4230 J 5000 35 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA19800
(2) Prep QC Batch: MP43067
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
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Report of Analysis Page 1 of 1
Client Sample ID:RW 3
Lab Sample ID:FC10770-2 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 53.1 23 0.27 mg/l 1 11/02/23 15:54 LM SM19 2340B
Solids, Total Suspended ND 25 2.1 mg/l 1 10/30/23 10:05 SS SM2540 D-15
pH b 6.42 su 1 10/30/23 11:45 CC 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. Temp of pH Reading: 19.2 Deg. C
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
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Report of Analysis Page 1 of 1
Client Sample ID:INF
Lab Sample ID:FC10770-3 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 3A3960.D 1 11/02/23 11:21 TD n/a n/a V3A192
Run #2
Purge Volume
Run #1 5.0 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 16.0 0.50 0.13 ug/l
107-06-2 1,2-Dichloroethane 1.1 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 105%70-130%
2037-26-5 Toluene-D8 102%70-130%
460-00-4 4-Bromofluorobenzene 103%70-130%
ND = Not detected MDL = Method Detection Limit J = Indicates an estimated value
RL = Reporting Limit B = Indicates analyte found in associated method blank
E = Indicates value exceeds calibration range N = Indicates presumptive evidence of a compound
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Report of Analysis Page 1 of 1
Client Sample ID:INF
Lab Sample ID:FC10770-3 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 14100 1000 50 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
Lead 2.1 J 5.0 1.1 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
Magnesium 4600 J 5000 35 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA19800
(2) Prep QC Batch: MP43067
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
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Client Sample ID:INF
Lab Sample ID:FC10770-3 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 11/02/23 15:59 LM SM19 2340B
Solids, Total Suspended ND 25 2.1 mg/l 1 10/30/23 10:05 SS SM2540 D-15
pH b 6.37 su 1 10/30/23 11:45 CC 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. Temp of pH Reading: 19.5 Deg. C
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
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Report of Analysis Page 1 of 1
Client Sample ID:EFF
Lab Sample ID:FC10770-4 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 3A3961.D 1 11/02/23 11:44 TD n/a n/a V3A192
Run #2
Purge Volume
Run #1 5.0 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 94%70-130%
17060-07-0 1,2-Dichloroethane-D4 106%70-130%
2037-26-5 Toluene-D8 103%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
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Report of Analysis Page 1 of 1
Client Sample ID:EFF
Lab Sample ID:FC10770-4 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 14300 1000 50 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
Lead ND 5.0 1.1 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
Magnesium 5120 5000 35 ug/l 1 11/01/23 11/02/23 LM SW846 6010D 1 SW846 3010A 2
(1) Instrument QC Batch: MA19800
(2) Prep QC Batch: MP43067
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
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Report of Analysis Page 1 of 1
Client Sample ID:EFF
Lab Sample ID:FC10770-4 Date Sampled:10/26/23
Matrix:AQ - Ground Water Date Received:10/27/23
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 56.8 23 0.27 mg/l 1 11/02/23 16:04 LM SM19 2340B
Solids, Total Suspended ND 25 2.1 mg/l 1 10/30/23 10:05 SS SM2540 D-15
pH b 7.98 su 1 10/30/23 11:45 CC 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. Temp of pH Reading: 19.6 Deg. C
RL = Reporting Limit ND = Not detected
MDL = Method Detection Limit J = Indicates a result >= MDL but < RL
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Misc. Forms
Custody Documents and Other Forms
Includes the following where applicable:
 Chain of Custody
Orlando, FL
Section 4
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FC10770: Chain of Custody
Page 1 of 2
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Job Number:fc10770 Client:ATLAS
Date / Time Received:10/27/2023 9:30:00 AM Delivery Method:FED EX
Project:STARBRITE
Airbill #'s:6840 3320 0187
Cooler Information
1. Custody Seals Present:
Y or N
2. Custody Seals Intact:
4. Cooler temp verification:
3. Temp criteria achieved:
5. Cooler media:
IR Gun
Ice (Bag)
Trip Blank Information Y or N N/A
1. Trip Blank present / cooler:
2. Trip Blank listed on COC:
Sample Information
1. Sample labels present on bottles:
2. Samples presented properly
3. Suffiient volume/containers recv'd for analysis
4. Condition of sample:
5. Sample recv'd within HT
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?
Intact
Comments
Cooler Temps (Raw Measured) °C:
Cooler Temps (Corrected) °C:
Cooler 1: (2.0);
Cooler 1: (2.4);
SM001Rev. Date 05/04/17
SGS Sample Receipt Summary
Test Strip Lot #s:pH 0-3:226422 pH 10-12:Other: (Specify)pH 1.0 - 12.0 222221
3. Type of TB Received
W or S N/A
Y or N N/A
11. % Solids Jar Received?
12. Residual Chlorine Present?
Misc Information
Number of Encores:25 Gram 5 Gram
Residual Chlorine Test Strip Lot #
Number of Lab Filtered Metals:
Technician:SHAYLAP Date:10/27/2023 2:58:23 PM Reviewer:Date:
FC10770: Chain of Custody
Page 2 of 2
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MS Volatiles
QC Data Summaries
Includes the following where applicable:
 Method Blank Summaries
 Blank Spike Summaries
 Matrix Spike and Duplicate Summaries
Orlando, FL
Section 5
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Method Blank Summary Page 1 of 1
Job Number:FC10770
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
V3A190-MB 3A3904.D 1 11/01/23 TD n/a n/a V3A190
The QC reported here applies to the following samples:Method: SM 6200B
FC10770-1, FC10770-2
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 92%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%70-130%
2037-26-5 Toluene-D8 103%70-130%
460-00-4 4-Bromofluorobenzene 102%70-130%
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Method Blank Summary Page 1 of 1
Job Number:FC10770
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
V3A192-MB 3A3957.D 1 11/02/23 TD n/a n/a V3A192
The QC reported here applies to the following samples:Method: SM 6200B
FC10770-3, FC10770-4
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 94%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%70-130%
2037-26-5 Toluene-D8 103%70-130%
460-00-4 4-Bromofluorobenzene 103%70-130%
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Blank Spike Summary Page 1 of 1
Job Number:FC10770
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
V3A190-BS 3A3902.D 1 11/01/23 TD n/a n/a V3A190
The QC reported here applies to the following samples:Method: SM 6200B
FC10770-1, FC10770-2
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
71-43-2 Benzene 10 9.0 90 70-130
107-06-2 1,2-Dichloroethane 10 9.1 91 70-130
100-41-4 Ethylbenzene 10 9.5 95 70-130
1634-04-4 Methyl Tert Butyl Ether 10 9.6 96 70-130
108-88-3 Toluene 10 9.4 94 70-130
1330-20-7 Xylene (total)30 28.6 95 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 96%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%70-130%
2037-26-5 Toluene-D8 105%70-130%
460-00-4 4-Bromofluorobenzene 105%70-130%
* = Outside of Control Limits.
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Blank Spike Summary Page 1 of 1
Job Number:FC10770
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
V3A192-BS 3A3955.D 1 11/02/23 TD n/a n/a V3A192
The QC reported here applies to the following samples:Method: SM 6200B
FC10770-3, FC10770-4
Spike BSP BSP
CAS No.Compound ug/l ug/l %Limits
71-43-2 Benzene 10 9.0 90 70-130
107-06-2 1,2-Dichloroethane 10 9.0 90 70-130
100-41-4 Ethylbenzene 10 9.4 94 70-130
1634-04-4 Methyl Tert Butyl Ether 10 9.4 94 70-130
108-88-3 Toluene 10 9.3 93 70-130
1330-20-7 Xylene (total)30 28.3 94 70-130
CAS No.Surrogate Recoveries BSP Limits
1868-53-7 Dibromofluoromethane 94%70-130%
17060-07-0 1,2-Dichloroethane-D4 101%70-130%
2037-26-5 Toluene-D8 103%70-130%
460-00-4 4-Bromofluorobenzene 103%70-130%
* = Outside of Control Limits.
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Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 1
Job Number:FC10770
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
FC10736-8MS 3A3923.D 5 11/01/23 TD n/a n/a V3A190
FC10736-8MSD 3A3924.D 5 11/01/23 TD n/a n/a V3A190
FC10736-8 3A3915.D 1 11/01/23 TD n/a n/a V3A190
The QC reported here applies to the following samples:Method: SM 6200B
FC10770-1, FC10770-2
FC10736-8 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 41.4 83 50 40.9 82 1 70-130/20
107-06-2 1,2-Dichloroethane ND 50 40.4 81 50 39.9 80 1 70-130/20
100-41-4 Ethylbenzene 0.45 J 50 43.6 86 50 42.9 85 2 70-130/20
1634-04-4 Methyl Tert Butyl Ether ND 50 41.4 83 50 41.1 82 1 70-130/20
108-88-3 Toluene ND 50 43.1 86 50 42.6 85 1 70-130/20
1330-20-7 Xylene (total)2.1 150 132 87 150 129 85 2 70-130/20
CAS No.Surrogate Recoveries MS MSD FC10736-8 Limits
1868-53-7 Dibromofluoromethane 94%96%93%70-130%
17060-07-0 1,2-Dichloroethane-D4 104%105%105%70-130%
2037-26-5 Toluene-D8 103%103%105%70-130%
460-00-4 4-Bromofluorobenzene 105%106%106%70-130%
* = Outside of Control Limits.
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Matrix Spike/Matrix Spike Duplicate Summary Page 1 of 1
Job Number:FC10770
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
FC10726-2MS 3A3978.D 5 11/02/23 TD n/a n/a V3A192
FC10726-2MSD 3A3979.D 5 11/02/23 TD n/a n/a V3A192
FC10726-2 3A3967.D 1 11/02/23 TD n/a n/a V3A192
The QC reported here applies to the following samples:Method: SM 6200B
FC10770-3, FC10770-4
FC10726-2 Spike MS MS Spike MSD MSD Limits
CAS No.Compound ug/l Q ug/l ug/l %ug/l ug/l %RPD Rec/RPD
71-43-2 Benzene ND 50 39.3 79 50 41.3 83 5 70-130/20
107-06-2 1,2-Dichloroethane ND 50 37.2 74 50 39.6 79 6 70-130/20
100-41-4 Ethylbenzene ND 50 40.6 81 50 42.4 85 4 70-130/20
1634-04-4 Methyl Tert Butyl Ether 1.5 50 39.8 77 50 42.4 82 6 70-130/20
108-88-3 Toluene ND 50 40.9 82 50 42.7 85 4 70-130/20
1330-20-7 Xylene (total)ND 150 121 81 150 127 85 5 70-130/20
CAS No.Surrogate Recoveries MS MSD FC10726-2 Limits
1868-53-7 Dibromofluoromethane 95%96%94%70-130%
17060-07-0 1,2-Dichloroethane-D4 105%103%104%70-130%
2037-26-5 Toluene-D8 102%102%102%70-130%
460-00-4 4-Bromofluorobenzene 104%102%103%70-130%
* = Outside of Control Limits.
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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
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BLANK RESULTS SUMMARY
Part 2 - Method Blanks
Login Number: FC10770
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP43067 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 11/01/23
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 17.6 <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
Lithium 10 .5 1.3
Magnesium 5000 35 35 -14 <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 MP43067: FC10770-1, FC10770-2, FC10770-3, FC10770-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
_________________________________________________________________________________________________________
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MATRIX SPIKE AND DUPLICATE RESULTS SUMMARY
Login Number: FC10770
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP43067 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 11/01/23 11/01/23
FC10770-1 QC FC10770-1 Spikelot QC
Metal Original DUP RPD Limits Original MS MPFLICP5 % Rec Limits
Aluminum anr
Antimony anr
Arsenic anr
Barium anr
Beryllium anr
Boron
Cadmium anr
Calcium 14100 14000 0.7 0-20 14100 57300 45000 96.0 80-120
Chromium anr
Cobalt anr
Copper anr
Iron anr
Lead 5.2 5.5 5.6 0-20 5.2 201 200 97.9 80-120
Lithium
Magnesium 4900 4860 0.8 0-20 4900 47600 45000 94.9 80-120
Manganese anr
Molybdenum anr
Nickel anr
Potassium anr
Selenium anr
Silver anr
Sodium anr
Strontium
Thallium anr
Tin
Titanium
Vanadium anr
Zinc anr
Associated samples MP43067: FC10770-1, FC10770-2, FC10770-3, FC10770-4
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
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MATRIX SPIKE AND DUPLICATE RESULTS SUMMARY
Login Number: FC10770
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP43067 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 11/01/23
FC10770-1 Spikelot MSD QC
Metal Original MSD MPFLICP5 % Rec RPD Limit
Aluminum anr
Antimony anr
Arsenic anr
Barium anr
Beryllium anr
Boron
Cadmium anr
Calcium 14100 57700 45000 96.9 0.7 20
Chromium anr
Cobalt anr
Copper anr
Iron anr
Lead 5.2 200 200 97.4 0.5 20
Lithium
Magnesium 4900 48000 45000 95.8 0.8 20
Manganese anr
Molybdenum anr
Nickel anr
Potassium anr
Selenium anr
Silver anr
Sodium anr
Strontium
Thallium anr
Tin
Titanium
Vanadium anr
Zinc anr
Associated samples MP43067: FC10770-1, FC10770-2, FC10770-3, FC10770-4
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
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SPIKE BLANK AND LAB CONTROL SAMPLE SUMMARY
Login Number: FC10770
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP43067 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 11/01/23
BSP Spikelot QC
Metal Result MPFLICP5 % Rec Limits
Aluminum anr
Antimony anr
Arsenic anr
Barium anr
Beryllium anr
Boron
Cadmium anr
Calcium 43300 45000 96.2 80-120
Chromium anr
Cobalt anr
Copper anr
Iron anr
Lead 191 200 95.5 80-120
Lithium
Magnesium 42000 45000 93.3 80-120
Manganese anr
Molybdenum anr
Nickel anr
Potassium anr
Selenium anr
Silver anr
Sodium anr
Strontium
Thallium anr
Tin
Titanium
Vanadium anr
Zinc anr
Associated samples MP43067: FC10770-1, FC10770-2, FC10770-3, FC10770-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
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SERIAL DILUTION RESULTS SUMMARY
Login Number: FC10770
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP43067 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 11/01/23
FC10770-1 QC
Metal Original SDL 1:5 %DIF Limits
Aluminum anr
Antimony anr
Arsenic anr
Barium anr
Beryllium anr
Boron
Cadmium anr
Calcium 14100 14500 2.3 0-10
Chromium anr
Cobalt anr
Copper anr
Iron anr
Lead 5.20 0.00 100.0(a) 0-10
Lithium
Magnesium 4900 4990 1.9 0-10
Manganese anr
Molybdenum anr
Nickel anr
Potassium anr
Selenium anr
Silver anr
Sodium anr
Strontium
Thallium anr
Tin
Titanium
Vanadium anr
Zinc anr
Associated samples MP43067: FC10770-1, FC10770-2, FC10770-3, FC10770-4
Results < IDL are shown as zero for calculation purposes
(*) Outside of QC limits
(anr) Analyte not requested
(a) Percent difference acceptable due to low initial sample concentration (< 50 times IDL).
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POST DIGESTATE SPIKE SUMMARY
Login Number: FC10770
Account: ATCNCC - ATC Group Services LLC
Project: RM 0528 Starbrite; 5639 Statesville Rd, Charlotte, NC
QC Batch ID: MP43067 Methods: SW846 6010D
Matrix Type: AQUEOUS Units: ug/l
Prep Date: 11/01/23
Sample Final FC10770-1 PS Spike Spike Spike QC
Metal ml ml Raw Corr.** ug/l ml ug/ml ug/l % Rec Limits
Aluminum
Antimony
Arsenic
Barium
Beryllium
Boron
Cadmium
Calcium 9.8 10 14130 13847.4 18610 0.2 250 5000 95.3 80-120
Chromium
Cobalt
Copper
Iron
Lead 9.8 10 5.2 5.096 51.5 0.2 2.5 50 92.8 80-120
Lithium
Magnesium 9.8 10 4896 4798.08 9531 0.2 250 5000 94.7 80-120
Manganese
Molybdenum
Nickel
Potassium
Selenium
Silver
Sodium
Strontium
Thallium
Tin
Titanium
Vanadium
Zinc
Associated samples MP43067: FC10770-1, FC10770-2, FC10770-3, FC10770-4
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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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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METHOD BLANK AND SPIKE RESULTS SUMMARY
GENERAL CHEMISTRY
Login Number: FC10770
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 GN95740 2.5 0.0 mg/l 200 191 95.6 85-115%
Associated Samples:
Batch GN95740: FC10770-1, FC10770-2, FC10770-3, FC10770-4
(*) Outside of QC limits
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DUPLICATE RESULTS SUMMARY
GENERAL CHEMISTRY
Login Number: FC10770
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 GN95740 FC10714-15 mg/l 563 553 1.8 0-10%
pH GN95748 FC10704-2 su 7.09 7.06 0.4 0-10%
pH GN95748 FC10704-2 su 7.09 7.06 0.4 0-10%
Associated Samples:
Batch GN95740: FC10770-1, FC10770-2, FC10770-3, FC10770-4
Batch GN95748: FC10770-1, FC10770-2, FC10770-3, FC10770-4
(*) Outside of QC limits
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