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WithersRavenel
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115 MacKenan Drive | Cary, NC 27511
t: 919.469.3340 | f: 919.467.6008 | www.withersravenel.com | License No. C‐0832
Asheville | Cary | Greensboro | Pittsboro | Raleigh | Wilmington
ANNUAL MONITORING REPORT
Save More #045
NCDEQ Incident # 15046
UST # WS‐4643
1424 North Fayetteville Street
Asheboro, Randolph County, North Carolina
WithersRavenel Project No. 02172214.24
Prepared for:
State of North Carolina
Department of Environmental Quality
Division of Waste Management
Underground Storage Tank Section
Trust Fund Branch
1646 Mail Service Center
Raleigh, North Carolina 27699‐1646
Prepared by:
WithersRavenel
115 MacKenan Drive
Cary, North Carolina 27511
North Carolina Firm License No. C‐0832
July 8, 2021
WithersRavenel
Our People. Your Success.
115 MacKenan Drive | Cary, NC 27511
t: 919.469.3340 | f: 919.467.6008 | www.withersravenel.com | License No. C‐0832
Asheville | Cary | Greensboro | Pittsboro | Raleigh | Wilmington
July 8, 2021
State of North Carolina
Department of Environmental Quality
Trust Fund Branch
Division of Waste Management‐Underground Storage Tank Section
1646 Mail Service Center
Raleigh, North Carolina 27699‐1646
Attn: Mr. Herb Berger, P.G.
Re: Annual Monitoring Report
Save More #045
1424 North Fayetteville Street
Asheboro, Randolph County, North Carolina
Groundwater Incident Number: 15046
UST Number: WS‐4643
WR Project Number: 02172214.24
Mr. Berger,
WithersRavenel, Inc. (WR) has completed this Annual Monitoring Report to document the receptor
survey and groundwater sampling activities completed at the facility in association with our
proposal, numbered TA‐01, for the above referenced site, approved by the Trust Fund Branch on
May 6, 2021. The enclosed report summarizes results of the recently completed monitoring
activities.
WR appreciates the opportunity to be of service to the Trust Fund Branch. Should you have any
questions regarding the attached, please contact Elizabeth Allyn at (919) 469‐3340.
Cordially,
WithersRavenel
Laura Robertson Elliott, P.G. Elizabeth A. Allyn, P.G.
Project Geologist Senior Project Manager
WithersRavenel
Our People. Your Success.
Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report July 2021
i
TABLE OF CONTENTS
SECTION A. SITE INFORMATION ..................................................................................................................... 1
SECTION B. EXECUTIVE SUMMARY ................................................................................................................ 3
SECTION C. SITE HISTORY AND CHARACTERIZATION ............................................................................ 4
SECTION D. RECEPTOR SURVEY ..................................................................................................................... 6
SECTION E. GROUNDWATER SAMPLING – JUNE 2021 ........................................................................... 7
SECTION F. CONCLUSIONS AND RECOMMENDATIONS ........................................................................ 8
FIGURES
Figure 1 General Location Map
Figure 2 Site Map
Figure 3 Site Map with Adjacent Parcels Shown
Figure 4 Groundwater Elevation Contour Map – June 2021
Figure 5 Groundwater Analytical Results Map – June 2021
Figure 6 Dissolved Benzene Isoconcentration Contour Map – June 2021
TABLES
Table B‐1 Site History: UST/AST System & Other Release Information
Table B‐4 Summary of Groundwater Analytical Results
Table B‐5C Adjacent Property Information
Table B‐7 Monitoring Well Construction Information and Liquid Level Data
APPENDICES
Appendix A Field Notes & Photographic Record
Appendix B Returned Water Supply Well Information Sheets & City of Asheboro Utility
Department Information
Appendix C Laboratory Analytical Report & Chain‐of‐Custody
Appendix D General Standard Operating Procedures
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Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report July 2021
1
SECTION A. SITE INFORMATION
1. Site Identification
Date of Report: July 8, 2021
Facility I.D.: 00‐0‐0000018414
Incident No.: 15046
No.: WS‐4643
Site Risk: Intermediate
Site Rank: I0150D
Land Use Category: Industrial/Commercial
Site Name: Save More #045
Site Location: 1424 North Fayetteville Street
Nearest City/Town: Asheboro
County: Randolph
Description of Geographical Data Point: Center of Source Area
Location Method: Google Earth
Latitude: 35.733008° N
Longitude: 79.807911° W
2. Contact Information
Responsible Party: Save More, Inc. (dissolved)
Address: Unknown
Phone: Unknown
Property Owner: Rey Petroleum LLC
Address: 300 Abbey Court, Alpharetta, GA 30004
Phone: 678‐541‐0750
Property Occupant: Marathon Gas
Address: 1424 N. Fayetteville Street, Asheboro, NC 27203
Phone: 336‐672‐3496
Consultant/Contractor: WithersRavenel
Address: 115 Mackenan Drive, Cary, NC 27511
Phone: 919‐469‐3340
Analytical Laboratory: Waypoint Analytical, LLC
State Certification Number: ENV402
Address: 449 Springbrook Rd., Charlotte, NC 28217
Phone: 704‐529‐6364
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Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report July 2021
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3. Release Information
Date Discovered: November 1995
Estimated Quantity of Release: Unknown
Cause of Release: Unknown
Source of Release: UST System
Type of Material Release Occurred: Gasoline
Criteria Used to Classify Risk: GCL exceedances
Sizes & Contents of UST System(s) from which
Release Occurred:
(2) 6,000‐gallon gasoline USTs and (1) 8,000‐gallon
gasoline UST
4. Information about Monitoring Report
Date(s) of Assessment/Monitoring Event(s): June 8, 2021
5. Certification
I, Elizabeth A. Allyn, a Licensed Geologist for
WithersRavenel, do certify that the information
contained in this report is correct and accurate to
the best of my knowledge.
WithersRavenel, is licensed to practice
geology/engineering in North Carolina.
The certification numbers are C‐293 (Geology) and
C‐0451 (Engineering).
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Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report July 2021
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SECTION B. EXECUTIVE SUMMARY
1. Summary of Activities Associated with Current TA
WithersRavenel, Inc. (WR) conducted a receptor survey and groundwater sampling event at the
Save More #045 site located at 1424 N. Fayetteville Street in Asheboro, Randolph County, North
Carolina in association with TA‐01 under NCDEQ Contract #N122019B. The scope of work for
this project included conducting a receptor survey and sampling the monitoring wells associated
with the site.
2. Soil, Groundwater and LNAPL Assessment Information
Soils
No soil samples were obtained in association with the monitoring activities conducted by WR
during the June 2021 event. In April 2003, Engineering Consulting Services, Inc. (ECS) supervised
the removal of two 6,000‐gallon and one 8,000‐gallon gasoline USTs from the site. Tank closure
soil sampling indicated petroleum contaminants in excess of the Soil‐to‐Groundwater Maximum
Soil Contaminant Concentrations (MSCCs), but below the Industrial/Commercial MSCCs.
Groundwater
WR collected groundwater samples from site monitoring wells MW‐1, MW‐3 through MW‐8, and
VEW‐1 on June 8, 2021. The collected groundwater samples were submitted for laboratory
analysis of VOCs by SM6200B plus oxygenates. Analytical results for the groundwater samples
collected on June 8, 2021, revealed the following:
Monitoring wells MW‐1, MW‐3, and MW‐7 contained benzene above the GCLs.
Monitoring wells MW‐1 and MW‐7 contained MTBE above the GCLs.
Monitoring wells MW‐1, MW‐3, MW‐7, and VEW‐1 contained several petroleum
compounds above the 2L Standards.
Tert‐Amyl Methyl Ether (TAME) was detected above the 2L Standards in monitoring wells
MW‐1, MW‐3, MW‐7, and VEW‐1.
Light Non‐Aqueous Phase Liquid
Light non‐aqueous phase liquid (LNAPL) was detected in monitoring well MW‐1 in January 2015
at a thickness of 0.10 feet.
3. Receptor Information
As part of TA‐01, WR performed a receptor survey which revealed the following:
No evidence of water supply wells was identified by WR within 1,000 feet of the source area.
WR inquired with the City of Asheboro Utility Department to obtain information regarding the
connection status of the properties within 1,000 ft of the site. The occupied parcels within
1,000 feet of the source area are connected to the municipal water supply.
Although subsurface utilities were identified in the site vicinity, the shallowest observed depth
to water at the site is approximately 20 feet below ground surface. Therefore, these utilities
are not expected to be conduits for contamination.
No additional receptors (streams or wetlands) were identified within 500‐ft of the source area.
WithersRavenel
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Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report July 2021
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The site was not determined to be in a Wellhead Protection (WHP) area.
4. Remediation Activities
Based on WR’s review of historical files available for the site, the following remedial activities have
been completed at the location:
Absorbent booms were installed in monitoring well MW‐1 in May 2015.
An Aggressive Fluid Vapor Recovery (AFVR) event was conducted using monitoring well MW‐
1 in January 2019 and recovered approximately 226 gallons of petroleum‐impacted
groundwater.
Based on currently available information, WR is unaware of additional remedial actions that have
been performed at the site.
5. Recommendations
Based on the results of assessment and monitoring activities conducted at the site in association
with this TA, WR recommends the following:
WR recommends performing an AFVR event combined with air sparging utilizing
monitoring wells MW‐1, MW‐3, MW‐7, and VEW‐1 to reduce contaminant concentrations
at the site.
Installation of a monitoring well to the southeast of the source area on the adjacent parcel
to the south across Rainbow Drive.
Annual sampling of the site monitoring wells.
SECTION C. SITE HISTORY AND CHARACTERIZATION
The following information summarizes the site history and characterization.
1. UST Information
Two 6,000‐gallon gasoline USTs and one 8,000‐gallon gasoline UST and associated product lines
and dispensers were removed from the site in April 2003 during site renovations. These USTs
were registered as JP Asheboro, Facility ID 00‐0‐0000018414. Current USTs at the site include
one 20,000‐gallon compartmentalized UST (14,000‐gallon gasoline and 6,000‐gallon gasoline
UST) and one 4,000‐gallon kerosene UST. No documentation of over‐excavation was identified
during the file review. Figure 1 depicts the site location on the Asheboro, NC USGS Topographic
Map. Figure 2 shows the location of the historical UST system.
Historical and current UST information is provided in Table B‐1. Photographs of site conditions
observed during the June 2021 sampling event are included in Appendix A.
2. Description of Release/General Assessment History
The following summary of the assessment history is based on WR’s review of historical files for
the subject incident:
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According to the December 17, 2019 Groundwater Monitoring Report prepared by ECS, gasoline
was discovered in the pit of one of the USTs located onsite on November 16, 1995. According to
the Report of Initial Response, Abatement Measures, Site Check and Initial Site Characterization,
submitted by LAW Engineering and Environmental Services, Inc. on January 19, 1996,
approximately 126 gallons of gasoline and impacted water were removed from the “pump pit” and
the UST pump was replaced. In January 1996, soil samples were collected around the UST system.
The soil sample collected from soil boring SB‐1 at a depth of approximately 13.5 to 15 feet below
ground surface (ft bgs) exhibited Total Petroleum Hydrocarbons Gasoline Range Organics (TPH‐
GRO) at a concentration of 2,000 milligrams per kilograms (mg/kg). The remaining soil samples
collected either contained concentrations of TPH‐GRO less that than the current NCDEQ Action
Level of 100 mg/kg or were not detected above the laboratory method reporting limit.
In 1998, a Phase I Limited Site Assessment (LSA) was performed at the site. Soil borings were
advanced, and a receptor survey was conducted. Laboratory analysis of the soil samples collected
indicated p‐isopropyltoluene and naphthalene at concentrations greater than the Soil‐to‐
Groundwater Maximum Soil Contaminant Concentrations (MSCCs), but less than the Residential
MSCCs. The receptor survey indicated that there were no water supply wells within 1,500 feet of
the site. No groundwater samples were collected during this Phase I LSA. According to the Phase
I LSA report, fractured bedrock was encountered at depths ranging from 10 to 15 ft bgs.
In April 2003, the former UST system (two 6,000‐gallon gasoline USTs, one 8,000‐gallon gasoline
UST, product lines, and dispensers) was removed from the site due to renovations. Soil samples
were collected during UST removal and soil analytical results indicated petroleum hydrocarbons
at concentrations greater than the Soil‐to‐Groundwater MSCCs, but below the residential MSCCs.
Replacement USTs including one 20,000‐gallon compartmentalized gasoline UST and one 4,000‐
gallon kerosene UST were installed on the site. No soil was removed from the site during the UST
closure activities.
ECS submitted a Report of Limited Site Assessments – Phases I and II on December 18, 2003.
Monitoring wells MW‐1 through MW‐6 and VEW‐1 were installed at the site and sampled.
Multiple targeted constituents were detected in the groundwater samples at concentrations
greater than their respective North Carolina 2L Groundwater Quality Standards (NC2LGWQS) and
Gross Contamination Levels (GCLs). An updated receptor survey indicated that there were no
water supply wells within 1,500 feet of the site.
On June 16, 2004, ECS submitted a Report of Comprehensive Site Assessment (CSA) – Petroleum‐
Impacted Soils. During the CSA a total of twenty soil borings were advanced to collect soil
samples. Soil analytical results indicated petroleum hydrocarbons at concentrations greater than
the Soil‐to‐Groundwater MSCCs, but less than the Residential MSCC.
Groundwater sampling events were performed in March 2009, January 2015, May 2016, July
2018, and October 2019. Multiple targeted constituents were detected in the groundwater
samples at concentrations greater than the NC2LGWQS and GCLs. Reportedly, 0.10 feet of liquid
non‐aqueous phase liquids (LNAPL) was measured in monitoring well MW‐1 during the sampling
event in January 2015. In May 2015, ATC supervised the installation of monitoring well MW‐7 in
order to delineate the groundwater impacted above the GCLs; however, concentrations in MW‐7
exceeded the GCL. In February 2016, ATC supervised the installation of monitoring well MW‐8
located off‐site across Rainbow Drive. This well has not shown concentrations exceeding the
laboratory reporting limits with the exception of acetone detected during one sampling event.
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Annual Monitoring Report July 2021
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On January 8, 2019, ECS conducted an AFVR event at the site, utilizing monitoring well MW‐1 as
an extraction point. Approximately 226 gallons of liquid was removed during the AFVR event. In
addition, Zebra calculated approximately 0.0001 gallons of volatile organic vapors were removed
during the AFVR event.
3. Brief Description of Site Characteristics
The property is located in a commercial and residential area of Asheboro, Randolph County, North
Carolina (Figure 1). The property is currently occupied by the Save More gas station (see Figure
2). The Randolph County Geographic Information System (GIS) website identifies the subject
property as parcel identification number 7762022630 and is approximately 0.82 acres.
4. Information on Receptors/Potential Receptors
During the June 2021 receptor survey, no evidence of water supply wells was identified by WR.
Although subsurface utilities were identified in the site vicinity, the shallowest observed depth to
water at the site is approximately 20 feet below ground surface. Therefore, these utilities are not
expected to be conduits for contamination. No additional receptors (streams or wetlands) were
identified within 1,000‐ft of the source area.
5. Regional and Site Geology and Hydrology
The Geologic Map of North Carolina depicts the site in the as being in the Carolina Slate Belt of
the Piedmont Physiographic Province. The site underlain by the Uwharrie Formation which
consists of light gray to greenish gray metamorphosed dacitic to rhyolitic flows and tuffs,
interbedded with mafic and intermediate metavolcanic rock, metargillite, and metamudstone of
the Cambrian to Late Proterozoic.
According to the United States Department of Agricultural (USDA) Natural Resources
Conservation Service (NRCS) Web Soil Survey, the source area is underlain by Georgeville‐Urban
land complex (2 to 10 percent slopes). The Georgeville‐Urban land complex is well drained, found
on summits and shoulders, and the parent material is residuum weathered from metavolcanics
and/or argillite. Silty clay was encountered to depths ranging from 1 to 10 feet bgs, underlain by
silty sand, followed by silt. According to the Phase I LSA report, fractured bedrock was
encountered at depths ranging from 10 to 15 ft bgs.
SECTION D. RECEPTOR SURVEY
On June 8, 2021, WR personnel mobilized to the subject site to perform a site reconnaissance and
receptor survey in association with the current TA. Activities included those more thoroughly
described below:
1 Site Reconnaissance
The site is currently an active gas station located at the northeast corner of North Fayetteville
Street and Rainbow Drive inside the corporate limits of Asheboro, Randolph County. The site is
located in a residential and commercial area. The adjacent property to the north is a vacant
WithersRavenel
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Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report July 2021
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residence. The adjacent property to the south across Rainbow Drive is a shopping center. Carter
Bank & Trust is located across North Fayetteville Street to the west. A vacant wooded parcel is
east‐adjacent to the site. The site is shown on Figure 2, including site features, structures and the
locations of the former and current UST systems included in Table B‐1. The site and adjoining
parcels are depicted on Figure 3, and adjacent property information included in Table B‐5C.
The site is zoned by the City of Asheboro as “General Commercial” (B‐2), “is intended to serve the
convenience goods, shoppers’ goods, retail, and service needs of the motoring public, both local
and transient”.
WR examined the U.S. Geological Survey 7.5‐minute series topographic map for the site (Figure
1) and the surface contours for the location indicate the site has an approximate elevation of 800‐
ft above mean sea level (AMSL), in a hilly area.
As determined using the June 2021 water table elevations, groundwater flow through the site is
to the south and southeast.
2 Receptor Survey
As part of TA‐01, WR performed a receptor survey:
No evidence of water supply wells was identified by WR within 1,000 feet of the source area.
WR inquired with the City of Asheboro Utility Department to obtain information regarding the
connection status of the properties within 1,000 ft of the site. The occupied parcels within
1,000 feet of the source area are connected to the municipal water supply.
Although subsurface utilities were identified in the site vicinity, the shallowest observed depth
to water at the site is approximately 20 feet below ground surface. Therefore, these utilities
are not expected to be conduits for contamination.
No additional receptors (streams or wetlands) were identified within 500‐ft of the source area.
An unnamed tributary of Hasketts Creek was identified approximately 600 feet west of the
site.
The site was not determined to be in a WHP area.
Returned water supply well forms are included in Appendix B. Information regarding municipal
water connections from the City of Asheboro Utilities Department (buffered parcels within 1,000
ft of the Save More #045 site) is also included in Appendix B.
SECTION E. GROUNDWATER SAMPLING – JUNE 2021
On June 8, 2021, WR personnel mobilized to the subject property to perform limited groundwater
sampling activities at the facility in association with TA‐01 under NCDEQ Contract # N122019B.
The scope of work for this project included gauging, purging, and sampling of monitoring wells
MW‐1 through MW‐8 and VEW‐1.
In the performance of assessment activities at the site, WR was able to gauge and sample
monitoring wells MW‐1, MW‐3 through MW‐8, and VEW‐1. Monitoring well MW‐2 has been
destroyed.
WithersRavenel
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Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report July 2021
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The following paragraphs describe the sampling activities and associated laboratory analytical
results.
Groundwater Sampling Activities
Prior to the purging and sampling of site monitoring wells as described below, WR personnel
gauged the wells with an electronic oil‐water interface meter to determine the depth to
groundwater at each well location. During the performance of these activities, LNAPL was not
identified in the site monitoring wells.
The depth to groundwater measurements in the monitoring wells across the site ranged from
17.51 feet below the top of casing (ft‐BTOC) in monitoring well MW‐6 to 20.42 ft‐BTOC in
monitoring well MW‐8. Based on groundwater elevation measurements on June 8, 2021, the
direction of groundwater flow is generally towards the south and southeast. Groundwater flow as
determined based on these measurements is shown on Figure 5. Groundwater elevation
measurements for this event are presented in Table B‐7.
Following gauging, the monitoring wells were purged and sampled with separate, disposable
polyethylene (PE) bailers for each well. Samples from the wells were decanted into pre‐preserved
laboratory provided sample containers. Samples collected from site monitoring wells were
submitted to Waypoint for testing by Standard Method (SM) 6200B plus oxygenates.
Laboratory Results
Analytical results for the groundwater samples collected on June 8, 2021, revealed the following:
Monitoring wells MW‐1, MW‐3, and MW‐7 contained benzene above the GCLs.
Monitoring wells MW‐1 and MW‐7 contained MTBE above the GCLs.
Monitoring wells MW‐1, MW‐3, MW‐7, and VEW‐1 contained several petroleum
compounds above the 2L Standards.
Tert‐Amyl Methyl Ether (TAME) was detected above the 2L Standards in monitoring wells
MW‐1, MW‐3, MW‐7, and VEW‐1.
These results are shown on Figure 6 and included in Table B‐4. Copies of the laboratory analytical
report and chain‐of‐custody are included in Appendix C. WR’s generalized standard operating
procedures are provided in Appendix D.
SECTION F. CONCLUSIONS AND RECOMMENDATIONS
This report documents the results of field activities conducted at the site for TA‐01, which included
conducting a receptor survey and sampling the monitoring wells associated with the site.
Conclusions based on observations, analytical data and research relating to the release at the site
combined with historical information include the following:
The site is currently operating as the Save More gas station and three USTs (two gasoline
and one kerosene) are in use at the site.
Municipal water is available to the site and surrounding area. Water supply wells were not
identified within 1,000 feet of the site.
Monitoring wells MW‐1, MW‐3 through MW‐8, and VEW‐1 were located, gauged, and
sampled. Monitoring well MW‐2 has been destroyed.
LNAPL was not identified in the gauged monitoring wells.
WithersRavenel
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Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report July 2021
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Monitoring wells MW‐1, MW‐3, and MW‐7 contained benzene above the GCLs.
Monitoring wells MW‐1 and MW‐7 contained MTBE above the GCLs.
Monitoring wells MW‐1, MW‐3, MW‐7, and VEW‐1 contained several petroleum
compounds above the 2L Standards.
Tert‐Amyl Methyl Ether (TAME) was detected above the 2L Standards in monitoring wells
MW‐1, MW‐3, MW‐7, and VEW‐1.
The groundwater elevation data indicated a south and southeasterly groundwater flow
direction.
Closure goals for the site are Industrial/Commercial MSCCs and GCLs.
Based on the results of assessment and monitoring activities conducted at the site in association
with this TA, WR recommends the following:
WR recommends performing an AFVR event combined with air sparging utilizing
monitoring wells MW‐1, MW‐3, MW‐7, and VEW‐1 to reduce contaminant concentrations
at the site.
Installation of a monitoring well to the southeast of the source area on the adjacent parcel
to the south across Rainbow Drive.
Annual sampling of the site monitoring wells.
WithersRavenel
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FIGURES
EAA
LRE
DRAWN BY:
7/8/21 02172214.24
1
SUBJECT SITE
±0.82 ACRES
SCALE:FIGURE NO.:
PROJECT NO.:DATE:APPROVED BY:
SAVE MORE #045 - NCDEQ INC. 15046
1424 N. FAYETTEVILLE STREET
ASHEBORO, RANDOLPH, COUNTY, NC
GENERAL LOCATION MAP
1"=1000 '
GRAPHIC SCALE
1 inch = 1000 ft.
0 1000500 2000
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500'
1,000'
1,500'
MW-8
MW-7
MW-3 MW-1
VEW-1
MW-4
MW-5
MW-6MW-2
(DESTROYED)
FORMER UST SYSTEM
CURRENT UST SYSTEM
N. FAYETTEVILLE STREETRAINBOW DRIVE
LEGEND
TYPE II MONITORING WELL LOCATION
TYPE III MONITORING WELL LOCATION
NOTES:
1.) AERIAL OBTAINED FROM THE LOCAL COUNTY GIS DEPARTMENT.1 inch = 40 ft.
4020 80
GRAPHIC SCALE
0
EAA
LRE
DRAWN BY:
1"=40 '
07/07/21 02172214.24
2
SCALE:FIGURE NO.:
PROJECT NO.:DATE:APPROVED BY:
SAVE MORE #045 - NCDEQ INC. 15046
1424 N. FAYETTEVILLE STREET
ASHEBORO, RANDOLPH, COUNTY, NC
SITE MAP
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www.withersravenel.com
MW-8
MW-7
MW-3 MW-1
VEW-1
MW-4
MW-5
MW-6MW-2
2
3
1
4SITE
4
EAA
DV
DRAWN BY:
1"=80 '
07/07/21 02172214.24
3
SCALE:FIGURE NO.:
PROJECT NO.:DATE:APPROVED BY:
SAVE MORE #045 - NCDEQ INC. 15046
1424 N. FAYETTEVILLE STREET
ASHEBORO, RANDOLPH, COUNTY, NC
SITE MAP WITH ADJACENT PARCELS SHOWN
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LEGEND
MONITORING WELL LOCATION
PROPERTY IDENTIFICATION (REFER TO
TABLE B-5C)
NOTES:
1.) AERIAL OBTAINED FROM THE LOCAL COUNTY GIS DEPARTMENT.1 inch = 80 ft.
8040 160
GRAPHIC SCALE
04
VALLEY ROAD
N. FAYETTEVILLE STREETRAINBOW DRIVE
WOODBERRY STREET
MW-8
MW-7
MW-3 MW-1
VEW-1
MW-4
MW-5
MW-6MW-2
(81.56)
(DESTROYED)
(82.51)
(81.14)
(80.90)
(82.26)
(81.71)
(80.69)
(79.45)
82.5
80.5
81.5
82.0
81.0
80.0
79.5
FORMER UST SYSTEM
CURRENT UST SYSTEM
N. FAYETTEVILLE STREETRAINBOW DRIVE
LEGEND
TYPE II MONITORING WELL LOCATION
TYPE III MONITORING WELL LOCATION
GROUNDWATER ELEVATION (FT.)
GROUNDWATER ELEVATION CONTOUR -
DASHED WHERE INFERRED
GROUNDWATER FLOW DIRECTION
NOTES:
1.) AERIAL OBTAINED FROM THE LOCAL COUNTY GIS DEPARTMENT.
2.) VEW-1 AND MW-7 NOT USED TO CONSTRUCT CONTOURS 1 inch = 40 ft.
4020 80
GRAPHIC SCALE
0
EAA
DV
DRAWN BY:
1"=40 '
07/07/21 02172214.24
4
SCALE:FIGURE NO.:
PROJECT NO.:DATE:APPROVED BY:
SAVE MORE #045 - NCDEQ INC. 15046
1424 N. FAYETTEVILLE STREET
ASHEBORO, RANDOLPH, COUNTY, NC
GROUNDWATER ELEVATION CONTOUR
MAP - JUNE 2021
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(81.71)
MW-8
MW-7
MW-3
MW-4
MW-5
MW-6MW-2
(DESTROYED)
LEGEND
TYPE II MONITORING WELL LOCATION
TYPE III MONITORING WELL LOCATION
NOTES:
1.) AERIAL OBTAINED FROM THE LOCAL COUNTY GIS DEPARTMENT.1 inch = 60 ft.
6030 120
GRAPHIC SCALE
0
EAA
LRE
DRAWN BY:
1"=60 '
07/07/21 02172214.24
5
SCALE:FIGURE NO.:
PROJECT NO.:DATE:APPROVED BY:
SAVE MORE #045 - NCDEQ INC. 15046
1424 N. FAYETTEVILLE STREET
ASHEBORO, RANDOLPH, COUNTY, NC
GROUNDWATER ANALYTICAL RESULTS MAP
JUNE 2021
WithersRavenel
Engineers | Planners | Surveyors
115 MacKenan Drive | Cary, NC 27511 | t: 919.469.3340 | license #: C-0832
www.withersravenel.com
MW-1MW-3
VEW-1
RAINBOW DRIVE
MW-1N. FAYETTEVILLE STREET
MW-8
MW-7
MW-3 MW-1
VEW-1
MW-4
MW-5
MW-6MW-2
(DESTROYED)
(29,100)
(<0.500)
(<0.500)
(<0.500)
(9,750)
(6,980)
(<50.0)
(<0.500)(5,000)FORMER UST SYSTEM
CURRENT UST SYSTEM
N. FAYETTEVILLE STREETRAINBOW DRIVE
LEGEND
TYPE II MONITORING WELL LOCATION
TYPE III MONITORING WELL LOCATION
DISSOLVED BENZENE CONCENTRATION (UG/L)
DISSOLVED BENZENE ISOCONCENTRATION
CONTOUR - DASHED WHERE INFERRED
NOTES:
1.) AERIAL OBTAINED FROM THE LOCAL COUNTY GIS DEPARTMENT.
2.) VEW-1 NOT USED TO CONSTRUCT CONTOURS 1 inch = 40 ft.
4020 80
GRAPHIC SCALE
0
EAA
LRE
DRAWN BY:
1"=40 '
07/07/21 02172214.24
6
SCALE:FIGURE NO.:
PROJECT NO.:DATE:APPROVED BY:
SAVE MORE #045 - NCDEQ INC. 15046
1424 N. FAYETTEVILLE STREET
ASHEBORO, RANDOLPH, COUNTY, NC
GROUNDWATER BENZENE ISOCONCENTRATION
MAP - JUNE 2021
WithersRavenel
Engineers | Planners | Surveyors
115 MacKenan Drive | Cary, NC 27511 | t: 919.469.3340 | license #: C-0832
www.withersravenel.com
(6,980)
WithersRavenel
Our People. Your Success.
TABLES
UST IDNumberCapacity(in gallons)ConstructionDetailsTankDimensions (diameter x length)Description ofAssociatedPiping & PumpsDate of TankInstallationStatus ofUSTWas release associated with UST System? (Y/N)1 8,000 Single Wall Steel Unknown Single Wall FRP 5/3/1972Permanently Closed By Removal (4/14/2003)Y2 6,000 Single Wall Steel Unknown Single Wall FRP 5/3/1972Permanently Closed By Removal (4/14/2003)Y3 6,000 Single Wall Steel Unknown Single Wall FRP 5/3/1972Permanently Closed By Removal (4/14/2003)YA1A 14,000 Single Wall FRPUnknown Single Wall FRP4/1/2003 Current UnknownA1B 6,000 Single Wall FRPUnknown Single Wall FRP4/1/2003 Current UnknownA2 4,000 Single Wall FRP Unknown Single Wall FRP 3/14/2003 Current UnknownAST IDNumberCapacity(in gallons)ConstructionDetailsTankDimensions (diameter x length) (ft)Description ofAssociatedPiping & PumpsDate of TankInstallationStatus ofASTWas release associated with AST System? (Y/N)IncidentNumberMaterialReleasedDateofRelease15046 GasolineDiscovered November 1995Notes:1) UST Information obtained from the NCDEQ Tank Database.Table B-1Site History: UST/AST System & Other Release InformationSave More #045According to the Comprehensive Site Assessment prepared by ECS and dated June 16, 2004, impacts exceeding the Soil-to-Groundwater MSCCs were identified in the samples collected during the tank closure activities. In the December 17, 2019 Groundwater Monitoring Report prepared by ECS, reference was made to samples collected as part of a UST pit investigation performed in November 1995 which identified concentrations exceeding the NCDEQ Action Level for TPH-GRO. A copy of the report documenting the November 1995 sampling activities was not available for review.1424 N. Fayetteville StreetAsheboro, Randolph County, North CarolinaDescription of ReleaseIncident # 15046Current/LastContentsCurrent/LastContentsGasolineKeroseneGasolineGasolineGasolineGasolinePage 1 of 1
Benzene Bromobenzene Butylbenzene, n‐ Butylbenzene, sec‐ Chlorobenzene Dichlorobenzene, 1,4‐ Ethylbenzene Isopropyl Ether Isopropylbenzene (Cumene) Methyl‐tert‐Butyl Ether Naphthalene Propylbenzene, n‐tert‐Amyl alcohol (TAA)tert‐Amyl Methyl Ether (TAME)tert‐Butyl Alcohol (TBA)Ethyl Tertiary Butyl Ether (ETBE)tert‐Butyl formate (TBF)Toluene Trimethylbenzene, 1,2,4‐ Trimethylbenzene, 1,3,5‐Xylenes, m,p‐ Xylene, o‐Xylenes, total 71‐43‐2 108‐86‐1 104‐51‐8 135‐98‐8 108‐90‐7 106‐46‐7 100‐41‐4 108‐20‐398‐82‐81634‐04‐491‐20‐3 103‐65‐175‐85‐4 994‐05‐875‐65‐0 637‐92‐3 762‐75‐4108‐88‐395‐63‐6 108‐67‐8108‐38‐3/ 106‐42‐395‐47‐61330‐20‐7MW‐1 6/8/202129,100<500 <500 <500 <500 <5003,470 762<50087,6001,160<500 <1000031,900<10000<10000<100007,550 3,450 971 7,070 2,350 9,420MW‐3 <0.5006,980<50.0 <50.0 <50.0 <50.0 <50.01,580 99.4 80.8 9,120 476 216<10001,560<1000 <1000 <1000773 1,010 183 3,230 74.9 3,300MW‐4 6/8/2021 <0.500 <0.5000.664 0.719 2.26 1.87<0.500 <0.5001.39<1.00 <1.000.569<10.0 <10.0 <10.0 <10.0 <10.0 <0.500 <0.500 <0.500 <1.00 <0.500 <0.500MW‐5 6/8/2021 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <1.00 <1.00 <0.500 <10.0 <10.0 <10.0 <10.0 <10.0 <0.500 <0.500 <0.500 <1.00<0.500 <0.500MW‐6 6/8/2021 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.5002.76<0.5001.08<1.00 <0.500 <10.0 <10.0 <10.0 <10.0 <10.0 <0.500 <0.500 <0.500 <1.00 <0.500 <0.500MW‐7 6/8/20219,750<50.0 <50.0 <50.0 <50.0 <50.0721 299<50.048,600492130 <10005,750<1000 <1000 <1000360 890 188 1,470<50.01,470MW‐8 6/8/2021 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <1.00 <1.00 <0.500 <10.0 <10.0 <10.0 <10.0 <10.0 <0.500 <0.500 <0.500 <1.00<0.500 <0.500VEW‐1 6/8/2021 <50.0 <50.0 <50.0 <50.0 <50.0 <50.0 <50.0 <50.0 <50.06,690<100 <50.0 <10001,320<1000 <1000 <1000 <50.0 <50.0 <50.0 <100 <50.0 <50.0Field Blank 6/8/2021 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <0.500 <1.00 <1.00 <0.500 <10.0 <10.0 <10.0 <10.0 <10.0 <0.500 <0.500 <0.500 <1.00 <0.500 <0.5001 NL 70 70 50 6 600 70 70 20 6 70 40 128 10 47 40 600 400 400500 500 5005,000 NL 5,900 8,800 50,000 405 80,000 70,000 30,500 20,000 6,000 26,100 40,000 128,000 10,000 47,000 40,000 260,000 28,500 24,100 50,000 50,000 50,000Notes:1)2)3)4)NRNABDLNLResultResultResultAsheboro, Randolph County, North CarolinaTABLE B‐4SUMMARY OF CURRENT GROUNDWATER ANALYTICAL RESULTSSave More #045Incident # 150461424 N. Fayetteville StreetGCLs for Groundwater = NCDEQ UST Section Gross Contamination Levels for Groundwater.Analytical MethodSample IDDateCollectedNC 2L Standard GCLs for GroundwaterAll results provided in ug/L (micrograms per liter) or parts per billion.Compounds analyzed for by laboratory but not listed were not detected above laboratory detection limits. See the laboratory report included in the Appendix for a full list of constituents. NC 2L Standard ‐ North Carolina Groundwater Quality Standard as per NC Administrative Code 15A NCAC 02L.SM6200B= Result Exceeds NC Gross Contaminant Level for Groundwater= Not Reported= Not Analyzed by Method Shown= Beneath Detection Limit (No Compounds Detected at Concentrations Above Laboratory Method Detection Limit).= No Regulatory Level Established= Result Exceeds Laboratory Detection Limits= Result Exceeds NC 2L Standard for Groundwater
SM6200BAcetone Benzene Butylbenzene, n‐Butylbenzene, sec‐ Dichlorobenzene, 1,4‐ Ethylbenzene Isopropyl Ether Isopropylbenzene (Cumene) Methyl‐tert‐Butyl Ether MIBK (4‐Methyl‐2‐pentanone) Naphthalene Propylbenzene, n‐tert‐Amyl Methyl Ether (TAME)tert‐Butyl Alcohol (TBA)Toluene Trimethylbenzene, 1,2,4‐ Trimethylbenzene, 1,3,5‐Xylenes, total 67‐64‐171‐43‐2 104‐51‐8 135‐98‐8 106‐46‐7 100‐41‐4 108‐20‐398‐82‐8 1634‐04‐4 108‐10‐191‐20‐3 103‐65‐1994‐05‐875‐65‐0108‐88‐395‐63‐6 108‐67‐81330‐20‐710/03/03‐‐‐9,400110‐‐‐ ‐‐‐1,100‐‐‐61140,000‐‐‐600 160‐‐‐ ‐‐‐970 540 160 1,64003/22/09‐‐‐12,400BQL‐‐‐ ‐‐‐1,430‐‐‐BQL226,000‐‐‐490BQL‐‐‐ ‐‐‐1,010 1,000 280 2,78001/20/1505/24/16‐‐‐20,00084‐‐‐2,700<1893170,000‐‐‐930 290‐‐‐‐‐‐3,800 2,900 750 8,40007/08/18<0.524,000<0.5<0.5 <2502,800 820<0.5170,000700 1,600 320‐‐‐‐‐‐5,200 4,000 1,000 11,00010/02/19NA14,100<250<250 <2502,020 392<25081,800NA1,060<25017,700<5,0002,820 2,850<2505,7606/8/2021 <1000029,100<500 <500 <5003,470 762<50087,600<10001,160<50031,900<100007,550 3,450 971 9,42010/03/03‐‐‐BQLBQL‐‐‐ ‐‐‐BQLND BQLBQL‐‐‐BQL BQL‐‐‐ ‐‐‐BQLBQL BQLBQL03/22/09‐‐‐BQLBQL‐‐‐ ‐‐‐BQL‐‐BQLBQL‐‐‐BQL BQL‐‐‐ ‐‐‐BQLBQL BQLBQL01/20/15‐‐‐<0.079 <0.054‐‐‐ ‐‐‐<0.092 <0.18 <0.11 <0.090‐‐‐<0.12 <0.094‐‐‐‐‐‐<0.09 <0.18 <0.01 <0.1805/24/16‐‐‐<0.12 <0.15‐‐‐ ‐‐‐<0.13 <0.18 <0.12 <0.090‐‐‐<0.12 <0.13‐‐‐‐‐‐<0.17 <0.18 <0.13 <0.2507/08/1810<0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5‐‐‐‐‐‐<0.5 <0.5 <0.5 <0.56/8/202111/17/2003‐‐‐3,900BQL‐‐‐ ‐‐‐BQL ND BQL62,000‐‐‐BQL BQL‐‐‐ ‐‐‐1,300BQL BQL5903/22/2009‐‐‐3,960BQL‐‐‐ ‐‐‐BQL‐‐BQL35,000‐‐‐BQL BQL‐‐‐ ‐‐‐1,030BQL BQL9101/20/2015‐‐‐14,000<5.4‐‐‐ ‐‐‐2,600 160 74 19,000‐‐‐760 200‐‐‐‐‐‐1,400 1,000 230 5,3505/24/2016‐‐‐9,500<30‐‐‐ ‐‐‐2,100<3672 J8,900‐‐‐450 180‐‐‐ ‐‐‐2,800 970 250 5,4507/8/2018 <2512,000<25 <25 <252,300 130 70 13,00032 J480 200‐‐‐ ‐‐‐1,900 650 120 4,00010/2/2019 NA8,670<50.0 <50.0 <50.01,830 82 60 10,100NA423 176 1,670<1,000713 584<50.02,8746/8/2021 <10006,980<50.0 <50.0 <50.01,58099.4 80.8 9,120<100476 216 1,560<1000773 1,0101833,30011/17/2003‐‐‐36BQL‐‐‐ ‐‐‐4.1ND BQL BQL‐‐‐10 1‐‐‐‐‐‐37.0 22 7.6 823/22/2009‐‐‐183 4.8‐‐‐ ‐‐‐28.5‐‐11.3BQL‐‐‐72 21‐‐‐‐‐‐30.6 134 36.6 14601/20/15‐‐‐73.7‐‐‐ ‐‐‐2.3<0.183.7<0.090‐‐‐13 4.4‐‐‐‐‐‐0.5 1.6 0.71.75 J05/24/16‐‐‐4.0 4.6‐‐‐ ‐‐‐4.4<0.184.6<0.090‐‐‐8.5 7.2‐‐‐ ‐‐‐0.47 J1.7 1.1 1.3907/08/1814 0.53 0.58 0.56<0.50.58<0.51.20.80 J<0.52.4 1.1‐‐‐ ‐‐‐<0.5 <0.5 <0.5 <0.510/02/19 NA <0.500.56<0.50 <0.50 <0.50 <0.500.95 4.9NA <2.00.55<100 <10.0 <0.50 <0.50 <0.50 <1.06/8/2021 <10.0 <0.5000.6640.7191.87<0.500 <0.5001.39<1.00 <1.00 <1.000.569<10.0 <10.0 <0.500 <0.500 <0.500 <0.50011/17/2003‐‐‐9.3BQL‐‐‐ ‐‐‐BQL ND0.83 0.81‐‐‐41.2‐‐‐‐‐‐BQL BQL BQLBQL3/22/2009‐‐‐BQL BQL‐‐‐ ‐‐‐BQL‐‐BQL BQL‐‐‐BQL BQL‐‐‐‐‐‐BQL BQL BQLBQL01/20/15‐‐‐<0.079 <0.054‐‐‐ ‐‐‐<0.092 <0.18 <0.110.62‐‐‐<0.12 <0.094‐‐‐‐‐‐<0.09 <0.18 <0.01 <0.1805/24/16‐‐‐<0.12 <0.15‐‐‐ ‐‐‐<0.13 <0.18 <0.12 <0.090‐‐‐<0.12 <0.13‐‐‐‐‐‐<0.17 <0.18 <0.13 <0.2507/08/18 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.50.57 J<0.5 <0.5 <0.5‐‐‐‐‐‐<0.5 <0.5 <0.5 <0.56/8/2021 <10.0 <0.500 <0.500 <0.500 <0.500<0.500 <0.500 <0.500 <1.00 <1.00 <1.00 <0.500 <10.0 <10.0 <0.500 <0.500 <0.500 <0.5006,0001 70 70 6 600 70 70 20 100 6 70 128 10 600 400 4005006,000,000 5,000 5,900 8,800 405 80,000 70,000 30,500 20,000100,000 6,000 26,100 128,000 10,000 260,000 28,500 24,100 50,000Notes:1)2)3)4)5) Historical Groundwater data from Monitoring Report by S&ME, dated May 26, 2020. 6) NA = Not Available ResultResultResultIncident # 15046TABLE B‐4ASUMMARY OF HISTORICAL GROUNDWATER ANALYTICAL RESULTSSave More #0451424 N. Fayetteville StreetAsheboro, Randolph County, North CarolinaAnalytical MethodMW‐1MW‐2MW‐3MW‐4MW‐5Sample IDDateCollectedNC 2L Standard GCLs for Groundwater= Result Exceeds NC Gross Contaminant Level for GroundwaterCompounds analyzed for by laboratory but not listed were not detected above laboratory detection limits. See the laboratory report included in the Appendix for a full list of constituents. NC 2L Standard ‐ North Carolina Groundwater Quality Standard as per NC Administrative Code 15A NCAC 02L.GCLs for Groundwater = NCDEQ UST Section Gross Contamination Levels for Groundwater.NOT SAMPLED ‐ 0.10 FEET OF LNAPL PRESENTDestroyed= Result Exceeds Laboratory Detection Limits= Result Exceeds NC 2L Standard for GroundwaterAll results provided in ug/L (micrograms per liter) or parts per billion.Page 1 of 2
SM6200BAcetone Benzene Butylbenzene, n‐Butylbenzene, sec‐ Dichlorobenzene, 1,4‐ Ethylbenzene Isopropyl Ether Isopropylbenzene (Cumene) Methyl‐tert‐Butyl Ether MIBK (4‐Methyl‐2‐pentanone) Naphthalene Propylbenzene, n‐tert‐Amyl Methyl Ether (TAME)tert‐Butyl Alcohol (TBA)Toluene Trimethylbenzene, 1,2,4‐ Trimethylbenzene, 1,3,5‐Xylenes, total 67‐64‐171‐43‐2 104‐51‐8 135‐98‐8 106‐46‐7 100‐41‐4 108‐20‐398‐82‐8 1634‐04‐4 108‐10‐191‐20‐3 103‐65‐1994‐05‐875‐65‐0108‐88‐395‐63‐6 108‐67‐81330‐20‐7Incident # 15046TABLE B‐4ASUMMARY OF HISTORICAL GROUNDWATER ANALYTICAL RESULTSSave More #0451424 N. Fayetteville StreetAsheboro, Randolph County, North CarolinaAnalytical MethodSample IDDateCollected11/17/2003‐‐‐BQL BQL‐‐‐ ‐‐‐BQL ND BQL9.2‐‐‐BQL BQL‐‐‐‐‐‐BQL BQL BQL BQL3/22/2009‐‐‐BQL BQL‐‐‐ ‐‐‐BQL‐‐BQL BQL‐‐‐BQL BQL‐‐‐‐‐‐BQL BQL BQL BQL1/20/2015‐‐‐<0.079 <0.054‐‐‐ ‐‐‐<0.092 <0.18 <0.110.57‐‐‐<0.12 <0.094‐‐‐‐‐‐<0.09 <0.18 <0.01 <0.185/24/2016‐‐‐<0.12 <0.15‐‐‐ ‐‐‐<0.13 <0.18 <0.12 <0.090‐‐‐<0.12 <0.13‐‐‐‐‐‐<0.17 <0.18 <0.13 <0.257/8/201811<0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5‐‐‐‐‐‐<0.5 <0.5 <0.5 <0.56/8/2021 <10.0 <0.500 <0.500 <0.500 <0.500 <0.5002.76<0.5001.08<1.00 <1.00 <0.500 <10.0 <10.0 <0.500 <0.500 <0.500 <0.5005/17/2015‐‐‐22,00048 J‐‐‐ ‐‐‐2,400 64062 J80,000‐‐‐<24190‐‐‐ ‐‐‐24,000 2,200 460 11,7005/24/2016‐‐‐1,90023 J‐‐‐ ‐‐‐510<18 <126,600‐‐‐130 65‐‐‐ ‐‐‐2,800 540 170 2,4707/8/2018 <509,400<50 <50 <501,900 290 6750,000110 600 210‐‐‐ ‐‐‐8,000 1,800 470 8,70010/2/2019 NA7,600<125 <125 <1251,120 231<12541,200NA559<1254,240 3,740 3,000 1,170<1254,0606/8/2021 <10009,750<50.0 <50.0 <50.0721 299<50.048,600<100492 130 5,750<1000360 890 188 1,4701/20/2015‐‐‐<0.12 <0.15‐‐‐ ‐‐‐<0.13 <0.18 <0.18 <0.090‐‐‐<0.12 <0.13‐‐‐ ‐‐‐<0.17 <0.18 <0.13 <0.255/24/2016‐‐‐<0.12 <0.15‐‐‐ ‐‐‐<0.13 <0.18 <0.18 <0.090‐‐‐<0.12 <0.13‐‐‐ ‐‐‐<0.17 <0.18 <0.13 <0.257/8/201815<0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5‐‐‐ ‐‐‐<0.5 <0.5 <0.5 <0.56/8/2021 <10.0 <0.500 <0.500 <0.500 <0.500<0.500 <0.500 <0.500 <1.00 <1.00 <1.00 <0.500 <10.0 <10.0 <0.500 <0.500 <0.500 <0.50011/17/2003‐‐‐36.0BQL‐‐‐ ‐‐‐BQL160BQL26,000‐‐‐BQL BQL‐‐‐ ‐‐‐2.8BQL BQL BQL3/22/2009‐‐‐BQL BQL‐‐‐ ‐‐‐BQL‐‐BQL23,200‐‐‐BQL BQL‐‐‐ ‐‐‐BQL BQL BQL BQL1/20/2015‐‐‐<2 <1.4‐‐‐ ‐‐‐<2.313<2.83,900‐‐‐<3 <2.4‐‐‐ ‐‐‐<2.2 <2.4 <2.5 <4.55/24/2016‐‐‐<12 <15‐‐‐ ‐‐‐<13 <18 <1213,000‐‐‐<12 <13‐‐‐ ‐‐‐21 J<18 <13 <257/8/201812<0.5 <0.5 <0.5 <0.5 <0.560<0.513,000<0.5 <0.5 <0.5‐‐‐ ‐‐‐<0.5 <0.5 <0.5 <0.510/2/2019 NA <62.5 <62.5 <62.5 <62.5 <62.5109<62.523,000NA <250 <62.53,240<1250 <62.5 <62.5 <62.5 <187.56/8/2021 <1000 <50.0 <50.0 <50.0 <50.0 <50.0 <50.0 <50.06,690<100 <100 <50.0 1,320 <1000 <50.0 <50.0 <50.0 <50.06,0001 70 70 6 600 70 70 20 100 6 70 128 10 600 400 4005006,000,000 5,000 5,900 8,800 405 80,000 70,000 30,500 20,000100,000 6,000 26,100 128,000 10,000 260,000 28,500 24,100 50,000Notes:1)2)3)4)5) Historical Groundwater data from Monitoring Report by S&ME, dated May 26, 2020. 6) NA = Not Available ResultResultResult= Result Exceeds Laboratory Detection Limits= Result Exceeds NC 2L Standard for Groundwater= Result Exceeds NC Gross Contaminant Level for GroundwaterGCLs for Groundwater = NCDEQ UST Section Gross Contamination Levels for Groundwater.GCLs for GroundwaterAll results provided in ug/L (micrograms per liter) or parts per billion.Compounds analyzed for by laboratory but not listed were not detected above laboratory detection limits. See the laboratory report included in the Appendix for a full list of constituents. NC 2L Standard ‐ North Carolina Groundwater Quality Standard as per NC Administrative Code 15A NCAC 02L.MW‐6MW‐7MW‐8VEW‐1NC 2L Standard Page 2 of 2
1424 N. Fayetteville Street Rey Petroleum LLCAsheboro, NC 27203 300 Abbey CourtAlpharetta, GA 300041430 N. Fayetteville Street Ronald and Kathi SewellAsheboro, NC 27203 2504 Parks Crossroads Church RoadRamseur, NC 273161406 N. Fayetteville Street J & A CastlerockAsheboro, NC 27203 PO Box 1104Asheboro, NC 272041425 N. Fayetteville Street Carter Bank & TrustAsheboro, NC 27203 1300 Kings Mountain RoadMartinsville, VA 24112Doris Osborne511 W. Bailey StreetAsheboro, NC 27203 Asheboro, NC 272031)2)3)City of Asheboro Zoning Codes:Downgradient3Bank B‐2/R‐15 160 ft West Downgradient2Shopping Center B‐275 ft South1Vacant Residence B‐2/R‐10 125 ft North UpgradientLocation Relative to Groundwater FlowSITEGas Station B‐2‐‐‐ ‐‐‐Property ID Property Address Property Owner & Address Usage ZoningDistance/Direction from Source AreaAsheboro, Randolph County, North CarolinaTABLE B‐5CADJACENT PROPERTY INFORMATIONSave More #045Incident # 150461424 N. Fayetteville StreetB‐2 = General CommercialR‐10 = Medium Density ResidentialR‐15 = Low Density Single Family ResidentialR‐10/B‐2 110 ft EastDistances shown from source area are measured from location of monitoring well MW‐1 and the nearest property boundary of the adjacent property.Property owner information from the Randolph County GIS Service, data current as of July 1, 2021. See Figure 3 for corresponding map information.Notes: 4DowngradientUndevelopedUnaddressed Parcel along Valley Road
Well ID
Total Depth
(feet below
ground surface)
Top‐of‐Casing
Elevation (feet)
Date Water Level
Measured
Depth‐to‐LNAPL
(feet)
Depth‐to‐Water
Uncorrected
(feet)
LNAPL Thickness
(feet)
Groundwater
Surface
Elevation (feet)
11/17/03 NM 20.45 NA 79.55
03/24/09 NM 23.53 NA 76.47
01/20/15 22.91 23.01 0.10 77.08
05/24/16 NM 19.25 NA 80.75
07/06/18 NM 21.46 NA 78.54
01/08/19 NM 18.74 NA 81.26
10/02/19 NM 20.74 NA 79.26
6/8/2021 NM 18.44 NM 81.56
11/17/03 NM 18.58 NM 81.15
03/24/09 NM 21.14 NM 78.59
01/20/15 NM 21.32 NM 78.41
05/24/16 NM 16.85 NM 82.88
07/06/18 NM 21.24 NM 78.49
6/8/2021
11/17/03 NM 20.36 NM 79.76
03/24/09 NM 23.21 NM 76.91
01/20/15 NM 22.92 NM 77.20
05/24/16 NM 18.78 NM 81.34
07/06/18 NM 19.48 NM 80.64
10/02/19 NM 20.73 NM 79.39
6/8/2021 NM 18.41 NM 81.71
11/17/03 NM 20.50 NM 78.49
03/24/09 NM 23.13 NM 75.86
01/20/15 NM 22.56 NM 76.43
05/24/16 NM 18.90 NM 80.09
07/06/18 NM 21.25 NM 77.74
10/02/19 NM 20.66 NM 78.33
6/8/2021 NM 18.09 NM 80.90
11/17/03 NM 18.52 NM 80.15
03/24/09 NM 21.59 NM 77.08
01/20/15 NM 18.91 NM 79.76
05/24/16 NM 15.57 NM 83.10
07/06/18 NM 18.86 NM 79.81
6/8/2021 NM 17.53 NM 81.14
11/17/03 NM 18.75 NM 81.27
03/24/09 NM 21.23 NM 78.79
01/20/15 NM 21.39 NM 78.63
05/24/16 NM 17.04 NM 82.98
07/06/18 NM 19.66 NM 80.36
6/8/2021 NM 17.51 NM 82.51
05/17/15 NM 23.45 NM 77.51
05/24/16 NM 19.38 NM 81.58
07/06/18 NM 21.70 NM 79.26
10/02/19 NM 20.87 NM 80.09
6/8/2021 NM 18.70 NM 82.26
02/23/16 NM 20.30 NM 79.57
05/24/16 NM 19.63 NM 80.24
07/06/18 NM 22.66 NM 77.21
6/8/2021 NM 20.42 NM 79.45
11/17/03 NM 21.19 NM 78.68
03/24/09 NM 24.33 NM 75.54
01/20/15 NM 23.65 NM 76.22
05/24/16 NM 20.00 NM 79.87
07/06/18 NM 22.12 NM 77.75
10/02/19 NM 21.37 NM 78.50
6/8/2021 NM 19.18 NM 80.69
1)
2)
3)
4)
Monitoring well construction and top of casing elevation information for monitoring wells obtained from December 17, 2019 Monitoring Report prepared by ECS.
VEW‐1 85.0
58.0
MW‐7 30.0
Asheboro, Randolph County, North Carolina
Notes:
LNAPL ‐ Light Non‐Aqueous Phase Liquid
Groundwater elevation adjusted for LNAPL is [Top of Casing Elevation ‐ Depth to Water] + [LNAPL Thickness * 0.8581]
MW‐1 100.00
MW‐3 47.0
100.02MW‐6
MW‐5
TABLE B‐7
MONITORING WELL CONSTRUCTION INFORMATION AND LIQUID LEVEL DATA
Save More #045
Incident # 15046
1424 N. Fayetteville Street
101.39
Destroyed
NM = Not Measured
53.0
98.99
98.67
100.96
99.87
51.5
100.12
99.73MW‐2 41.5
MW‐8 30.0
53.0
MW‐4
WithersRavenel
Our People. Your Success.
APPENDIX A
FIELD NOTES & PHOTOGRAPHIC RECORD
WithersRavenel
Our People. Your Success.
Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report Photograph Date: June 8, 2021
PHOTO 1
View of the site facing east
PHOTO 2
Location of monitoring wells MW‐1 and VEW‐1
WithersRavenel
Our People. Your Success.
Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report Photograph Date: June 8,2021
PHOTO 3
Location of monitoring well MW‐2
PHOTO 4
Interior of monitoring well MW‐2 vault
WithersRavenel
Our People. Your Success.
Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report Photograph Date: June 8,2021
PHOTO 5
Location of monitoring well MW‐3
PHOTO 6
Location of monitoring well MW‐4
WithersRavenel
Our People. Your Success.
Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report Photograph Date: June 8,2021
PHOTO 7
Location of monitoring well MW‐5
PHOTO 8
Location of monitoring well MW‐6
WithersRavenel
Our People. Your Success.
Save More #045 – Incident #15046 WR Project # 02172214.24
Annual Monitoring Report Photograph Date: June 8,2021
PHOTO 9
Location of monitoring well MW‐7
PHOTO 10
Location of monitoring well MW‐8
WithersRavenel
Our People. Your Success.
APPENDIX B
RETURNED WATER SUPPLY WELL INFORMATION SHEETS
&
CITY OF ASHEBORO UTILITY DEPARTMENT INFORMATION
LOCATION ADDRESS Connected to Municipal Water?
1334 N FAYETTEVILLE ST yes
1335 N FAYETTEVILLE ST yes
1338 N FAYETTEVILLE ST yes
1341 N FAYETTEVILLE ST yes
1342 N FAYETTEVILLE ST No building on parcel‐ do not have acct in system for this service address ‐ had an acct in 2001.
1344 N FAYETTEVILLE ST No building on parcel‐ yes ‐ vacant
1347 N FAYETTEVILLE ST yes
1350 N FAYETTEVILLE ST yes
1404 N FAYETTEVILLE ST yes
1406 N FAYETTEVILLE ST yes
1415 N FAYETTEVILLE ST yes
1419 N FAYETTEVILLE ST yes
1424 N FAYETTEVILLE ST yes
1425 N FAYETTEVILLE ST Owner indicated connected to city water
1430 N FAYETTEVILLE ST yes
1433 N FAYETTEVILLE ST yes
1436 N FAYETTEVILLE ST yes
1441 N FAYETTEVILLE ST yes
1442 N FAYETTEVILLE ST yes
1445 N FAYETTEVILLE ST yes
1448 N FAYETTEVILLE ST do not find an account in utility system at this location, multiple addresses
1453 N FAYETTEVILLE ST yes
1454 N FAYETTEVILLE ST yes
1512 N FAYETTEVILLE ST yes
107 SAUNDERS DR No building on parcel‐ listed as inactive vacant
120 SAUNDERS DR do not find an account in utility system at this location ‐ also addressed as 1454 N Fayetteville w/acct
201 SAUNDERS DR yes
207 SAUNDERS DR yes
306 SAUNDERS DR yes
113 BRITTAIN ST do not find an account in utility system at this location, multiple addresses for parcel
203 BRITTAIN ST yes
208 BRITTAIN ST yes
211 BRITTAIN ST yes
300 BRITTAIN ST listed as inactive vacant, house is vacant
306 BRITTAIN ST yes
307 BRITTAIN ST yes
310 BRITTAIN ST yes
311 BRITTAIN ST yes
315 BRITTAIN ST yes
401 BRITTAIN ST listed as inactive vacant
102 WOODBURY ST do not find an account in utility system at this location ‐ Parcel also addressed as 109 ARTHUR ‐ Active account
113 WOODBURY ST Owner indicated connected to city water‐ yes
117 WOODBURY ST yes
123 WOODBURY ST No building on parcel‐ yes
1450 HASTY ST listed as inactive vacant ‐ vacant parcel
1452 HASTY ST yes
1453 HASTY ST yes
1454 HASTY ST yes
1459 HASTY ST yes
1460 HASTY ST yes
205 VALLEY RD yes
311 VALLEY RD yes
317 VALLEY RD No building on parcel‐yes
319 VALLEY RD listed as inactive vacant
1338 MOODY ST yes
111 ARTHUR ST yes
115 ARTHUR ST yes
314 IDEAL DR yes
106 VERNON ST yes
109 VERNON ST yes
110 VERNON ST yes
204 RAINBOW DR yes
WithersRavenel
Our People. Your Success.
APPENDIX C
LABORATORY ANALYTICAL REPORT
&
CHAIN‐OF‐CUSTODY
Laboratory's liability in any claim relating to analyses performed shall be limited to, at laboratory's option, repeating the
analysis in question at laboratory's expense, or the refund of the charges paid for performance of said analysis.
6/16/2021
Withers & Ravenel Liz Allyn
115 Mackenan Dr. BUILDING 117 Cary, NC, 27511
Ref: Analytical Testing
Lab Report Number: 21-160-0004 Client Project Description: Save More #45
02172214.24
Dear Liz Allyn:
Waypoint Analytical, LLC (Charlotte) received sample(s) on 6/9/2021 for the analyses presented in the following report.
The above referenced project has been analyzed per your instructions. The analyses were performed in
accordance with the applicable analytical method.
The analytical data has been validated using standard quality control measures performed as required by the analytical method. Quality Assurance, method validations, instrumentation maintenance and calibration for all
parameters were performed in accordance with guidelines established by the USEPA (including 40 CFR 136 Method Update Rule May 2012) unless otherwise indicated. Certain parameters (chlorine, pH, dissolved oxygen, sulfite...) are required to be analyzed within 15 minutes of
sampling. Usually, but not always, any field parameter analyzed at the laboratory is outside of this holding time. Refer to sample analysis time for confirmation of holding time compliance.
The results are shown on the attached Report of Analysis(s). Results for solid matrices are reported on an as-
received basis unless otherwise indicated. This report shall not be reproduced except in full and relates only to the samples included in this report. Please do not hesitate to contact me or client services if you have any questions or need additional information.
Sincerely,
Angela D Overcash Senior Project Manager
Page 1 of 50
Certification Summary
Laboratory ID: WP CNC: Waypoint Analytical Carolina, Inc. (C), Charlotte, NC
State Program Lab ID Expiration Date
07/31/202137735State ProgramNorth Carolina
12/31/2021402State ProgramNorth Carolina
07/31/202199012State ProgramSouth Carolina
12/31/202199012State ProgramSouth Carolina
Page 1 of 1 00016/21-160-0004
Page 2 of 50
Report Number:
Sample Summary Table
Client Project Description:
21-160-0004
Save More #45
02172214.24
Lab No Client Sample ID Matrix Date Collected Date Received
06/08/2021 12:00Aqueous 89296 MW-1 06/09/2021 12:40
06/08/2021 12:30Aqueous 89297 MW-3 06/09/2021 12:40
06/08/2021 11:05Aqueous 89298 MW-4 06/09/2021 12:40
06/08/2021 10:35Aqueous 89299 MW-5 06/09/2021 12:40
06/08/2021 10:05Aqueous 89300 MW-6 06/09/2021 12:40
06/08/2021 13:00Aqueous 89301 MW-7 06/09/2021 12:40
06/08/2021 13:30Aqueous 89302 MW-8 06/09/2021 12:40
06/08/2021 11:35Aqueous 89303 VEW-1 06/09/2021 12:40
06/08/2021 14:00Aqueous 89304 Field Blank 06/09/2021 12:40
Page 3 of 50
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
21-160-0004
Report Limit
Project:Save More #45
V 89296MW-1
29100 06/16/2021 07:556200BBenzeneµg/L 500
762 06/16/2021 07:556200BDi-Isopropyl Ether (DIPE)µg/L 500
3470 06/16/2021 07:556200BEthylbenzeneµg/L 500
87600 06/16/2021 12:536200BMethyl tert-butyl ether (MTBE)µg/L 10000
1160 06/16/2021 07:556200BNaphthaleneµg/L 1000
7550 06/16/2021 07:556200BTolueneµg/L 500
3450 06/16/2021 07:556200B1,2,4-Trimethylbenzene µg/L 500
971 06/16/2021 07:556200B1,3,5-Trimethylbenzene µg/L 500
2350 06/16/2021 07:556200Bo-Xylene µg/L 500
7070 06/16/2021 07:556200Bm,p-Xylene µg/L 1000
9420 06/16/2021 07:556200BXylene (Total)µg/L 500
V 89297MW-3
6980 06/16/2021 13:186200BBenzeneµg/L 500
99.4 06/16/2021 08:186200BDi-Isopropyl Ether (DIPE)µg/L 50.0
1580 06/16/2021 08:186200BEthylbenzeneµg/L 50.0
80.8 06/16/2021 08:186200BIsopropylbenzeneµg/L 50.0
9120 06/16/2021 08:186200BMethyl tert-butyl ether (MTBE)µg/L 100
476 06/16/2021 08:186200BNaphthaleneµg/L 100
216 06/16/2021 08:186200Bn-Propylbenzene µg/L 50.0
773 06/16/2021 08:186200BTolueneµg/L 50.0
1010 06/16/2021 08:186200B1,2,4-Trimethylbenzene µg/L 50.0
183 06/16/2021 08:186200B1,3,5-Trimethylbenzene µg/L 50.0
74.9 06/16/2021 08:186200Bo-Xylene µg/L 50.0
3230 06/16/2021 08:186200Bm,p-Xylene µg/L 100
3300 06/16/2021 08:186200BXylene (Total)µg/L 50.0
V 89298MW-4
0.664 06/16/2021 05:556200Bn-Butylbenzene µg/L 0.500
0.719 06/16/2021 05:556200Bsec-Butyl benzene µg/L 0.500
2.26 06/16/2021 05:556200BChlorobenzeneµg/L 0.500
1.87 06/16/2021 05:556200B1,4-Dichlorobenzene µg/L 0.500
1.39 06/16/2021 05:556200BIsopropylbenzeneµg/L 0.500
0.569 06/16/2021 05:556200Bn-Propylbenzene µg/L 0.500
V 89300MW-6
2.76 06/16/2021 06:436200BDi-Isopropyl Ether (DIPE)µg/L 0.500
1.08 06/16/2021 06:436200BMethyl tert-butyl ether (MTBE)µg/L 1.00
Page 4 of 50
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
21-160-0004
Report Limit
Project:Save More #45
V 89301MW-7
9750 06/16/2021 08:426200BBenzeneµg/L 50.0
299 06/16/2021 08:426200BDi-Isopropyl Ether (DIPE)µg/L 50.0
721 06/16/2021 08:426200BEthylbenzeneµg/L 50.0
48600 06/16/2021 09:066200BMethyl tert-butyl ether (MTBE)µg/L 1000
492 06/16/2021 08:426200BNaphthaleneµg/L 100
130 06/16/2021 08:426200Bn-Propylbenzene µg/L 50.0
360 06/16/2021 08:426200BTolueneµg/L 50.0
890 06/16/2021 08:426200B1,2,4-Trimethylbenzene µg/L 50.0
188 06/16/2021 08:426200B1,3,5-Trimethylbenzene µg/L 50.0
1470 06/16/2021 08:426200Bm,p-Xylene µg/L 100
1470 06/16/2021 08:426200BXylene (Total)µg/L 50.0
V 89303VEW-1
6690 06/16/2021 07:316200BMethyl tert-butyl ether (MTBE)µg/L 100
Page 5 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-1
89296 Matrix:
6/8/2021 12:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<10000 µg/L 10000Acetone 1000 06/16/21 07:55 6200BJLB
29100 µg/L 500Benzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Bromobenzene 1000 06/16/21 07:55 6200BJLB
<1000 µg/L 1000Bromochloromethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Bromodichloromethane 1000 06/16/21 07:55 6200BJLB
<5000 µg/L 5000Bromoform 1000 06/16/21 07:55 6200BJLB
<1000 µg/L 1000Bromomethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500n-Butylbenzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500sec-Butyl benzene 1000 06/16/21 07:55 6200BJLB
<2000 µg/L 2000tert-Butyl benzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Carbon Tetrachloride 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Chlorobenzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Chlorodibromomethane 1000 06/16/21 07:55 6200BJLB
<1000 µg/L 1000Chloroethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Chloroform 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Chloromethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5002-Chlorotoluene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5004-Chlorotoluene 1000 06/16/21 07:55 6200BJLB
<2000 µg/L 20001,2-Dibromo-3-Chloropropane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,2-Dibromoethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Dibromomethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,2-Dichlorobenzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,3-Dichlorobenzene 1000 06/16/21 07:55 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 6 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-1
89296 Matrix:
6/8/2021 12:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<500 µg/L 5001,4-Dichlorobenzene 1000 06/16/21 07:55 6200BJLB
<5000 µg/L 5000Dichlorodifluoromethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,1-Dichloroethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,2-Dichloroethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,1-Dichloroethene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500cis-1,2-Dichloroethene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500trans-1,2-Dichloroethene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,2-Dichloropropane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,3-Dichloropropane 1000 06/16/21 07:55 6200BJLB
<2000 µg/L 20002,2-Dichloropropane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,1-Dichloropropene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500cis-1,3-Dichloropropene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500trans-1,3-Dichloropropene 1000 06/16/21 07:55 6200BJLB
<200000 µg/L 200000Ethanol 1000 06/16/21 07:55 6200BJLB
3470 µg/L 500Ethylbenzene 1000 06/16/21 07:55 6200BJLB
<3000 µg/L 3000Hexachlorobutadiene 1000 06/16/21 07:55 6200BJLB
762 µg/L 500Di-Isopropyl Ether (DIPE)1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Isopropylbenzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5004-Isopropyl toluene 1000 06/16/21 07:55 6200BJLB
<1000 µg/L 10002-Hexanone 1000 06/16/21 07:55 6200BJLB
<5000 µg/L 5000Methyl Ethyl Ketone (MEK)1000 06/16/21 07:55 6200BJLB
<2000 µg/L 2000Methylene Chloride 1000 06/16/21 07:55 6200BJLB
87600 µg/L 10000Methyl tert-butyl ether (MTBE)10000 06/16/21 12:53 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 7 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-1
89296 Matrix:
6/8/2021 12:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1000 µg/L 10004-Methyl-2-Pentanone 1000 06/16/21 07:55 6200BJLB
1160 µg/L 1000Naphthalene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500n-Propylbenzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Styrene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,1,1,2-Tetrachloroethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,1,2,2-Tetrachloroethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Tetrachloroethene 1000 06/16/21 07:55 6200BJLB
7550 µg/L 500Toluene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,2,3-Trichlorobenzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,2,4-Trichlorobenzene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,1,1-Trichloroethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,1,2-Trichloroethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Trichloroethene 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Trichlorofluoromethane 1000 06/16/21 07:55 6200BJLB
<500 µg/L 5001,2,3-Trichloropropane 1000 06/16/21 07:55 6200BJLB
3450 µg/L 5001,2,4-Trimethylbenzene 1000 06/16/21 07:55 6200BJLB
971 µg/L 5001,3,5-Trimethylbenzene 1000 06/16/21 07:55 6200BJLB
<5000 µg/L 5000Vinyl Acetate 1000 06/16/21 07:55 6200BJLB
<500 µg/L 500Vinyl Chloride 1000 06/16/21 07:55 6200BJLB
7070 µg/L 1000m,p-Xylene 1000 06/16/21 07:55 6200BJLB
2350 µg/L 500o-Xylene 1000 06/16/21 07:55 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 8 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-1
89296 Matrix:
6/8/2021 12:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
9420 µg/L 500Xylene (Total)1000 06/16/21 07:55 6200B
Surrogate: 4-Bromofluorobenzene 97.6 Limits: 70-130%06/16/21 07:551000 JLB V5426
Surrogate: Dibromofluoromethane 97.0 Limits: 70-130%06/16/21 07:551000 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 89.4 Limits: 70-130%06/16/21 07:551000 JLB V5426
Surrogate: Toluene-d8 85.8 Limits: 70-130%06/16/21 07:551000 JLB V5426
Surrogate: 4-Bromofluorobenzene 101 Limits: 70-130%06/16/21 12:5310000 JLB V5442
Surrogate: Dibromofluoromethane 109 Limits: 70-130%06/16/21 12:5310000 JLB V5442
Surrogate: 1,2-Dichloroethane - d4 119 Limits: 70-130%06/16/21 12:5310000 JLB V5442
Surrogate: Toluene-d8 121 Limits: 70-130%06/16/21 12:5310000 JLB V5442
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 9 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-3
89297 Matrix:
6/8/2021 12:30
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1000 µg/L 1000Acetone 100 06/16/21 08:18 6200BJLB
6980 µg/L 500Benzene 1000 06/16/21 13:18 6200BJLB
<50.0 µg/L 50.0Bromobenzene 100 06/16/21 08:18 6200BJLB
<100 µg/L 100Bromochloromethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Bromodichloromethane 100 06/16/21 08:18 6200BJLB
<500 µg/L 500Bromoform 100 06/16/21 08:18 6200BJLB
<100 µg/L 100Bromomethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0n-Butylbenzene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0sec-Butyl benzene 100 06/16/21 08:18 6200BJLB
<200 µg/L 200tert-Butyl benzene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Carbon Tetrachloride 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Chlorobenzene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Chlorodibromomethane 100 06/16/21 08:18 6200BJLB
<100 µg/L 100Chloroethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Chloroform 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Chloromethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.02-Chlorotoluene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.04-Chlorotoluene 100 06/16/21 08:18 6200BJLB
<200 µg/L 2001,2-Dibromo-3-Chloropropane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,2-Dibromoethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Dibromomethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,2-Dichlorobenzene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,3-Dichlorobenzene 100 06/16/21 08:18 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 10 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-3
89297 Matrix:
6/8/2021 12:30
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<50.0 µg/L 50.01,4-Dichlorobenzene 100 06/16/21 08:18 6200BJLB
<500 µg/L 500Dichlorodifluoromethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,1-Dichloroethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,2-Dichloroethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,1-Dichloroethene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0cis-1,2-Dichloroethene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0trans-1,2-Dichloroethene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,2-Dichloropropane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,3-Dichloropropane 100 06/16/21 08:18 6200BJLB
<200 µg/L 2002,2-Dichloropropane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,1-Dichloropropene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0cis-1,3-Dichloropropene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0trans-1,3-Dichloropropene 100 06/16/21 08:18 6200BJLB
<20000 µg/L 20000Ethanol 100 06/16/21 08:18 6200BJLB
1580 µg/L 50.0Ethylbenzene 100 06/16/21 08:18 6200BJLB
<300 µg/L 300Hexachlorobutadiene 100 06/16/21 08:18 6200BJLB
99.4 µg/L 50.0Di-Isopropyl Ether (DIPE)100 06/16/21 08:18 6200BJLB
80.8 µg/L 50.0Isopropylbenzene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.04-Isopropyl toluene 100 06/16/21 08:18 6200BJLB
<100 µg/L 1002-Hexanone 100 06/16/21 08:18 6200BJLB
<500 µg/L 500Methyl Ethyl Ketone (MEK)100 06/16/21 08:18 6200BJLB
<200 µg/L 200Methylene Chloride 100 06/16/21 08:18 6200BJLB
9120 µg/L 100Methyl tert-butyl ether (MTBE)100 06/16/21 08:18 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 11 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-3
89297 Matrix:
6/8/2021 12:30
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<100 µg/L 1004-Methyl-2-Pentanone 100 06/16/21 08:18 6200BJLB
476 µg/L 100Naphthalene 100 06/16/21 08:18 6200BJLB
216 µg/L 50.0n-Propylbenzene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Styrene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,1,1,2-Tetrachloroethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,1,2,2-Tetrachloroethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Tetrachloroethene 100 06/16/21 08:18 6200BJLB
773 µg/L 50.0Toluene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,2,3-Trichlorobenzene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,2,4-Trichlorobenzene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,1,1-Trichloroethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,1,2-Trichloroethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Trichloroethene 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Trichlorofluoromethane 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.01,2,3-Trichloropropane 100 06/16/21 08:18 6200BJLB
1010 µg/L 50.01,2,4-Trimethylbenzene 100 06/16/21 08:18 6200BJLB
183 µg/L 50.01,3,5-Trimethylbenzene 100 06/16/21 08:18 6200BJLB
<500 µg/L 500Vinyl Acetate 100 06/16/21 08:18 6200BJLB
<50.0 µg/L 50.0Vinyl Chloride 100 06/16/21 08:18 6200BJLB
3230 µg/L 100m,p-Xylene 100 06/16/21 08:18 6200BJLB
74.9 µg/L 50.0o-Xylene 100 06/16/21 08:18 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 12 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-3
89297 Matrix:
6/8/2021 12:30
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
3300 µg/L 50.0Xylene (Total)100 06/16/21 08:18 6200B
Surrogate: 4-Bromofluorobenzene 100 Limits: 70-130%06/16/21 08:18100 JLB V5426
Surrogate: Dibromofluoromethane 97.8 Limits: 70-130%06/16/21 08:18100 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 88.8 Limits: 70-130%06/16/21 08:18100 JLB V5426
Surrogate: Toluene-d8 85.4 Limits: 70-130%06/16/21 08:18100 JLB V5426
Surrogate: 4-Bromofluorobenzene 101 Limits: 70-130%06/16/21 13:181000 JLB V5442
Surrogate: Dibromofluoromethane 109 Limits: 70-130%06/16/21 13:181000 JLB V5442
Surrogate: 1,2-Dichloroethane - d4 117 Limits: 70-130%06/16/21 13:181000 JLB V5442
Surrogate: Toluene-d8 121 Limits: 70-130%06/16/21 13:181000 JLB V5442
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 13 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-4
89298 Matrix:
6/8/2021 11:05
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<10.0 µg/L 10.0Acetone 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Benzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Bromobenzene 1 06/16/21 05:55 6200BJLB
<1.00 µg/L 1.00Bromochloromethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Bromodichloromethane 1 06/16/21 05:55 6200BJLB
<5.00 µg/L 5.00Bromoform 1 06/16/21 05:55 6200BJLB
<1.00 µg/L 1.00Bromomethane 1 06/16/21 05:55 6200BJLB
0.664 µg/L 0.500n-Butylbenzene 1 06/16/21 05:55 6200BJLB
0.719 µg/L 0.500sec-Butyl benzene 1 06/16/21 05:55 6200BJLB
<2.00 µg/L 2.00tert-Butyl benzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Carbon Tetrachloride 1 06/16/21 05:55 6200BJLB
2.26 µg/L 0.500Chlorobenzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Chlorodibromomethane 1 06/16/21 05:55 6200BJLB
<1.00 µg/L 1.00Chloroethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Chloroform 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Chloromethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5002-Chlorotoluene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5004-Chlorotoluene 1 06/16/21 05:55 6200BJLB
<2.00 µg/L 2.001,2-Dibromo-3-Chloropropane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,2-Dibromoethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Dibromomethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,2-Dichlorobenzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,3-Dichlorobenzene 1 06/16/21 05:55 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 14 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-4
89298 Matrix:
6/8/2021 11:05
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
1.87 µg/L 0.5001,4-Dichlorobenzene 1 06/16/21 05:55 6200BJLB
<5.00 µg/L 5.00Dichlorodifluoromethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,2-Dichloroethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500cis-1,2-Dichloroethene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500trans-1,2-Dichloroethene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,2-Dichloropropane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,3-Dichloropropane 1 06/16/21 05:55 6200BJLB
<2.00 µg/L 2.002,2-Dichloropropane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,1-Dichloropropene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500cis-1,3-Dichloropropene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500trans-1,3-Dichloropropene 1 06/16/21 05:55 6200BJLB
<200 µg/L 200Ethanol 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Ethylbenzene 1 06/16/21 05:55 6200BJLB
<3.00 µg/L 3.00Hexachlorobutadiene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Di-Isopropyl Ether (DIPE)1 06/16/21 05:55 6200BJLB
1.39 µg/L 0.500Isopropylbenzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5004-Isopropyl toluene 1 06/16/21 05:55 6200BJLB
<1.00 µg/L 1.002-Hexanone 1 06/16/21 05:55 6200BJLB
<5.00 µg/L 5.00Methyl Ethyl Ketone (MEK)1 06/16/21 05:55 6200BJLB
<2.00 µg/L 2.00Methylene Chloride 1 06/16/21 05:55 6200BJLB
<1.00 µg/L 1.00Methyl tert-butyl ether (MTBE)1 06/16/21 05:55 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 15 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-4
89298 Matrix:
6/8/2021 11:05
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1.00 µg/L 1.004-Methyl-2-Pentanone 1 06/16/21 05:55 6200BJLB
<1.00 µg/L 1.00Naphthalene 1 06/16/21 05:55 6200BJLB
0.569 µg/L 0.500n-Propylbenzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Styrene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,1,1,2-Tetrachloroethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,1,2,2-Tetrachloroethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Tetrachloroethene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Toluene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichlorobenzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,2,4-Trichlorobenzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,1,1-Trichloroethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,1,2-Trichloroethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Trichloroethene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Trichlorofluoromethane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichloropropane 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,2,4-Trimethylbenzene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.5001,3,5-Trimethylbenzene 1 06/16/21 05:55 6200BJLB
<5.00 µg/L 5.00Vinyl Acetate 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500Vinyl Chloride 1 06/16/21 05:55 6200BJLB
<1.00 µg/L 1.00m,p-Xylene 1 06/16/21 05:55 6200BJLB
<0.500 µg/L 0.500o-Xylene 1 06/16/21 05:55 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 16 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-4
89298 Matrix:
6/8/2021 11:05
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.500Xylene (Total)1 06/16/21 05:55 6200B
Surrogate: 4-Bromofluorobenzene 99.4 Limits: 70-130%06/16/21 05:551 JLB V5426
Surrogate: Dibromofluoromethane 101 Limits: 70-130%06/16/21 05:551 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 94.6 Limits: 70-130%06/16/21 05:551 JLB V5426
Surrogate: Toluene-d8 86.4 Limits: 70-130%06/16/21 05:551 JLB V5426
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 17 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-5
89299 Matrix:
6/8/2021 10:35
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<10.0 µg/L 10.0Acetone 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Benzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Bromobenzene 1 06/16/21 06:19 6200BJLB
<1.00 µg/L 1.00Bromochloromethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Bromodichloromethane 1 06/16/21 06:19 6200BJLB
<5.00 µg/L 5.00Bromoform 1 06/16/21 06:19 6200BJLB
<1.00 µg/L 1.00Bromomethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500n-Butylbenzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500sec-Butyl benzene 1 06/16/21 06:19 6200BJLB
<2.00 µg/L 2.00tert-Butyl benzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Carbon Tetrachloride 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Chlorobenzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Chlorodibromomethane 1 06/16/21 06:19 6200BJLB
<1.00 µg/L 1.00Chloroethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Chloroform 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Chloromethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5002-Chlorotoluene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5004-Chlorotoluene 1 06/16/21 06:19 6200BJLB
<2.00 µg/L 2.001,2-Dibromo-3-Chloropropane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,2-Dibromoethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Dibromomethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,2-Dichlorobenzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,3-Dichlorobenzene 1 06/16/21 06:19 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 18 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-5
89299 Matrix:
6/8/2021 10:35
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.5001,4-Dichlorobenzene 1 06/16/21 06:19 6200BJLB
<5.00 µg/L 5.00Dichlorodifluoromethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,2-Dichloroethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500cis-1,2-Dichloroethene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500trans-1,2-Dichloroethene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,2-Dichloropropane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,3-Dichloropropane 1 06/16/21 06:19 6200BJLB
<2.00 µg/L 2.002,2-Dichloropropane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,1-Dichloropropene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500cis-1,3-Dichloropropene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500trans-1,3-Dichloropropene 1 06/16/21 06:19 6200BJLB
<200 µg/L 200Ethanol 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Ethylbenzene 1 06/16/21 06:19 6200BJLB
<3.00 µg/L 3.00Hexachlorobutadiene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Di-Isopropyl Ether (DIPE)1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Isopropylbenzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5004-Isopropyl toluene 1 06/16/21 06:19 6200BJLB
<1.00 µg/L 1.002-Hexanone 1 06/16/21 06:19 6200BJLB
<5.00 µg/L 5.00Methyl Ethyl Ketone (MEK)1 06/16/21 06:19 6200BJLB
<2.00 µg/L 2.00Methylene Chloride 1 06/16/21 06:19 6200BJLB
<1.00 µg/L 1.00Methyl tert-butyl ether (MTBE)1 06/16/21 06:19 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 19 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-5
89299 Matrix:
6/8/2021 10:35
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1.00 µg/L 1.004-Methyl-2-Pentanone 1 06/16/21 06:19 6200BJLB
<1.00 µg/L 1.00Naphthalene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500n-Propylbenzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Styrene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,1,1,2-Tetrachloroethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,1,2,2-Tetrachloroethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Tetrachloroethene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Toluene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichlorobenzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,2,4-Trichlorobenzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,1,1-Trichloroethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,1,2-Trichloroethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Trichloroethene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Trichlorofluoromethane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichloropropane 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,2,4-Trimethylbenzene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.5001,3,5-Trimethylbenzene 1 06/16/21 06:19 6200BJLB
<5.00 µg/L 5.00Vinyl Acetate 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500Vinyl Chloride 1 06/16/21 06:19 6200BJLB
<1.00 µg/L 1.00m,p-Xylene 1 06/16/21 06:19 6200BJLB
<0.500 µg/L 0.500o-Xylene 1 06/16/21 06:19 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 20 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-5
89299 Matrix:
6/8/2021 10:35
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.500Xylene (Total)1 06/16/21 06:19 6200B
Surrogate: 4-Bromofluorobenzene 98.6 Limits: 70-130%06/16/21 06:191 JLB V5426
Surrogate: Dibromofluoromethane 98.8 Limits: 70-130%06/16/21 06:191 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 94.8 Limits: 70-130%06/16/21 06:191 JLB V5426
Surrogate: Toluene-d8 84.4 Limits: 70-130%06/16/21 06:191 JLB V5426
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 21 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-6
89300 Matrix:
6/8/2021 10:05
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<10.0 µg/L 10.0Acetone 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Benzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Bromobenzene 1 06/16/21 06:43 6200BJLB
<1.00 µg/L 1.00Bromochloromethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Bromodichloromethane 1 06/16/21 06:43 6200BJLB
<5.00 µg/L 5.00Bromoform 1 06/16/21 06:43 6200BJLB
<1.00 µg/L 1.00Bromomethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500n-Butylbenzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500sec-Butyl benzene 1 06/16/21 06:43 6200BJLB
<2.00 µg/L 2.00tert-Butyl benzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Carbon Tetrachloride 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Chlorobenzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Chlorodibromomethane 1 06/16/21 06:43 6200BJLB
<1.00 µg/L 1.00Chloroethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Chloroform 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Chloromethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5002-Chlorotoluene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5004-Chlorotoluene 1 06/16/21 06:43 6200BJLB
<2.00 µg/L 2.001,2-Dibromo-3-Chloropropane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,2-Dibromoethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Dibromomethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,2-Dichlorobenzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,3-Dichlorobenzene 1 06/16/21 06:43 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 22 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-6
89300 Matrix:
6/8/2021 10:05
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.5001,4-Dichlorobenzene 1 06/16/21 06:43 6200BJLB
<5.00 µg/L 5.00Dichlorodifluoromethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,2-Dichloroethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500cis-1,2-Dichloroethene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500trans-1,2-Dichloroethene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,2-Dichloropropane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,3-Dichloropropane 1 06/16/21 06:43 6200BJLB
<2.00 µg/L 2.002,2-Dichloropropane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,1-Dichloropropene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500cis-1,3-Dichloropropene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500trans-1,3-Dichloropropene 1 06/16/21 06:43 6200BJLB
<200 µg/L 200Ethanol 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Ethylbenzene 1 06/16/21 06:43 6200BJLB
<3.00 µg/L 3.00Hexachlorobutadiene 1 06/16/21 06:43 6200BJLB
2.76 µg/L 0.500Di-Isopropyl Ether (DIPE)1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Isopropylbenzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5004-Isopropyl toluene 1 06/16/21 06:43 6200BJLB
<1.00 µg/L 1.002-Hexanone 1 06/16/21 06:43 6200BJLB
<5.00 µg/L 5.00Methyl Ethyl Ketone (MEK)1 06/16/21 06:43 6200BJLB
<2.00 µg/L 2.00Methylene Chloride 1 06/16/21 06:43 6200BJLB
1.08 µg/L 1.00Methyl tert-butyl ether (MTBE)1 06/16/21 06:43 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 23 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-6
89300 Matrix:
6/8/2021 10:05
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1.00 µg/L 1.004-Methyl-2-Pentanone 1 06/16/21 06:43 6200BJLB
<1.00 µg/L 1.00Naphthalene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500n-Propylbenzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Styrene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,1,1,2-Tetrachloroethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,1,2,2-Tetrachloroethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Tetrachloroethene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Toluene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichlorobenzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,2,4-Trichlorobenzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,1,1-Trichloroethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,1,2-Trichloroethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Trichloroethene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Trichlorofluoromethane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichloropropane 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,2,4-Trimethylbenzene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.5001,3,5-Trimethylbenzene 1 06/16/21 06:43 6200BJLB
<5.00 µg/L 5.00Vinyl Acetate 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500Vinyl Chloride 1 06/16/21 06:43 6200BJLB
<1.00 µg/L 1.00m,p-Xylene 1 06/16/21 06:43 6200BJLB
<0.500 µg/L 0.500o-Xylene 1 06/16/21 06:43 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 24 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-6
89300 Matrix:
6/8/2021 10:05
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.500Xylene (Total)1 06/16/21 06:43 6200B
Surrogate: 4-Bromofluorobenzene 98.8 Limits: 70-130%06/16/21 06:431 JLB V5426
Surrogate: Dibromofluoromethane 99.8 Limits: 70-130%06/16/21 06:431 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 94.6 Limits: 70-130%06/16/21 06:431 JLB V5426
Surrogate: Toluene-d8 83.6 Limits: 70-130%06/16/21 06:431 JLB V5426
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 25 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-7
89301 Matrix:
6/8/2021 13:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1000 µg/L 1000Acetone 100 06/16/21 08:42 6200BJLB
9750 µg/L 50.0Benzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Bromobenzene 100 06/16/21 08:42 6200BJLB
<100 µg/L 100Bromochloromethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Bromodichloromethane 100 06/16/21 08:42 6200BJLB
<500 µg/L 500Bromoform 100 06/16/21 08:42 6200BJLB
<100 µg/L 100Bromomethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0n-Butylbenzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0sec-Butyl benzene 100 06/16/21 08:42 6200BJLB
<200 µg/L 200tert-Butyl benzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Carbon Tetrachloride 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Chlorobenzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Chlorodibromomethane 100 06/16/21 08:42 6200BJLB
<100 µg/L 100Chloroethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Chloroform 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Chloromethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.02-Chlorotoluene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.04-Chlorotoluene 100 06/16/21 08:42 6200BJLB
<200 µg/L 2001,2-Dibromo-3-Chloropropane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,2-Dibromoethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Dibromomethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,2-Dichlorobenzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,3-Dichlorobenzene 100 06/16/21 08:42 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 26 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-7
89301 Matrix:
6/8/2021 13:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<50.0 µg/L 50.01,4-Dichlorobenzene 100 06/16/21 08:42 6200BJLB
<500 µg/L 500Dichlorodifluoromethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,1-Dichloroethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,2-Dichloroethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,1-Dichloroethene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0cis-1,2-Dichloroethene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0trans-1,2-Dichloroethene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,2-Dichloropropane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,3-Dichloropropane 100 06/16/21 08:42 6200BJLB
<200 µg/L 2002,2-Dichloropropane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,1-Dichloropropene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0cis-1,3-Dichloropropene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0trans-1,3-Dichloropropene 100 06/16/21 08:42 6200BJLB
<20000 µg/L 20000Ethanol 100 06/16/21 08:42 6200BJLB
721 µg/L 50.0Ethylbenzene 100 06/16/21 08:42 6200BJLB
<300 µg/L 300Hexachlorobutadiene 100 06/16/21 08:42 6200BJLB
299 µg/L 50.0Di-Isopropyl Ether (DIPE)100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Isopropylbenzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.04-Isopropyl toluene 100 06/16/21 08:42 6200BJLB
<100 µg/L 1002-Hexanone 100 06/16/21 08:42 6200BJLB
<500 µg/L 500Methyl Ethyl Ketone (MEK)100 06/16/21 08:42 6200BJLB
<200 µg/L 200Methylene Chloride 100 06/16/21 08:42 6200BJLB
48600 µg/L 1000Methyl tert-butyl ether (MTBE)1000 06/16/21 09:06 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 27 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-7
89301 Matrix:
6/8/2021 13:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<100 µg/L 1004-Methyl-2-Pentanone 100 06/16/21 08:42 6200BJLB
492 µg/L 100Naphthalene 100 06/16/21 08:42 6200BJLB
130 µg/L 50.0n-Propylbenzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Styrene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,1,1,2-Tetrachloroethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,1,2,2-Tetrachloroethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Tetrachloroethene 100 06/16/21 08:42 6200BJLB
360 µg/L 50.0Toluene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,2,3-Trichlorobenzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,2,4-Trichlorobenzene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,1,1-Trichloroethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,1,2-Trichloroethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Trichloroethene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Trichlorofluoromethane 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.01,2,3-Trichloropropane 100 06/16/21 08:42 6200BJLB
890 µg/L 50.01,2,4-Trimethylbenzene 100 06/16/21 08:42 6200BJLB
188 µg/L 50.01,3,5-Trimethylbenzene 100 06/16/21 08:42 6200BJLB
<500 µg/L 500Vinyl Acetate 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0Vinyl Chloride 100 06/16/21 08:42 6200BJLB
1470 µg/L 100m,p-Xylene 100 06/16/21 08:42 6200BJLB
<50.0 µg/L 50.0o-Xylene 100 06/16/21 08:42 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 28 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-7
89301 Matrix:
6/8/2021 13:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
1470 µg/L 50.0Xylene (Total)100 06/16/21 08:42 6200B
Surrogate: 4-Bromofluorobenzene 97.4 Limits: 70-130%06/16/21 08:42100 JLB V5426
Surrogate: Dibromofluoromethane 98.2 Limits: 70-130%06/16/21 08:42100 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 91.8 Limits: 70-130%06/16/21 08:42100 JLB V5426
Surrogate: Toluene-d8 84.2 Limits: 70-130%06/16/21 08:42100 JLB V5426
Surrogate: 4-Bromofluorobenzene 100 Limits: 70-130%06/16/21 09:061000 JLB V5426
Surrogate: Dibromofluoromethane 97.8 Limits: 70-130%06/16/21 09:061000 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 91.0 Limits: 70-130%06/16/21 09:061000 JLB V5426
Surrogate: Toluene-d8 83.8 Limits: 70-130%06/16/21 09:061000 JLB V5426
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 29 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-8
89302 Matrix:
6/8/2021 13:30
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<10.0 µg/L 10.0Acetone 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Benzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Bromobenzene 1 06/16/21 07:07 6200BJLB
<1.00 µg/L 1.00Bromochloromethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Bromodichloromethane 1 06/16/21 07:07 6200BJLB
<5.00 µg/L 5.00Bromoform 1 06/16/21 07:07 6200BJLB
<1.00 µg/L 1.00Bromomethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500n-Butylbenzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500sec-Butyl benzene 1 06/16/21 07:07 6200BJLB
<2.00 µg/L 2.00tert-Butyl benzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Carbon Tetrachloride 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Chlorobenzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Chlorodibromomethane 1 06/16/21 07:07 6200BJLB
<1.00 µg/L 1.00Chloroethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Chloroform 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Chloromethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5002-Chlorotoluene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5004-Chlorotoluene 1 06/16/21 07:07 6200BJLB
<2.00 µg/L 2.001,2-Dibromo-3-Chloropropane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,2-Dibromoethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Dibromomethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,2-Dichlorobenzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,3-Dichlorobenzene 1 06/16/21 07:07 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 30 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-8
89302 Matrix:
6/8/2021 13:30
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.5001,4-Dichlorobenzene 1 06/16/21 07:07 6200BJLB
<5.00 µg/L 5.00Dichlorodifluoromethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,2-Dichloroethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500cis-1,2-Dichloroethene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500trans-1,2-Dichloroethene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,2-Dichloropropane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,3-Dichloropropane 1 06/16/21 07:07 6200BJLB
<2.00 µg/L 2.002,2-Dichloropropane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,1-Dichloropropene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500cis-1,3-Dichloropropene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500trans-1,3-Dichloropropene 1 06/16/21 07:07 6200BJLB
<200 µg/L 200Ethanol 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Ethylbenzene 1 06/16/21 07:07 6200BJLB
<3.00 µg/L 3.00Hexachlorobutadiene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Di-Isopropyl Ether (DIPE)1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Isopropylbenzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5004-Isopropyl toluene 1 06/16/21 07:07 6200BJLB
<1.00 µg/L 1.002-Hexanone 1 06/16/21 07:07 6200BJLB
<5.00 µg/L 5.00Methyl Ethyl Ketone (MEK)1 06/16/21 07:07 6200BJLB
<2.00 µg/L 2.00Methylene Chloride 1 06/16/21 07:07 6200BJLB
<1.00 µg/L 1.00Methyl tert-butyl ether (MTBE)1 06/16/21 07:07 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 31 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-8
89302 Matrix:
6/8/2021 13:30
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1.00 µg/L 1.004-Methyl-2-Pentanone 1 06/16/21 07:07 6200BJLB
<1.00 µg/L 1.00Naphthalene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500n-Propylbenzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Styrene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,1,1,2-Tetrachloroethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,1,2,2-Tetrachloroethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Tetrachloroethene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Toluene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichlorobenzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,2,4-Trichlorobenzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,1,1-Trichloroethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,1,2-Trichloroethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Trichloroethene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Trichlorofluoromethane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichloropropane 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,2,4-Trimethylbenzene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.5001,3,5-Trimethylbenzene 1 06/16/21 07:07 6200BJLB
<5.00 µg/L 5.00Vinyl Acetate 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500Vinyl Chloride 1 06/16/21 07:07 6200BJLB
<1.00 µg/L 1.00m,p-Xylene 1 06/16/21 07:07 6200BJLB
<0.500 µg/L 0.500o-Xylene 1 06/16/21 07:07 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 32 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:MW-8
89302 Matrix:
6/8/2021 13:30
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.500Xylene (Total)1 06/16/21 07:07 6200B
Surrogate: 4-Bromofluorobenzene 98.2 Limits: 70-130%06/16/21 07:071 JLB V5426
Surrogate: Dibromofluoromethane 103 Limits: 70-130%06/16/21 07:071 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 93.2 Limits: 70-130%06/16/21 07:071 JLB V5426
Surrogate: Toluene-d8 85.0 Limits: 70-130%06/16/21 07:071 JLB V5426
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 33 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:VEW-1
89303 Matrix:
6/8/2021 11:35
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1000 µg/L 1000Acetone 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Benzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Bromobenzene 100 06/16/21 07:31 6200BJLB
<100 µg/L 100Bromochloromethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Bromodichloromethane 100 06/16/21 07:31 6200BJLB
<500 µg/L 500Bromoform 100 06/16/21 07:31 6200BJLB
<100 µg/L 100Bromomethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0n-Butylbenzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0sec-Butyl benzene 100 06/16/21 07:31 6200BJLB
<200 µg/L 200tert-Butyl benzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Carbon Tetrachloride 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Chlorobenzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Chlorodibromomethane 100 06/16/21 07:31 6200BJLB
<100 µg/L 100Chloroethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Chloroform 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Chloromethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.02-Chlorotoluene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.04-Chlorotoluene 100 06/16/21 07:31 6200BJLB
<200 µg/L 2001,2-Dibromo-3-Chloropropane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,2-Dibromoethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Dibromomethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,2-Dichlorobenzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,3-Dichlorobenzene 100 06/16/21 07:31 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 34 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:VEW-1
89303 Matrix:
6/8/2021 11:35
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<50.0 µg/L 50.01,4-Dichlorobenzene 100 06/16/21 07:31 6200BJLB
<500 µg/L 500Dichlorodifluoromethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,1-Dichloroethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,2-Dichloroethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,1-Dichloroethene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0cis-1,2-Dichloroethene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0trans-1,2-Dichloroethene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,2-Dichloropropane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,3-Dichloropropane 100 06/16/21 07:31 6200BJLB
<200 µg/L 2002,2-Dichloropropane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,1-Dichloropropene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0cis-1,3-Dichloropropene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0trans-1,3-Dichloropropene 100 06/16/21 07:31 6200BJLB
<20000 µg/L 20000Ethanol 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Ethylbenzene 100 06/16/21 07:31 6200BJLB
<300 µg/L 300Hexachlorobutadiene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Di-Isopropyl Ether (DIPE)100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Isopropylbenzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.04-Isopropyl toluene 100 06/16/21 07:31 6200BJLB
<100 µg/L 1002-Hexanone 100 06/16/21 07:31 6200BJLB
<500 µg/L 500Methyl Ethyl Ketone (MEK)100 06/16/21 07:31 6200BJLB
<200 µg/L 200Methylene Chloride 100 06/16/21 07:31 6200BJLB
6690 µg/L 100Methyl tert-butyl ether (MTBE)100 06/16/21 07:31 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 35 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:VEW-1
89303 Matrix:
6/8/2021 11:35
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<100 µg/L 1004-Methyl-2-Pentanone 100 06/16/21 07:31 6200BJLB
<100 µg/L 100Naphthalene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0n-Propylbenzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Styrene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,1,1,2-Tetrachloroethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,1,2,2-Tetrachloroethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Tetrachloroethene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Toluene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,2,3-Trichlorobenzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,2,4-Trichlorobenzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,1,1-Trichloroethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,1,2-Trichloroethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Trichloroethene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Trichlorofluoromethane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,2,3-Trichloropropane 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,2,4-Trimethylbenzene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.01,3,5-Trimethylbenzene 100 06/16/21 07:31 6200BJLB
<500 µg/L 500Vinyl Acetate 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0Vinyl Chloride 100 06/16/21 07:31 6200BJLB
<100 µg/L 100m,p-Xylene 100 06/16/21 07:31 6200BJLB
<50.0 µg/L 50.0o-Xylene 100 06/16/21 07:31 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 36 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:VEW-1
89303 Matrix:
6/8/2021 11:35
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<50.0 µg/L 50.0Xylene (Total)100 06/16/21 07:31 6200B
Surrogate: 4-Bromofluorobenzene 98.0 Limits: 70-130%06/16/21 07:31100 JLB V5426
Surrogate: Dibromofluoromethane 98.6 Limits: 70-130%06/16/21 07:31100 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 93.4 Limits: 70-130%06/16/21 07:31100 JLB V5426
Surrogate: Toluene-d8 84.4 Limits: 70-130%06/16/21 07:31100 JLB V5426
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 37 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:Field Blank
89304 Matrix:
6/8/2021 14:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<10.0 µg/L 10.0Acetone 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Benzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Bromobenzene 1 06/16/21 01:57 6200BJLB
<1.00 µg/L 1.00Bromochloromethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Bromodichloromethane 1 06/16/21 01:57 6200BJLB
<5.00 µg/L 5.00Bromoform 1 06/16/21 01:57 6200BJLB
<1.00 µg/L 1.00Bromomethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500n-Butylbenzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500sec-Butyl benzene 1 06/16/21 01:57 6200BJLB
<2.00 µg/L 2.00tert-Butyl benzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Carbon Tetrachloride 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Chlorobenzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Chlorodibromomethane 1 06/16/21 01:57 6200BJLB
<1.00 µg/L 1.00Chloroethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Chloroform 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Chloromethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5002-Chlorotoluene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5004-Chlorotoluene 1 06/16/21 01:57 6200BJLB
<2.00 µg/L 2.001,2-Dibromo-3-Chloropropane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,2-Dibromoethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Dibromomethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,2-Dichlorobenzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,3-Dichlorobenzene 1 06/16/21 01:57 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 38 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:Field Blank
89304 Matrix:
6/8/2021 14:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.5001,4-Dichlorobenzene 1 06/16/21 01:57 6200BJLB
<5.00 µg/L 5.00Dichlorodifluoromethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,2-Dichloroethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,1-Dichloroethene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500cis-1,2-Dichloroethene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500trans-1,2-Dichloroethene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,2-Dichloropropane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,3-Dichloropropane 1 06/16/21 01:57 6200BJLB
<2.00 µg/L 2.002,2-Dichloropropane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,1-Dichloropropene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500cis-1,3-Dichloropropene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500trans-1,3-Dichloropropene 1 06/16/21 01:57 6200BJLB
<200 µg/L 200Ethanol 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Ethylbenzene 1 06/16/21 01:57 6200BJLB
<3.00 µg/L 3.00Hexachlorobutadiene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Di-Isopropyl Ether (DIPE)1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Isopropylbenzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5004-Isopropyl toluene 1 06/16/21 01:57 6200BJLB
<1.00 µg/L 1.002-Hexanone 1 06/16/21 01:57 6200BJLB
<5.00 µg/L 5.00Methyl Ethyl Ketone (MEK)1 06/16/21 01:57 6200BJLB
<2.00 µg/L 2.00Methylene Chloride 1 06/16/21 01:57 6200BJLB
<1.00 µg/L 1.00Methyl tert-butyl ether (MTBE)1 06/16/21 01:57 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 39 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:Field Blank
89304 Matrix:
6/8/2021 14:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<1.00 µg/L 1.004-Methyl-2-Pentanone 1 06/16/21 01:57 6200BJLB
<1.00 µg/L 1.00Naphthalene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500n-Propylbenzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Styrene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,1,1,2-Tetrachloroethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,1,2,2-Tetrachloroethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Tetrachloroethene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Toluene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichlorobenzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,2,4-Trichlorobenzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,1,1-Trichloroethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,1,2-Trichloroethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Trichloroethene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Trichlorofluoromethane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,2,3-Trichloropropane 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,2,4-Trimethylbenzene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.5001,3,5-Trimethylbenzene 1 06/16/21 01:57 6200BJLB
<5.00 µg/L 5.00Vinyl Acetate 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500Vinyl Chloride 1 06/16/21 01:57 6200BJLB
<1.00 µg/L 1.00m,p-Xylene 1 06/16/21 01:57 6200BJLB
<0.500 µg/L 0.500o-Xylene 1 06/16/21 01:57 6200BJLB
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 40 of 50
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 27511
21-160-0004
01221
Withers & Ravenel
115 Mackenan Dr. BUILDING 117
Liz Allyn
Cary
02172214.24 Received : 06/09/2021
Save More #45
Report Date : 06/16/2021
Sample ID :
Lab No :
Sampled:Field Blank
89304 Matrix:
6/8/2021 14:00
Aqueous
Test Results Units MQL By Analytical
Method
Date / Time
Analyzed
DF
<0.500 µg/L 0.500Xylene (Total)1 06/16/21 01:57 6200B
Surrogate: 4-Bromofluorobenzene 97.6 Limits: 70-130%06/16/21 01:571 JLB V5426
Surrogate: Dibromofluoromethane 99.8 Limits: 70-130%06/16/21 01:571 JLB V5426
Surrogate: 1,2-Dichloroethane - d4 95.4 Limits: 70-130%06/16/21 01:571 JLB V5426
Surrogate: Toluene-d8 85.6 Limits: 70-130%06/16/21 01:571 JLB V5426
Qualifiers/
Definitions
Limit ExceededLDilution FactorDF
Method Quantitation LimitMQL
Page 41 of 50
Quality Control Data
21-160-0004Report No:
Project Description:
Client ID:Withers & Ravenel
Save More #45
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V5426QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V5425
Associated Lab Samples: 89296, 89297, 89298, 89299, 89300, 89301, 89302, 89303, 89304
LRB-V5425 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLBlank
ResultUnits
%
Recovery
% Rec
Limits
06/16/21 01:3310.0< 10.0µg/LAcetone
06/16/21 01:330.500< 0.500µg/LBenzene
06/16/21 01:330.500< 0.500µg/LBromobenzene
06/16/21 01:331.00< 1.00µg/LBromochloromethane
06/16/21 01:330.500< 0.500µg/LBromodichloromethane
06/16/21 01:335.00< 5.00µg/LBromoform
06/16/21 01:331.00< 1.00µg/LBromomethane
06/16/21 01:330.500< 0.500µg/Ln-Butylbenzene
06/16/21 01:330.500< 0.500µg/Lsec-Butyl benzene
06/16/21 01:332.00< 2.00µg/Ltert-Butyl benzene
06/16/21 01:330.500< 0.500µg/LCarbon Tetrachloride
06/16/21 01:330.500< 0.500µg/LChlorobenzene
06/16/21 01:330.500< 0.500µg/LChlorodibromomethane
06/16/21 01:331.00< 1.00µg/LChloroethane
06/16/21 01:330.500< 0.500µg/LChloroform
06/16/21 01:330.500< 0.500µg/LChloromethane
06/16/21 01:330.500< 0.500µg/L2-Chlorotoluene
06/16/21 01:330.500< 0.500µg/L4-Chlorotoluene
06/16/21 01:332.00< 2.00µg/L1,2-Dibromo-3-Chloropropane
06/16/21 01:330.500< 0.500µg/L1,2-Dibromoethane
06/16/21 01:330.500< 0.500µg/LDibromomethane
06/16/21 01:330.500< 0.500µg/L1,2-Dichlorobenzene
06/16/21 01:330.500< 0.500µg/L1,3-Dichlorobenzene
06/16/21 01:330.500< 0.500µg/L1,4-Dichlorobenzene
06/16/21 01:335.00< 5.00µg/LDichlorodifluoromethane
06/16/21 01:330.500< 0.500µg/L1,1-Dichloroethane
06/16/21 01:330.500< 0.500µg/L1,2-Dichloroethane
Page 1 of 7Date:06/16/2021 05:14 PM
Page 42 of 50
Quality Control Data
21-160-0004Report No:
Project Description:
Client ID:Withers & Ravenel
Save More #45
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V5426QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V5425
Associated Lab Samples: 89296, 89297, 89298, 89299, 89300, 89301, 89302, 89303, 89304
LRB-V5425 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLBlank
ResultUnits
%
Recovery
% Rec
Limits
06/16/21 01:330.500< 0.500µg/L1,1-Dichloroethene
06/16/21 01:330.500< 0.500µg/Lcis-1,2-Dichloroethene
06/16/21 01:330.500< 0.500µg/Ltrans-1,2-Dichloroethene
06/16/21 01:330.500< 0.500µg/L1,2-Dichloropropane
06/16/21 01:330.500< 0.500µg/L1,3-Dichloropropane
06/16/21 01:332.00< 2.00µg/L2,2-Dichloropropane
06/16/21 01:330.500< 0.500µg/L1,1-Dichloropropene
06/16/21 01:330.500< 0.500µg/Lcis-1,3-Dichloropropene
06/16/21 01:330.500< 0.500µg/Ltrans-1,3-Dichloropropene
06/16/21 01:33200< 200µg/LEthanol
06/16/21 01:330.500< 0.500µg/LEthylbenzene
06/16/21 01:333.00< 3.00µg/LHexachlorobutadiene
06/16/21 01:330.500< 0.500µg/LDi-Isopropyl Ether (DIPE)
06/16/21 01:330.500< 0.500µg/LIsopropylbenzene
06/16/21 01:330.500< 0.500µg/L4-Isopropyl toluene
06/16/21 01:331.00< 1.00µg/L2-Hexanone
06/16/21 01:335.00< 5.00µg/LMethyl Ethyl Ketone (MEK)
06/16/21 01:332.00< 2.00µg/LMethylene Chloride
06/16/21 01:331.00< 1.00µg/LMethyl tert-butyl ether (MTBE)
06/16/21 01:331.00< 1.00µg/L4-Methyl-2-Pentanone
06/16/21 01:331.00< 1.00µg/LNaphthalene
06/16/21 01:330.500< 0.500µg/Ln-Propylbenzene
06/16/21 01:330.500< 0.500µg/LStyrene
06/16/21 01:330.500< 0.500µg/L1,1,1,2-Tetrachloroethane
06/16/21 01:330.500< 0.500µg/L1,1,2,2-Tetrachloroethane
06/16/21 01:330.500< 0.500µg/LTetrachloroethene
06/16/21 01:330.500< 0.500µg/LToluene
Page 2 of 7Date:06/16/2021 05:14 PM
Page 43 of 50
Quality Control Data
21-160-0004Report No:
Project Description:
Client ID:Withers & Ravenel
Save More #45
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V5426QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V5425
Associated Lab Samples: 89296, 89297, 89298, 89299, 89300, 89301, 89302, 89303, 89304
LRB-V5425 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLBlank
ResultUnits
%
Recovery
% Rec
Limits
06/16/21 01:330.500< 0.500µg/L1,2,3-Trichlorobenzene
06/16/21 01:330.500< 0.500µg/L1,2,4-Trichlorobenzene
06/16/21 01:330.500< 0.500µg/L1,1,1-Trichloroethane
06/16/21 01:330.500< 0.500µg/L1,1,2-Trichloroethane
06/16/21 01:330.500< 0.500µg/LTrichloroethene
06/16/21 01:330.500< 0.500µg/LTrichlorofluoromethane
06/16/21 01:330.500< 0.500µg/L1,2,3-Trichloropropane
06/16/21 01:330.500< 0.500µg/L1,2,4-Trimethylbenzene
06/16/21 01:330.500< 0.500µg/L1,3,5-Trimethylbenzene
06/16/21 01:335.00< 5.00µg/LVinyl Acetate
06/16/21 01:330.500< 0.500µg/LVinyl Chloride
06/16/21 01:331.00< 1.00µg/Lm,p-Xylene
06/16/21 01:330.500< 0.500µg/Lo-Xylene
06/16/21 01:334-Bromofluorobenzene (S)97.8 70-130
06/16/21 01:33Dibromofluoromethane (S)98.0 70-130
06/16/21 01:331,2-Dichloroethane - d4 (S)91.0 70-130
06/16/21 01:33Toluene-d8 (S)86.8 70-130
LCS-V5425 LCSD-V5425Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
47.1 11811144.440.0µg/LAcetone 40-160 5.9 20.0
23.5 11811823.620.0µg/LBenzene 70-130 0.4 20.0
18.3 91.591.018.220.0µg/LBromobenzene 70-130 0.5 20.0
24.4 12211823.520.0µg/LBromochloromethane 70-130 3.7 20.0
23.2 11611322.620.0µg/LBromodichloromethane 70-130 2.6 20.0
Page 3 of 7Date:06/16/2021 05:14 PM
Page 44 of 50
Quality Control Data
21-160-0004Report No:
Project Description:
Client ID:Withers & Ravenel
Save More #45
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V5426QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V5425
LCS-V5425 LCSD-V5425Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
20.8 10410120.220.0µg/LBromoform 70-130 2.9 20.0
23.1 11611723.420.0µg/LBromomethane 60-140 1.2 20.0
17.8 89.091.018.220.0µg/Ln-Butylbenzene 70-130 2.2 20.0
17.9 89.591.518.320.0µg/Lsec-Butyl benzene 70-130 2.2 20.0
18.2 91.091.518.320.0µg/Ltert-Butyl benzene 70-130 0.5 20.0
23.6 11811623.120.0µg/LCarbon Tetrachloride 70-130 2.1 20.0
19.5 97.510120.120.0µg/LChlorobenzene 70-130 3.0 20.0
20.7 10410320.520.0µg/LChlorodibromomethane 70-130 0.9 20.0
21.9 11011222.420.0µg/LChloroethane 60-140 2.2 20.0
23.6 11811523.020.0µg/LChloroform 70-130 2.5 20.0
23.7 11911623.120.0µg/LChloromethane 60-140 2.5 20.0
18.2 91.090.518.120.0µg/L2-Chlorotoluene 70-130 0.5 20.0
18.2 91.090.518.120.0µg/L4-Chlorotoluene 70-130 0.5 20.0
20.4 10296.019.220.0µg/L1,2-Dibromo-3-Chloropropane 70-130 6.0 20.0
19.8 99.010120.120.0µg/L1,2-Dibromoethane 70-130 1.5 20.0
24.1 12111823.520.0µg/LDibromomethane 70-130 2.5 20.0
19.2 96.094.018.820.0µg/L1,2-Dichlorobenzene 70-130 2.1 20.0
18.6 93.091.518.320.0µg/L1,3-Dichlorobenzene 70-130 1.6 20.0
18.5 92.592.518.520.0µg/L1,4-Dichlorobenzene 70-130 0.0 20.0
23.5 11811823.620.0µg/LDichlorodifluoromethane 60-140 0.4 20.0
23.4 11711723.420.0µg/L1,1-Dichloroethane 70-130 0.0 20.0
23.8 11911623.220.0µg/L1,2-Dichloroethane 70-130 2.5 20.0
22.8 11411623.120.0µg/L1,1-Dichloroethene 70-130 1.3 20.0
23.4 11711823.620.0µg/Lcis-1,2-Dichloroethene 70-130 0.8 20.0
23.0 11511723.320.0µg/Ltrans-1,2-Dichloroethene 70-130 1.2 20.0
23.2 11611623.220.0µg/L1,2-Dichloropropane 70-130 0.0 20.0
Page 4 of 7Date:06/16/2021 05:14 PM
Page 45 of 50
Quality Control Data
21-160-0004Report No:
Project Description:
Client ID:Withers & Ravenel
Save More #45
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V5426QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V5425
LCS-V5425 LCSD-V5425Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
21.0 10510320.620.0µg/L1,3-Dichloropropane 70-130 1.9 20.0
23.0 11511522.920.0µg/L2,2-Dichloropropane 70-130 0.4 20.0
23.3 11711923.720.0µg/L1,1-Dichloropropene 70-130 1.7 20.0
24.1 12111923.720.0µg/Lcis-1,3-Dichloropropene 70-130 1.6 20.0
24.8 12412023.920.0µg/Ltrans-1,3-Dichloropropene 70-130 3.6 20.0
520 104102511500µg/LEthanol 60-140 1.7 20.0
19.6 98.010120.120.0µg/LEthylbenzene 70-130 2.5 20.0
17.2 86.091.018.220.0µg/LHexachlorobutadiene 70-130 5.6 20.0
23.3 11711322.620.0µg/LDi-Isopropyl Ether (DIPE)70-130 3.0 20.0
18.2 91.092.018.420.0µg/LIsopropylbenzene 70-130 1.0 20.0
17.9 89.591.518.320.0µg/L4-Isopropyl toluene 70-130 2.2 20.0
19.0 95.093.018.620.0µg/L2-Hexanone 60-140 2.1 20.0
23.6 11811923.720.0µg/LMethyl Ethyl Ketone (MEK)60-140 0.4 20.0
22.5 11311322.520.0µg/LMethylene Chloride 70-130 0.0 20.0
24.6 12311823.620.0µg/LMethyl tert-butyl ether (MTBE)70-130 4.1 20.0
23.9 12011021.920.0µg/L4-Methyl-2-Pentanone 60-140 8.7 20.0
19.6 98.097.019.420.0µg/LNaphthalene 70-130 1.0 20.0
17.8 89.090.518.120.0µg/Ln-Propylbenzene 70-130 1.6 20.0
19.7 98.510020.020.0µg/LStyrene 70-130 1.5 20.0
19.5 97.599.019.820.0µg/L1,1,1,2-Tetrachloroethane 70-130 1.5 20.0
19.3 96.593.018.620.0µg/L1,1,2,2-Tetrachloroethane 70-130 3.6 20.0
18.6 93.010120.220.0µg/LTetrachloroethene 70-130 8.2 20.0
22.8 11411523.020.0µg/LToluene 70-130 0.8 20.0
20.1 10110320.620.0µg/L1,2,3-Trichlorobenzene 70-130 2.4 20.0
19.8 99.096.519.320.0µg/L1,2,4-Trichlorobenzene 70-130 2.5 20.0
22.5 11311122.220.0µg/L1,1,1-Trichloroethane 70-130 1.3 20.0
Page 5 of 7Date:06/16/2021 05:14 PM
Page 46 of 50
Quality Control Data
21-160-0004Report No:
Project Description:
Client ID:Withers & Ravenel
Save More #45
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V5426QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V5425
LCS-V5425 LCSD-V5425Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
23.7 11911522.920.0µg/L1,1,2-Trichloroethane 70-130 3.4 20.0
23.4 11712024.020.0µg/LTrichloroethene 70-130 2.5 20.0
23.0 11511523.020.0µg/LTrichlorofluoromethane 60-140 0.0 20.0
19.4 97.093.518.720.0µg/L1,2,3-Trichloropropane 70-130 3.6 20.0
18.1 90.591.518.320.0µg/L1,2,4-Trimethylbenzene 70-130 1.0 20.0
17.9 89.592.018.420.0µg/L1,3,5-Trimethylbenzene 70-130 2.7 20.0
22.5 11311623.220.0µg/LVinyl Acetate 60-140 3.0 20.0
22.6 11311623.120.0µg/LVinyl Chloride 60-140 2.1 20.0
40.0 10010341.040.0µg/Lm,p-Xylene 70-130 2.4 20.0
19.7 98.599.519.920.0µg/Lo-Xylene 70-130 1.0 20.0
97.697.64-Bromofluorobenzene (S)70-130
99.096.6Dibromofluoromethane (S)70-130
99.094.81,2-Dichloroethane - d4 (S)70-130
85.687.4Toluene-d8 (S)70-130
Page 6 of 7Date:06/16/2021 05:14 PM
Page 47 of 50
Quality Control Data
21-160-0004Report No:
Project Description:
Client ID:Withers & Ravenel
Save More #45
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V5442QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V5441
Associated Lab Samples: 89296, 89297
LRB-V5441 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLBlank
ResultUnits
%
Recovery
% Rec
Limits
06/16/21 12:290.500< 0.500µg/LBenzene
06/16/21 12:291.00< 1.00µg/LMethyl tert-butyl ether (MTBE)
06/16/21 12:294-Bromofluorobenzene (S)102 70-130
06/16/21 12:29Dibromofluoromethane (S)101 70-130
06/16/21 12:291,2-Dichloroethane - d4 (S)109 70-130
06/16/21 12:29Toluene-d8 (S)120 70-130
LCS-V5441 LCSD-V5441Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
16.7 83.584.016.820.0µg/LBenzene 70-130 0.5 20.0
16.5 82.580.016.020.0µg/LMethyl tert-butyl ether (MTBE)70-130 3.0 20.0
1001014-Bromofluorobenzene (S)70-130
109108Dibromofluoromethane (S)70-130
1221201,2-Dichloroethane - d4 (S)70-130
119120Toluene-d8 (S)70-130
Page 7 of 7Date:06/16/2021 05:14 PM
Page 48 of 50
Fed Ex
UPS
US Postal
Client
Lab
Courier
Other :
Shipment Receipt Form
Customer Number:
Customer Name:
Report Number:21-160-0004
Withers & Ravenel
01221
Shipping Method
Shipping container/cooler uncompromised?
Thermometer ID:IRT-15 5.2C
Chain of Custody (COC) present?Yes No
Yes No Not Present
Yes No Not Present
Yes No
COC agrees with sample label(s)? Yes No
COC properly completed
Samples in proper containers?
Sample containers intact?
Sufficient sample volume for indicated test(s)?
All samples received within holding time?
Cooler temperature in compliance?
Yes No
Yes No
Yes No
Yes No
Yes No
Yes NoCooler/Samples arrived at the laboratory on ice.
Samples were considered acceptable as cooling
process had begun.
Yes No
Yes No N/A
Yes No N/A
Yes No N/ASoil VOA method 5035 – compliance criteria met
Water - Sample containers properly preserved
Water - VOA vials free of headspace Yes No N/A
Trip Blanks received with VOAs
Low concentration EnCore samplers (48 hr)
High concentration pre-weighed (methanol -14 d) Low conc pre-weighed vials (Sod Bis -14 d)
High concentration container (48 hr)
Custody seals intact on shipping container/cooler?
Custody seals intact on sample bottles?
Number of coolers/boxes received
Yes No
1
Signature:Talon J Yelton Date & Time:06/09/2021 13:05:29
Special precautions or instructions included?
Comments:
Page 49 of 50
Page 50 of 50
WithersRavenel
Our People. Your Success.
APPENDIX D
GENERAL STANDARD OPERATING PROCEDURES
Generalized Standard Operating Procedures (Not All Inclusive)
WithersRavenel
Our People. Your Success.
Soil Sampling, Soil Boring and Monitor Well Installation, Well Development Soil borings are installed utilizing a stainless-steel hand auger, direct-push hydraulic drill or auger rotary
drill using either a macro core™ sampler, hollow stem augers, or air rotary roller cone bit. Soil borings are
typically sampled at discrete intervals from the bucket of a clean stainless steel hand auger, direct push stainless steel sampler with acetate sleeve, or a split barrel sampler. When appropriate, soil samples may be collected from drill cuttings associated with the boring or well installation. Monitor wells are constructed within select soil borings of one, two, or four-inch inside diameter PVC
casing and machine slotted screen in accordance with NCAC Title 15A, Subchapter 02C (Well Construction Standards, Criteria and Standards Applicable to Water Supply and Certain Other Wells). Clean-washed “#2 Torpedo Sand” is typically utilized to fill the boring annulus surrounding the well screen, extending to a minimum of 1-foot above the well screen. A minimum 1-foot thick bentonite clay seal is emplaced above the sand pack and hydrated. Neat cement grout is placed in the remaining annulus
space from the upper portion of the bentonite seal to within 1-foot of surface grade. In coastal plain areas where shallow groundwater is encountered, a variance to construction standards may be employed to ensure the upper portion of the well screen intersects the upper aquifer surface. Wellheads may be completed with either concrete-set flush mounted traffic-bearing steel skirted manholes with bolt down covers or steel above-ground “stick-up” well protectors set in a concrete pad. The monitoring wells are
secured with locking caps. Temporary wells or piezometers may be completed with the PVC riser cut at or above grade, and are abandoned within 24-hours of their installation. Wells may be developed using a bailer, electric submersible pump, pneumatic pump, or peristaltic pump, dependent upon site conditions. When wells are developed by the driller, they may be developed with
any of the methods outlined above, in addition to air or water injection. Soil boring logs and well construction details are typically prepared for presentation in a report appendix. Borings completed in bedrock may be drilled using air rotary, coring, or sonic drilling methods. Groundwater Depth to Water Measurements
Groundwater level measurements are typically obtained using an electronic water level indicator which registers a tone and/or illuminated light when the probe contacts groundwater. Depth to groundwater measurements are obtained by lowering the probe attached to a cable usually marked in 0.01 foot intervals into the well until the probe of the meter intersects the water surface. The measurement from
the top of the riser pipe or top of casing (TOC) to the water level is recorded to the nearest 0.01 foot. The
electronic water level indicator probe and exposed probe cable is decontaminated between measurement locations.
Generalized Standard Operating Procedures (Not All Inclusive)
WithersRavenel
Our People. Your Success.
Free Product Level Measurements Light Non-Aqueous Phase Liquid (LNAPL) or “free product” present on the water table is measured using
an electronic oil/water interface probe. The interface probe has both an audible and illuminating light
that indicate when a liquid level is encountered. The oil/water interface probe registers a solid tone and solidly lit light when LNAPL petroleum product is encountered and a beeping tone flashing light when groundwater is encountered. Depth to LNAPL measurements are obtained by lowering the probe attached to a cable marked in 0.01 foot intervals into the well until the probe of the meter intersects the product or groundwater. The measurements from the top of the riser pipe or TOC to the liquid level are
recorded to the nearest 0.01 foot. The thickness of LNAPL is calculated by subtracting the depth to LNAPL measurement from the depth to groundwater measurement. The electronic interface probe is decontaminated between measurement locations. Soil Sampling and Field Screening
Soil sampling is performed in general accordance with ASTM: 1586-84 where applicable. Sampling procedures are followed to protect the chemical integrity of the soil samples and minimize the potential for cross contamination between sample locations, including discarding of the exterior of the sample which contacts the auger bucket, acetate sleeve, or split barrel sampler, the use of stainless steel sampling
equipment, and the thorough decontamination of sampling apparatus prior to use and between sample locations. Soil samples retained as a part of excavation or other intrusive “digging” activities may be collected from the bucket of excavation equipment or using a hand shovel, if appropriate. Care to collect soil samples
from excavation equipment includes retrieving native soil from material that has not made contact with the excavating equipment. Samples are collected in sealable bags or by directly filling sample containers as described above. Sampling is performed using new, disposable nitrile gloves for each sample location to ensure sample
integrity and minimize the potential for cross contamination or field personnel exposure to contaminants.
Sampling equipment such as hand auger extensions and buckets, direct push samplers, split spoons or shovels, are decontaminated prior to their use in the collection of samples. Samples are placed within laboratory grade sample containers provided by the laboratory to which the
samples are submitted, labeled, sealed, and placed in an ice filled cooler. An aliquot of the sample is
typically placed in a clean sealable bag and allowed to reach ambient air temperature for future screening of volatile vapor content with a photoionization detector (PID), flame-ionization detector (FID) or other portable screening device.
Screening of samples with a PID, FID or other field screening device is performed in accordance with
device manufacturer specifications for screening, following calibration of the instrument based on manufacturer recommended procedures.
Generalized Standard Operating Procedures (Not All Inclusive)
WithersRavenel
Our People. Your Success.
Groundwater Sampling Groundwater samples are generally collected using one of three standard methods – through the use of a
dedicated, disposable bailer, a peristaltic pump or submersible electric pump.
When sampling with a bailer, a minimum of three well volumes of groundwater are extracted from the well as a means of purging, unless the well is purged to a “dry” state prior to the removal of three volumes of water. Prior to collection of the groundwater sample with the bailer, the water level is allowed to recover to within 80% of the original level measured prior to purging.
When sampling with a peristaltic or submersible electric pump, polyethylene (PE) tubing (or equivalent) is emplaced into the screened section of the monitoring well, and the pump is used to extract water through the tubing. When using the either of these methods, general water quality measurements including but not limited to pH, temperature, dissolved oxygen (DO), oxygen reductive potential (ORP), specific
conductivity and turbidity may be used as methods for determining when an adequate purge of the well has been conducted. When water quality parameters are measured, the resulting data are included in well purge forms or field notes specific to each site and sampling point. Following the purging of three well volumes of groundwater (in the case of the bailed well) or stability of
monitored measurements (in the case of the peristaltic or submersible electric pump), the groundwater sample(s) are introduced directly into sample containers provided by the laboratory to which samples are ultimately submitted for analysis. Any samples requiring chemical preservation are contained in pre-preserved container(s) provided by the laboratory.
Sampling is performed using new, disposable nitrile gloves for each sample location to ensure sample integrity and minimize the potential for cross contamination of samples or field personnel exposure to contaminants. Water Supply Well Sampling
Sampling of water supply wells is accomplished through the collection of a representative sample from an in-line water tap or other point accessible for sampling. Where possible, the sample is collected from a point prior to any filtration or point of entry (POE) system which might be installed on a well. In some cases, samples will be collected from both pre and post-POE locations. Prior to the collection of samples
through an in-place sampling point, the tap or sampling port is cleaned with an Alconox® and deionized
water solution, rinsed with deionized water, and again with an isopropyl alcohol (IPA) rinse. In the case of active supply wells (e.g., a well with a useable well pump with an active power supply), the well pump is energized and allowed to run for a minimum of ten (10) minutes time, after which a sample is
contained in laboratory grade sample containers as described in the previous section. Water quality
parameters may be (but are not necessarily) measured in association with the well purging. Supply wells without active power supplies are not generally sampled, as the well seal cannot be compromised by individuals not certified as a well contractor. However, in the case of a well with no
power supply or pump installed, samples could be obtained through the use of a bailer, peristaltic pump or
electric submersible pump.
Generalized Standard Operating Procedures (Not All Inclusive)
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Decontamination Procedures Decontamination procedures employed in the performance of field activities will vary dependent upon
the method(s) of sampling performed at any site, but will generally include the following:
• Remove excess soil/sludge from any sampling equipment as needed, • Wash and scrub the equipment with a phosphate-free detergent such as Alconox® or Liquinox® in a contaminant-free tap water solution. Use a brush to remove particulate matter and surface films as necessary,
• Rinse thoroughly with tap water, • Rinse thoroughly with analyte-free water (deionized water),
Rinse thoroughly with isopropyl alcohol, • Allow the equipment to air dry,
• Prevent inadvertent contamination during storage and transport (accomplished through storage of equipment in foil or plastic bags/sheeting). In the case of disposable bailers and tubing utilized for the purging and sampling of wells, these items may be decontaminated prior to their disposal. In general, no decontamination of these items is necessary
prior to their use in sampling.