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HomeMy WebLinkAboutMO-14414_14414_CA_MRP_20201130_Annual Monitoring ReportPrepared for:
Colonial Pipeline Company
PO Box 87 C
Paw Creek, North Carolina 28130
Annual Groundwater Monitoring Report
Kannapolis Booster Station
Incident Number 14414 & 91340
September 2019 — August 2020
Ark
APEX
5900 Northwoods Business Parkway, Suite 5900-0
Charlotte NC 28269
Prepared by:
Andrew Street, CHMM, RSM
Senior Project Manager
November 30, 2020
Reviewed by:
Tom Naumann, P.G.
Scientist II
NC Geology License No. 2405
Apex Companies, LLC • 5900 Northwoods Business Parkway, Suite 5900-0 • Charlotte, NC 28269 • T 704.799.6390 • apexcos.com
Annual Groundwater Monitoring Report, September 2019 - August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page i
TABLE OF CONTENTS
1.0 INTRODUCTION.................................................................................................................................... 1
2.0 PROJECT BACKGROUND.................................................................................................................. 1
2.1 Historic Site Impacts................................................................................................................. 1
2.2 Recent Site Impacts.................................................................................................................. 2
3.0 FIELD ACTIVITIES................................................................................................................................3
3.1 Groundwater Gauging.............................................................................................................. 3
3.2 Groundwater Sampling and Analysis....................................................................................... 3
3.3 Water Supply Well Sampling and Analysis.............................................................................. 4
4.0 FINDINGS...............................................................................................................................................4
4.1 Well Gauging Results and Groundwater Flow........................................................................ 4
4.2 Groundwater Analytical Results............................................................................................... 5
4.3 Water Supply Well Analytical Results...................................................................................... 6
5.0 REMEDIATION SYSTEM PERFORMANCE........................................................................................7
5.1 Air Sparge Trench Remediation System................................................................................. 7
5.2 Bio-Sparge and Bio-Venting Systems..................................................................................... 7
6.0 CONCLUSIONS AND RECOMMENDATIONS.................................................................................... 7
6.1 Conclusions.............................................................................................................................. 7
6.2 Recommendations....................................................................................................................8
Tables
Table 1
Summary of Groundwater Monitoring Program
Table 2
Summary of Water Supply Well Information
Table 3
Summary of Groundwater Elevation Data
Table 4
Recovery Well Gauging Data
Table 5
Groundwater Sample Analytical Results
Table 6
Water Supply Well Sample Analytical Results
Figures
Figure 1 Site Location Map
Figure 2 Site Plan
Figure 3 Recovery Well Locations — August 6, 2020
Figure 4 Groundwater Potentiometric Surface Map — Surficial Saprolite Unit — August 6, 2020
Figure 5 Benzene Isoconcentration Map — August 6, 2020
Figure 6 Water Supply Well Location Map
Appendices
Appendix A Groundwater Sampling Field Logs
Appendix B Laboratory Analytical Reports
Appendix C Concentration Time Trend Series Graph — MW-13
Annual Groundwater Monitoring Report, September 2019 — August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page 1
1.0 INTRODUCTION
This report summarizes the annual groundwater monitoring activities performed at the Colonial
Pipeline Company (CPC) Kannapolis Booster Station (the `Site') located at 9301 Mooresville Road
in Concord, North Carolina (Figure 1) from September 2019 through August 2020. This report
also describes the remediation systems operations performed during the reporting period in
accordance with the Corrective Action Plans (CAPs) for the Site approved by the North Carolina
Department of Environmental Quality (NCDEQ). Apex Companies, LLC (Apex; dba Apex
Engineering, P.C.) prepared this Annual Groundwater Monitoring Report on behalf of CPC for
submittal to NCDEQ.
2.0 PROJECT BACKGROUND
The facility consists of a control building, a switch gear building, eight electric booster pumps, a 40-
inch diameter pipeline for transporting gasoline products (Line 1), a 36-inch diameter pipeline for
transporting kerosene, diesel fuel, and other fuel oil products (Line 2), and two 21,000-gallon above
ground storage tanks and associated above -ground and below -ground piping and valves. The
facility has been in operation since the 1970s.
2.1 Historic Site Impacts
Formal assessment and remediation activities were initiated at the facility in 1995. Three areas of
concern were identified at the facility including: (i) the Line 2 Manifold Area; (ii) the Line 1 Manifold
Area; and, (iii) the Line 1 Pig Signal Area. Impacts identified during the 1995 assessment are
included in Incident Number 14414 (Figure 2).
Petroleum impacts in the Line 2 Manifold Area were the result of a kerosene release. Excavation of
impacted soils was limited due to the presence of pumps, footings, and associated underground
piping and valves. A light non -aqueous phase liquid (LNAPL) recovery system and a soil vapor
extraction (SVE) system were installed and formerly operated in this area.
A dissolved phase plume consisting of gasoline -related compounds was identified in the Line 1
Manifold Area. A limited amount of impacted soil was excavated in this area and an SVE system
was installed and formerly operated in the Line 1 Manifold Area.
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Annual Groundwater Monitoring Report, September 2019 — August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page 2
Gasoline impacted soil was also identified in the Line 1 Pig Signal Area as a result of a release from
a leaking pipe fitting. Approximately 1,000 tons of soil was excavated and thermally treated from this
area. The excavation extended to bedrock, removing the source material; however, the release
resulted in dissolved phase groundwater impacts. An air sparge trench located near the
downgradient property boundary and a non -discharge pump and treat system were installed in the
late-1990s to prevent off -Site migration of petroleum hydrocarbons.
The air sparge trench is currently in operation. The groundwater pump and treatment system were
taken off-line in 2010, following approval from NCDEQ on April 12, 2010. The LNAPL recovery and
SVE systems were taken off-line in 2010, following approval from NCDEQ on September 29, 2010.
2.2 Recent Site Impacts
A 920-gallon petroleum release occurred at the Site on March 13, 2015, when a valve gasket failed
near the Line 2, Unit 4 booster pump. Emergency response and abatement activities were
performed from March 13, 2015 through August 11, 2015. On August 13, 2015, a three -quarter -inch
nipple on Line 2 was struck by a piece of equipment during backfilling operations resulting in a 5,000-
gallon petroleum release over the recently remediated area. Approximately 4,750-gallons of diesel
fuel were recovered during initial response activities and subsequent recovery well evacuation
efforts. Residual soil impacts were detected at areas where additional excavation was not feasible
due to the presence of booster pumps, footings, and associated underground piping and valves.
Approximately 750 tons of petroleum -impacted soil were removed from the release area during the
initial response activities associated with both 2015 releases. Impacts identified during the 2015
assessment are included in Incident Number 91340.
A CAP and CAP Addendum were submitted to NCDEQ on April 15, 2016 and July 12, 2016,
respectively. The CAP documents specify installation and operation of a bio-venting and bio-sparge
system to address residual soil impacts and dissolved phase groundwater impacts. The CAP was
approved on May 6, 2016, and the CAP Addendum was approved on July 28, 2016. The
semiannual groundwater monitoring program for the Site incorporates the groundwater monitoring
programs associated with Incident Numbers 14414 and 91340. A summary of the Groundwater
Monitoring Program for the Site is provided in Table 1.
In a letter from dated October 24, 2019, NCDEQ requested that the next Annual Groundwater
Monitoring Report include a table summarizing nearby water supply well information including
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Annual Groundwater Monitoring Report, September 2019 - August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page 3
ownership, well status, and the access permission status. The requested information is provided in
Table 2.
3.0 FIELD ACTIVITIES
3.1 Groundwater Gauging
Prior to sampling, groundwater monitoring wells were gauged to measure the depth to groundwater
and LNAPL, if present. Upon arriving at the Site, wells were opened and allowed to equilibrate.
Wells were gauged in accordance with the United States Environmental Protection Agency
(USEPA) Region IV Science and Ecosystem Support Division Field Branches Quality System and
Technical Procedures. The wells were gauged in order of potential impact, moving from
upgradient wells, to downgradient wells and finally source area wells. Depths to groundwater and
LNAPL were measured using an electronic oil/water interface probe capable of measuring to an
accuracy of 0.01 feet. The interface probe was thoroughly decontaminated before collecting
measurements at each subsequent monitoring well. On February 18, 2020 and August 6, 2020,
ten monitoring wells (MW-1, MW-4, MW-5, MW-6, MW-8, MW-13, MW-23, MW-24, MW-25, and
MW-25D) and 13 recovery wells (SB-4, SB-6, SB-8, SB-9, SB-10, SB-11, SB-12, SB-14, SB-15,
SB-16, S13-18, RW-1, and RW-2) were gauged. The location of each monitoring well is shown on
Figure 2 and the location of each recovery well is shown on Figure 3.
3.2 Groundwater Sampling and Analysis
During both 2020 sampling events, groundwater samples were collected from seven monitoring wells
(MW-4, MW-6, MW-8, MW-13, MW-24, MW-25, and MW-25D). At each monitoring well, a baseline
set of water quality stabilization data were measured (temperature, pH, specific conductance, and
oxidation reduction potential) and recorded. The total volume of water in each well was calculated
and a minimum of three well volumes were purged from each well prior to collecting each sample
unless the well was purged dry prior to bailing three well volumes. Wells that were purged dry were
sampled following well recharge. All monitoring wells were purged and sampled with disposable
bailers. Groundwater sampling logs documenting the groundwater purging and sampling are
provided in Appendix A.
After purging an adequate volume of water from each well, a sample was retrieved and transferred
to laboratory supplied, pre -preserved containers and immediately placed on ice. Groundwater
samples were transported under standard chain -of -custody procedures to Pace Analytical
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Annual Groundwater Monitoring Report, September 2019 — August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page 4
Services, LLC of West Columbia, South Carolina. Groundwater samples collected from monitoring
wells MW-4, MW-6, MW-8, and MW-13 were analyzed for benzene, toluene, ethylbenzene, and
xylenes (BTEX) and methyl tert-butyl ether (MTBE) by Environmental Protection Agency (EPA)
Method 602 — purgeable aromatics SM 6200B. Groundwater samples collected from monitoring
wells MW-24, MW-25, and MW-25D were analyzed for BTEX by EPA Method 602 — purgeable
aromatics SM 6200B; semi -volatile organic compounds by EPA Method 625.1; and Massachusetts
Department of Environmental Protection (MADEP) extractable petroleum hydrocarbons (EPH) and
volatile petroleum hydrocarbons (VPH) in consideration of the diesel releases that occurred on
March 13, 2015 and August 13, 2015.
Two quality assurance/quality control samples were collected and analyzed for BTEX and MTBE
by EPA Method 602. During the February 2020 and August 2020 sampling events, DUP-1 was
collected as a duplicate sample of MW-8 and MW-4, respectively. EB-1 was an equipment blank
collected during both sampling events by pouring de -ionized water over an interface probe
following the completion of sampling activities.
3.3 Water Supply Well Sampling and Analysis
Annual water supply well sampling was performed by CPC personnel in the Site vicinity on October
16, 2020. CPC provides point -of -entry (POE) treatment systems (i.e., activated carbon vessels) at
several water supply wells. Seven water supply wells were sampled during the October 16, 2020
sampling event. Samples were collected in laboratory supplied containers, placed in an ice -filled
cooler, and transferred to Waypoint Analytical of Charlotte, North Carolina under chain -of -custody
procedures for analysis of BTEX, MTBE, and naphthalene by EPA Method 8260D.
4.0 FINDINGS
4.1 Well Gauging Results and Groundwater Flow
Depth to water and top of well casing elevation data from the monitoring wells were used to
calculate groundwater elevations relative to an on -Site benchmark referenced to mean sea level
datum. No LNAPL was detected in any of the monitoring wells during the February 18, 2020 or
August 6, 2020 sampling event. A summary of monitoring well gauging data is provided in Table
3.
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Annual Groundwater Monitoring Report, September 2019 — August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page 5
A groundwater potentiometric map for the surficial unit using water level elevation data from the
August 2020 sampling event is provided on Figure 4. The potentiometric map depicts the direction
of groundwater flow to the southeast. A hydraulic gradient of approximately 0.051 feet per foot
was measured between the 720 feet potentiometric contour line near MW-23 and the 705 feet
potentiometric contour line near MW-8. Groundwater flow patterns observed in August 2020 are
consistent with historic sampling events.
LNAPL was detected in recovery well SB-6 at an apparent thickness of 0.04 feet during the
February 18, 2020 sampling event. LNAPL was not detected in any of the recovery wells during the
August 6, 2020 sampling event. A summary of recovery well gauging data is provided in Table 4
4.2 Groundwater Analytical Results
Groundwater sampling activities performed at the Site focused on collecting analytical data from
the upgradient, downgradient, and central plume areas to evaluate Constituents of Concern (COC)
trends over time. The analytical results for groundwater samples collected during this monitoring
period were compared to the 15A NCAC 2L .0202 Groundwater Quality Standards (21- Standards)
and to the 15A NCAC 2B .0215 Surface Water Standards (2B Standards) for a Water Supply II,
High Quality Waters surface water classification. A groundwater isoconcentration map showing the
concentrations of benzene in groundwater monitoring wells during the August 2020 sampling event
is provided as Figure 5. Laboratory analytical reports and chain -of -custody records for the
groundwater samples are presented in Appendix B. A summary of groundwater analytical results
is provided in Table 5.
Notable results from the February 2020 sampling event are summarized below:
■ Benzene was detected at a concentration of 4.8 micrograms per liter (pg/L) in MW-13,
exceeding the 2L and 2B Standards of 1.0 pg/L and 1.19 pg/L, respectively. A graph
illustrating fluctuations in benzene concentrations with time in MW-13 is included in
Appendix C.
■ Benzene was detected at a concentration of 8.3 pg/L in MW-24, exceeding the 2L and 2B
Standards of 1.0 pg/L and 1.19 pg/L, respectively. Benzene concentrations in this well
have typically exceeded the 2L and 2B standards since the 2015 releases.
■ EPH and VPH were detected in MW-24 during the sampling event. Hydrocarbon fractions
C19-C36 Aliphatics were detected at concentrations below the 2B and 2L Standards. C9-
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Annual Groundwater Monitoring Report, September 2019 — August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page 6
C18 Aliphatics and C9-C12 Aliphatics were detected at concentrations of 230 pg/L and 500
pg/L respectively, exceeding the 2B standards for each of 180 pg/L, and the combined 2L
Standard of 700 pg/L for C9-C18 Aromatics. C5-C8 Aliphatics were detected at a
concentration of 1700 pg/L exceeding the 2B and 2L Standards of 400 pg/L and 125 pg/L,
respectively. Hydrocarbon fractions C9-C10 Aromatics were detected at a concentration of
490 pg/L and C11-C22 Aromatics were detected at a concentration of 290 pg/L, exceeding
the combined 2L Standard of 200 pg/L for C9-C22 Aromatics.
■ Ethylbenzene, acenaphthene, fluoranthene, 1-methyl naphthalene, MTBE, naphthalene,
pyrene, toluene, and total xylenes were also detected in one or more monitoring wells at
concentrations below applicable 2L and 2B Standards.
Notable results from the August 2020 sampling event are summarized below:
■ Benzene was detected at a concentration of 4.9 pg/L in MW-24, exceeding the 2L and 2B
Standards of 1.0 pg/L and 1.19 pg/L, respectively.
• EPH and VPH were detected in MW-24 during the sampling event. C9-C12 Aliphatics were
detected at a concentration of 200 pg/L, below 2L Standards but exceeding 2B Standards
of 180 pg/L. C5-C8 Aliphatics were detected at a concentration of 790 pg/L exceeding the
2B and 2L Standards of 125 pg/L and 400 pg/L, respectively. Hydrocarbon fractions C9-
C10 Aromatics were detected at a concentration of 220 pg/L, and C11-C22 Aromatics were
detected at a concentration of 140 pg/L, exceeding the combined 2L Standard of 200 pg/L
for C9-C22 Aromatics.
■ Ethylbenzene, fluoranthene, MTBE, 1-methyl naphthalene, pyrene, di-n-butyl phthalate,
toluene, and total xylenes were also detected in one or more monitoring wells at
concentrations below applicable 2L and 2B Standards.
4.3 Water Supply Well Analytical Results
Laboratory analytical results indicate that no petroleum hydrocarbon constituents were detected in
the water supply wells sampled. A summary of historic and recent water supply well sampling
analytical results is provided in Table 6. Water supply well locations are shown on Figure 6. A
copy of the laboratory analytical report and chain -of -custody records are included in Appendix B.
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Annual Groundwater Monitoring Report, September 2019 — August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page 7
5.0 REMEDIATION SYSTEM PERFORMANCE
5.1 Air Sparge Trench Remediation System
The air sparge trench remediation system was brought on-line in June 1998 to treat shallow
groundwater prior to migration off -Site. The air sparge system continues to operate to aid in the
removal of benzene and MTBE from groundwater in the vicinity of monitoring wells MW-8 and MW-
13. The air sparge trench operated continuously during the reporting period; however, it was shut
down approximately two weeks prior to the August 6, 2020 groundwater sampling event to allow
for collection of representative groundwater samples.
5.2 Bio-Sparge and Bio-Venting Systems
The bio-sparge and bio-venting systems were brought on-line on March 7, 2017 to address soil
and groundwater impacts associated with the 2015 diesel fuel releases. The bio-sparge system
ran continuously during the reporting period. The bio-venting system ran approximately 75% of the
time during the reporting period due to fouling of float switches. Approximately two weeks prior to
the August 6, 2020 groundwater sampling event, the bio-sparge and bio-venting systems were
shut down to allow for collection of representative groundwater samples.
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6.1 Conclusions
During the February 2020 monitoring event, LNAPL was detected in recovery well SB-6. Benzene
was detected above 2L and 2B Standards in monitoring wells MW-13 and MW-24. Detections of
benzene in MW-13 and MW-24 are associated with historic releases at the Site. Benzene
concentrations in MW-13 have decreased overall since 1998. Aliphatic concentrations exceeded
the applicable 2B and 2L standards in MW-24, and Aromatic concentrations exceeded the
applicable 2L Standards. Although 2B Surface Water Standards were exceeded in MW-13 and
MW-24, any discharge of the groundwater plume to surface water would not likely contravene the
surface water standards within the surface water body.
During the August 2020 monitoring event, LNAPL was not detected in groundwater beneath the
Site. Benzene was detected above 2L and 2B Standards in monitoring well MW-24. C9-C12
Aliphatic concentrations exceeded 2B Standards in MW-24, and C5-C8 Aliphatic concentrations
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Annual Groundwater Monitoring Report, September 2019 — August 2020 November 30, 2020
Colonial Pipeline Company, Kannapolis Booster Station Page 8
exceeded applicable 2B and 2L standards. C9-C10 Aromatic concentrations and C11-C22
Aromatic concentrations also exceeded the applicable 2L Standards in MW-24.
Results of the water supply well sampling indicated an absence of petroleum hydrocarbon
constituents in the water supply wells. Colonial will continue to maintain the off -Site POE water
treatment systems and continue annual sampling of select water supply wells.
6.2 Recommendations
On behalf of CPC, Apex recommends the continuation of the semiannual groundwater and annual
private well sampling program. The next sampling event will be performed in February 2021.
APEX
TABLES
�1
APEX
Table 1
Summary of Groundwater Monitoring Program
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Top of Casing
Screen
Total Depth
Analysis
Well ID
Elevation
Interval
Sampling Frequency
(ft. BGS)
(Following Establishment of COCs)
(ft. MSL)
(ft. BGS)
MW-1
717.24
23.5
3.5 - 23.5
NA
NA
MW-2
708.52
103
88 - 103
NA
NA
(MW-2D)
MW-3
716.64
24
4 - 24
NA
NA
MW-4
729.9
28
8 - 28
BTEX and MTBE by EPA Method 602
Semiannual
MW-5
726.87
19
4 -19
NA
NA
MW-6
724.61
15
5-15
BTEX and MTBE by EPA Method 602
Semiannual
MW-7
725.1
58
53 -58
NA
NA
(MW-6D)
MW-8
710.26
20
10 - 20
BTEX and MTBE by EPA Method 602
Semiannual
MW-13
707.35
22
2 - 22
BTEX and MTBE by EPA Method 602
Semiannual
MW-14
707.03
15
3-15
NA
NA
(MW-17)
MW-15
706.23
109
--
NA
NA
MW-16
--
--
--
NA
NA
MW-17
707.45
--
--
NA
NA
(MW-TR1 U)
MW-18
706.79
--
--
NA
NA
(MW-TR1 D)
MW-23
726.70
15
5-15
NA
NA
Page 1 of 2
Table 1
Summary of Groundwater Monitoring Program
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Top of Casing
Screen
Well ID
Elevation
Total Depth
Interval
Analysis
Sampling Frequency
(ft. BGS)
(Following Establishment of COCs)
(ft. MSL)
(ft. BGS)
BTEX by EPA Method 602;
MW-24
724.61
22
12 - 22
SVOCs by EPA Method 625; MADEP VPH
Semiannual
and EPH
BTEX by EPA Method 602;
MW-25
724.32
17
7 - 17
SVOCs by EPA Method 625; MADEP VPH
Semiannual
and EPH
BTEX by EPA Method 602;
MW-25D
724.00
74
69 - 74
SVOCs by EPA Method 625; MADEP VPH
Semiannual
and EPH
Notes:
-- - unknown
ft. - Feet
ft. MSL - Feet above mean sea level
BGS - Below ground surface
COCs - Constituents of Concern
NA - Not Applicable
BTEX - Benzene, toluene, ethylbenzene, and xylenes
MTBE - Methyl tert-butyl ether
EPA - United States Environmental Protection Agency
SVOCs - Semi -volatile Organic Compounds
MADEP - Massachusetts Department of Environmental Protection
VPH - Volatile Petroleum Hydrocarbons
EPH - Extractable Petroleum Hydrocarbons
Page 2 of 2
Table 2
Summary of Water Supply Well Information
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Last Name
First Name
M/M
Well Address
City
Home Phone
Well Access
Status
Well Status/Usage
DW-Allen
Allen
Wendy
Ms.
4658 Windy Road
Concord, NC 28027
(704) 721-0917
Access Granted
No system installed.
DW-Bethpage Presbyterian
Church
Bethpage Presbyterian
Church
8701 Mooresville Road
Concord, NC 28027
(704) 933-2209
Access Granted
No system installed.
DW-Boan
Boan
Robin
Ms.
9500 Mooresville Road
Concord, NC 28027
704 786-4786
Access Granted
Nos stem installed.
DW-Brasin ton
Brasin ton
R.
Mr.
5557 Castle Road
Concord, NC 28027
704 786-7498
Access Granted
Nos stem installed.
DW-Brooks
Brooks
Cyrus
Mr.
5879 Alexander Road
Concord, NC 28027
704 938-3516
Access Granted
Nos stem installed.
DW-Buchanan
Buchanan
Kelly
Mrs.
8913 Gentry Lane
Concord, NC 28027
980 521-0676
Access Granted
Bottled water provided
DW-Cain
Aldag
Zachary
Mr.
8806 Mooresville Road
Concord, NC 28027
Access Granted
System
DW-Cain-Influent
DW-Cain-Effluent
DW-Cheeseman
Cheeseman
Rene
Ms.
5565 Castle Road
Concord, NC 28027
(704) 795-1343
Access Granted
No system installed.
DW-Childers
Childers
John
Mr.
4920 Wakefield Drive
Concord, NC 28027
(704) 782-9595
Access Granted
Nos stem installed.
DW-Childers-Influent
Access Granted
Nos stem installed.
DW-Clark
Clark
Francis
Mr.
9110 Mooresville Road
Concord, NC 28027
CPC Not
Permitted to
Access
No system installed.
DW-Cook
Coren
Everett
Mr.
9261 Mooresville Road
Concord, NC 28027
(704) 782-6378
Access Granted
System
DW-Cook-Effluent
DW-Cook-Influent
DW-Coren
Coren
Everett
Mr.
9221 Mooresville Road
Concord, NC 28027
(704) 786-4322
Access Granted
System. Bottled Water Provided.
DW-Coren-Influent
DW-Crainshaw
Crainshaw
Frank
Mr.
4675 Windy Road
Concord, NC 28027
704 786-3570
Access Granted
Nos stem installed.
DW-Crowe (MW-16)(')
Well No Longer Sampled - Owner Information Outdated
DW-Deaton
Deaton
John
Mr.
8899 Mooresville Road
Concord, NC 28027
704 788-8395
Access Granted
Nos stem installed.
DW-Daughtery
Daughtery
Karen
Ms.
9417 Gilbrook Road
Davidson, NC 28036
704 789-9359
Access Granted
Nos stem installed.
DW-Ellis
Ellis
Shane
Ms.
5020 Wakefield Drive
Concord, NC 28027
704 614-1331
Access Granted
System, bottled water provided.
DW-Elwood
Elwood
Mr. and Ms.
8820 Saxon Drive
Concord, NC 28027
(704) 786-5777
Access Granted
No system installed.
DW-Elwood-D
DW-Emerson
Emerson
Mr. and Ms.
9014 Mooresville Road
Concord, NC 28027
(704) 788-8390
Access Granted
System. Bottled Water Provided.
DW-Emerson-Effluent
DW-Emerson-Influent
DW-Franklin
Franklin
Hoe
Ms.
4412 Robins Nest Road
1 Concord, NC 28027
704 720-0517
Access Granted
Nos stem installed.
GW-Gaultney
Well No Longer Sampled - Owner Information Outdated
DW-Goodnight-New
Goodnight
Ed
Mr.
8907 Mooresville Road
Concord, NC 28027
(704) 786-8916
Access Granted
System. Bottled Water Provided.
DW-Goodnight-New-CV-1
DW-Goodnight-New-CV-2
DW-Goodnight-New-Influent
DW-Goodnight-Old
DW-Goodnight-Old-CV-1
DW-Goodnight-Old-CV-2
DW-Goodnight-Old-Influent
DW-Guenot
Guenot
Chris
Mr.
8912 Mooresville Road
Concord, NC 28027
Access Granted
System
DW-Harwood
Harwood
John
Mr.
5411 Sheridan Drive
Concord, NC 28027
704 786-1761
Access Granted
Nos stem installed.
DW-Johnston
Johnston
Rick
Mr.
4675 Windy Road
Concord, NC 28027
704 782-2478
Access Granted
Nos stem installed.
DW-Kann-Station(')
Colonial Pipeline Booster Station Well
DW-Keasler
Well No Longer Sampled - Owner Information Outdated
DW-Keenan
Watts
Lester
Mr.
9171 Mooresville Road
Concord, NC 28027
(704) 786-6686
Access Granted
System
DW-Keenan-Influent
DW-Kissiah
Kissiah
David
Mr.
4425 Robins Nest Road
Concord, NC 28027
704 792-9240
Access Granted
Nos stem installed.
DW-Laws
Laws
Jamie
Ms.
5220 Norwood Drive
ConcordNC 28027
,
Access Granted
Nos stem installed.
DW-Laws-Influent
Laws
Warren
Mr.
5212 Norwood Drive
704 786-8906
Access Granted
System
DW-Lunsford-D
Lunsford
Wayne
Mr.
8450 Mooresville Road
Concord, NC 28027
704 782-7495
Access Granted
Nos stem installed.
DW-Luther
Luther
Larry
Mr.
9191 Mooresville Road
Concord, NC 28027
(704) 786-7791
Access Granted
System. Bottled Water Provided.
DW-Luther-Effluent
Page 1 of 2
Table 2
Summary of Water Supply Well Information
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Last Name
First Name
M/M
Well Address
city
Home Phone
Well Access
Status
Well Status/Usage
DW-MacAnult -Influent
MacAnulty
Debbie
Ms.
5314 Sheridan Drive
Concord, NC 28027
704 788-1748
Access Granted
System. Bottled Water Provided.
DW-Maurer-CV-1
Maurer
David
Mr.
5111 Wakefield Drive
Concord, NC 28027
(704) 792-1902
Access Granted
System
DW-Maurer-CV-2
DW-Maurer
DW-Maurer-Influent
DW-Messimer-D
Mesimer
Larry
Mr.
5601 Alexander Road
Concord, NC 28027
(704) 425-2580
Access Granted
No system installed.
DW-Messimer-H
DW-Messimer-K
DW-Michael
Well No Longer Sampled - Owner Information Outdated
DW-MurphyMurphy
Duard
Mr.
9560 Barnett Road
Concord, NC 28027
704 786-4489
Access Granted
Nos stem installed.
DW-M ers
Myers
William
Mr.
1010 Dakota Street
Kannapolis, NC 28083
(704) 938-8117
Access Granted
No system installed.
DW-M ers-CV-1
DW-M ers-CV-2
DW-M ers-Influent
DW-Owens
Owens
Steve
Mr.
5221 Sheridan Drive
Concord, NC 28027
704 786-8747
Access Granted
Nos stem installed.
DW-Parker
Parker
Wayne
Mr.
4650 Windy Road
Concord, NC 28027
704 782-2463
Access Granted
Nos stem installed.
DW-Porter
Porter
Cecil
Mr.
8600 Mooresville Road
Concord, NC 28027
704 720-0846
1 Access Granted
System
DW-Poteat
Poteat
Keith
Mr.
4930 Wakefield Drive
Concord, NC 28027
704 782-4535
Access Granted
Nos stem installed.
DW-Preslar
Preslar
Mr.
5355 Norwood Road
Concord, NC 28027
704 723-9617
Access Granted
Nos stem installed.
DW-Re nolds
Reynolds
Pat
Mrs.
4401 Robins Nest Road
Concord, NC 28027
704 795-5152
Access Granted
Nos stem installed.
DW-Rhodes
Rhodes
Jim
Mr.
5300 Sheridan Drive
Concord, NC 28027
704 786-5269
Access Granted
Nos stem installed.
DW-Schaffner-Influent
Shaffner
James
Mr.
4930 Wakefield Drive
Concord, NC 28027
Access Granted
Nos stem installed.
DW-Schroeder
Schroeder
Don
Mr.
5361 Lynchburg Drive
Concord, NC 28027
704 938-1513
Access Granted
Nos stem installed.
DW-Shinn
Well No Longer Sampled - Owner Information Outdated
DW-Smith
Smith
Elizabeth
Ms.
9405 Mooresville Road
Concord, NC 28027
704 786-9284
Access Granted
System
DW-Smith-David
Smith
David
Mr.
8912 Gentry Drive
Concord, NC 28027
704 723-9617
Access Granted
Nos stem installed.
DW-Smith-Influent
Smith
Elizabeth
Ms.
9405 Mooresville Road
Concord, NC 28027
704 786-9284
Access Granted
System
DW-Snyder
Snyder
Mr. and Mrs.
9059 Sandburg Drive
Concord, NC 28027
704 785-8336
Access Granted
3 families
DW-Teal
Teal
Ralph
Mr.
5129 Norwood Drive
Concord, NC 28027
(704) 787-9483
Access Granted
Bottle Water Provided
DW-Teal-Effluent
DW-Teal-Influent
DW-Tucker
Guenot
Chris
Mr.
8912 Mooresville Road
Concord, NC 28027
(704) 786-6686
Access Granted
System
DW-Tucker-CV-1
DW-Tucker-CV-2
D W -Tucker-Infl uent(3)
DW-Wally
Wally
Cindy
Ms.
10800 Mooresville Road
Davidson, NC 28036
704 784-4094
Access Granted
Nos stem installed.
DW-Ware
Access Granted
Nos stem installed.
DW-Watts
Watts
Lester
Mr.
9171/8916 Mooresville
Road
Concord, NC 28027
(704) 786-6686 /
(704) 784-2488
Access Granted
System. Bottled Water Provided.
DW-Watts-CV-1
DW-Watts-CV-2
DW-Watts-New-CV-2
DW-Watts-Influent
DW-Watts-New-Influent
DW-Wilkinson
Wilkinson
Jimmy
Mr.
9403 Mooresville Road
Concord, NC 28027
(704) 786-1424
Access Granted
System Removed per owner request.
Bottled water provided.
DW-Wright
Wright
Kath
Ms.
9202 Casey Drive
I Concord, NC 28027
704 720-9204
1 Access Granted
Notes:
CV-1 = 1 st carbon vessel effluent.
CV-2 = 2nd carbon vessel effluent
Influent = For point of entry system
Effluent = For pont of entry system.
(1) = DW-Crowe (MW-16) used as monitoring well only.
(2) = New well installed in 2010.
(3) = Tucker sold to Stief 3/2014.
Page 2 of 2
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
M W-1
1 /31 /2001
717.24
6.70
710.54
2/7/2001
6.84
710.40
2/8/2001
6.80
710.44
2/9/2001
6.74
710.50
2/14/2001
6.22
711.02
2/21 /2001
6.54
710.70
8/16/2001
6.75
710.49
2/27/2002
6.32
710.92
8/28/2002
7.43
709.81
2/18/2003
5.15
712.09
8/18/2003
5.63
711.61
2/19/2004
5.45
711.79
8/17/2004
6.34
710.90
2/23/2005
5.64
711.60
8/16/2005
6.50
710.74
2/22/2006
5.85
711.39
8/16/2006
4.05
713.19
2/20/2007
5.78
711.46
8/15/2007
7.08
710.16
2/25/2008
6.20
711.04
8/27/2008
4.85
712.39
8/12/2010
6.18
711.06
9/8/2011
7.15
710.09
2/13/2012
6.14
711.10
8/3/2012
NM
NM
2/4/2013
6.3
710.94
2/19/2014
5.06
712.18
8/25/2014
6.67
710.57
2/23/2015
5.96
711.28
8/18/2015
7.57
709.67
12/3/2015
5.10
712.14
2/16/2016
4.29
712.95
8/19/2016
6.71
710.53
2/7/2017
6.46
710.78
8/15/2017
7.00
710.24
2/1/2018
6.29
710.95
8/16/2018
6.32
710.92
2/15/2019
5.95
711.29
8/8/2019
7.09
710.15
2/18/2020
5.40
711.84
8/6/2020
6.30
710.94
Page 1 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-2 (MW-2D)
1/31/2001
708.52
3.40
705.12
2/7/2001
13.80
694.72
2/8/2001
13.50
695.02
2/9/2001
12.97
695.55
2/14/2001
13.25
695.27
2/21 /2001
13.72
694.80
7/23/2001
14.15
694.37
8/16/2001
14.30
694.22
8/20/2001
5.83
702.69
8/22/2001
9.20
699.32
2/27/2002
10.50
698.02
8/28/2002
10.60
697.92
2/18/2003
9.63
698.89
8/18/2003
6.68
701.84
2/19/2004
11.35
697.17
8/17/2004
4.70
703.82
2/23/2005
12.49
696.03
12/3/2015
3.58
704.94
MW-3
1 /31 /2001
716.64
11.48
705.16
2/7/2001
11.86
704.78
2/8/2001
12.15
704.49
2/9/2001
12.48
704.16
2/14/2001
13.04
703.60
2/21 /2001
13.40
703.24
8/16/2001
13.30
703.34
2/27/2002
11.15
705.49
8/28/2002
13.95
702.69
2/18/2003
10.28
706.36
8/18/2003
9.17
707.47
2/19/2004
9.28
707.36
8/17/2004
10.61
706.03
2/23/2005
10.77
705.87
12/3/2015
9.33
707.31
MW-4
1 /31 /2001
729.9
15.57
714.33
2/7/2001
15.58
714.32
2/8/2001
15.51
714.39
2/9/2001
14.90
715.00
2/12/2001
14.07
715.83
2/14/2001
13.45
716.45
2/16/2001
12.80
717.10
2/21 /2001
7.00
722.90
2/27/2001
6.70
723.20
3/2/2001
6.85
723.05
3/9/2001
4.97
724.93
3/19/2001
5.02
724.88
3/26/2001
5.65
724.25
4/2/2001
5.00
724.90
Page 2 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-4 continued
4/9/2001
729.9
3.80
726.10
4/16/2001
5.00
724.90
4/23/2001
4.04
725.86
4/27/2001
3.65
726.25
5/1 /2001
4.35
725.55
5/21 /2001
5.33
724.57
6/13/2001
4.75
725.15
7/3/2001
3.64
726.26
7/19/2001
4.10
725.80
7/23/2001
3.58
726.32
7/30/2001
4.30
725.60
8/14/2001
3.55
726.35
8/16/2001
3.30
726.60
9/5/2001
4.62
725.28
9/11/2001
4.50
725.40
10/11/2001
5.20
724.70
11 /7/2001
5.62
724.28
11 /21 /2001
5.26
724.64
12/18/2001
3.35
726.55
12/27/2001
4.65
725.25
1/17/2002
6.16
723.74
2/26/2002
4.50
725.40
2/27/2002
4.75
725.15
3/14/2002
5.40
724.50
4/26/2002
6.75
723.15
5/10/2002
5.70
724.20
5/28/2002
3.80
726.10
6/19/2002
4.90
725.00
7/3/2002
5.85
724.05
8/20/2002
5.80
724.10
8/28/2002
5.80
724.10
2/18/2003
4.38
725.52
3/17/2003
3.55
726.35
4/28/2003
3.80
726.10
5/19/2003
3.30
726.60
6/5/2003
3.75
726.15
7/7/2003
4.38
725.52
8/18/2003
4.73
725.17
9/5/2003
5.10
724.80
10/6/2003
4.70
725.20
11 /21 /2003
4.90
725.00
12/8/2003
4.30
725.60
1 /29/2004
4.48
725.42
2/19/2004
4.50
725.40
3/9/2004
4.90
725.00
Page 3 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-4 continued
4/6/2004
729.9
4.00
725.90
5/7/2004
4.64
725.26
6/8/2004
4.66
725.24
7/22/2004
7.62
722.28
8/10/2004
7.15
722.75
8/17/2004
7.73
722.17
9/9/2004
6.40
723.50
2/23/2005
3.51
726.39
3/23/2005
6.95
722.95
4/11/2005
4.35
725.55
5/5/2005
3.94
725.96
6/23/2005
3.80
726.10
7/7/2005
3.90
726.00
8/16/2005
5.50
724.40
9/9/2005
5.40
724.50
10/18/2005
5.82
724.08
11 /9/2005
6.70
723.20
12/20/2005
3.55
726.35
1 / 18/2006
4.33
725.57
2/22/2006
5.32
724.58
2/20/2007
5.54
724.36
8/15/2007
8.45
721.45
2/25/2008
4.46
725.44
8/27/2008
4.90
725.00
2/11/2009
8.66
721.24
8/20/2009
9.08
720.82
2/4/2010
6.06
723.84
8/12/2010
9.87
720.03
2/15/2011
11.73
718.17
9/8/2011
13.82
716.08
2/13/2012
10.76
719.14
8/3/2012
12.87
717.03
2/4/2013
13.12
716.78
2/19/2014
10.12
719.78
8/25/2014
11.03
718.87
2/23/2015
11.39
718.51
8/18/2015
13.96
715.94
12/3/2015
10.26
719.64
2/16/2016
8.46
721.44
8/19/2016
11.34
718.56
2/7/2017
12.01
717.89
8/15/2017
11.74
718.16
2/1/2018
13.56
716.34
8/16/2018
12.2
717.70
2/15/2019
7.79
722.11
8/8/2019
10.65
719.25
2/18/2020
7.65
722.25
8/6/2020
8.50
721.40
Page 4 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-5
2/23/2001
726.87
13.27
713.60
2/27/2002
10.35
716.52
2/18/2003
9.50
717.37
8/17/2004
9.85
717.02
2/23/2005
9.24
717.63
8/12/2010
10.32
716.55
9/8/2011
12.34
714.53
2/13/2012
10.97
715.90
8/3/2012
NM
NM
2/4/2013
12.39
714.48
2/19/2014
10.76
716.11
8/25/2014
11.68
715.19
2/23/2015
11.41
715.46
8/18/2015
13.14
713.73
12/3/2015
10.02
716.85
2/16/2016
9.65
717.22
8/19/2016
11.22
715.65
2/7/2017
12.02
714.85
8/15/2017
11.94
714.93
2/1/2018
12.76
714.11
8/16/2018
11.02
715.85
2/15/2019
9.73
717.14
8/8/2019
11.69
715.18
2/18/2020
8.75
718.12
8/6/2020
9.87
717.00
MW-6
1 /31 /2001
724.61
15.10
709.51
2/7/2001
15.18
709.43
2/8/2001
15.17
709.44
2/9/2001
15.18
709.43
2/14/2001
15.18
709.43
2/21 /2001
15.18
709.43
8/16/2001
15.52
709.09
2/27/2002
14.00
710.61
8/28/2002*
30.45
694.16
2/18/2003
13.17
711.44
8/18/2003
11.62
712.99
2/19/2004
12.17
712.44
8/17/2004
12.98
711.63
2/23/2005
13.28
711.33
8/16/2005
12.97
711.64
2/22/2006
11.98
712.63
8/16/2006
12.55
712.06
2/20/2007
11.90
712.71
8/15/2007
14.23
710.38
2/25/2008
13.10
711.51
Page 5 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-6 continued
8/27/2008
724.61
12.78
711.83
2/11/2009
13.27
711.34
8/20/2009
13.86
710.75
2/4/2010
13.75
710.86
8/12/2010
12.15
712.46
2/15/2011
13.09
711.52
9/8/2011
DRY
DRY
2/13/2012
12.42
712.19
8/3/2012
13.66
710.95
2/4/2013
13.61
711.00
2/19/2014
12.02
712.59
8/25/2014
13.31
711.30
2/23/2015
13.01
711.60
8/18/2015
14.50
710.11
12/3/2015
11.63
712.98
2/16/2016
11.24
713.37
8/19/2016
13.05
711.56
2/7/2017
13.35
711.26
8/15/2017
13.36
711.25
2/1/2018
14.28
710.33
8/16/2018
12.93
711.68
2/15/2019
11.67
712.94
8/8/2019
13.50
711.11
2/18/2020
10.12
714.49
8/6/2020
11.80
712.81
MW-7 (MW-6D)
1/31/2001
725.52
21.40
704.12
2/7/2001
30.48
695.04
2/8/2001
30.40
695.12
2/9/2001
29.23
696.29
2/14/2001
30.12
695.40
2/21 /2001
30.60
694.92
7/23/2001
31.02
694.50
8/16/2001
31.15
694.37
8/20/2001
22.75
702.77
8/22/2001
26.12
699.40
2/27/2002
27.40
698.12
8/28/2002A
14.62
710.90
2/18/2003
26.50
699.02
8/18/2003
23.60
701.92
2/19/2004
28.17
697.35
8/17/2004
21.69
703.83
2/23/2005
29.37
696.15
8/16/2005
28.75
696.77
2/22/2006
25.10
700.42
8/16/2006
28.75
696.77
2/20/2007
26.68
698.84
8/15/2007
28.68
696.84
2/25/2008A
13.10
712.42
8/27/2008
28.60
696.92
9/8/2011
23.76
701.76
2/13/2012
21.12
704.40
8/3/2012
NM
NM
2/4/2013
21.69
703.83
Page 6 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-7 (MW-6D) Continued
8/18/2015
725.52
NM
NM
12/3/2015
20.38
705.14
MW-8
1 /31 /2001
710.26
1
6.72
703.54
2/7/2001
6.80
703.46
2/8/2001
6.97
703.29
2/9/2001
7.08
703.18
2/14/2001
7.20
703.06
2/21 /2001
7.37
702.89
8/16/2001
7.75
702.51
2/27/2002
6.65
703.61
8/28/2002
8.60
701.66
2/18/2003
6.25
704.01
8/18/2003
6.13
704.13
2/19/2004
6.00
704.26
8/17/2004
6.36
703.90
2/23/2005
6.28
703.98
8/16/2005
6.55
703.71
2/22/2006
5.75
704.51
8/16/2006
7.08
703.18
2/20/2007
6.70
703.56
8/15/2007
15.80
694.46
2/25/2008
7.50
702.76
8/27/2008
10.30
699.96
2/11/2009
6.13
704.13
8/20/2009
7.90
702.36
2/4/2010
6.00
704.26
8/12/2010
6.52
703.74
2/15/2011
6.69
703.57
9/8/2011
8.82
701.44
2/13/2012
6.23
704.03
8/3/2012
7.12
703.14
2/4/2013
6.72
703.54
2/19/2014
6.08
704.18
8/25/2014
4.67
705.59
2/23/2015
6.62
703.64
8/18/2015
7.87
702.39
12/3/2015
6.22
704.04
2/16/2016
5.82
704.44
8/19/2016
7.25
703.01
2/7/2017
6.48
703.78
8/15/2017
7.14
703.12
2/1 /2018
6.44
703.82
8/16/2018
7.14
703.12
2/15/2019
6.43
703.83
8/8/2019
7.26
703.00
2/18/2020
6.16
704.10
8/6/2020
6.63
703.63
Page 7 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-9 (MW-9D)
1/31/2001
711.84
7.78
704.06
2/7/2001
12.24
699.60
2/8/2001
15.85
695.99
2/9/2001
15.64
696.20
2/14/2001
15.83
696.01
2/21 /2001
16.25
695.59
8/16/2001
16.95
694.89
8/20/2001
9.20
702.64
8/22/2001
12.25
699.59
2/27/2002
13.20
698.64
8/28/2002
16.40
695.44
2/18/2003
12.46
699.38
8/18/2003
6.94
704.90
2/19/2004
12.75
699.09
8/17/2004
8.04
703.80
2/23/2005
15.13
696.71
MW-10 (MW-10D)
1/31/2001
706.24
3.70
702.54
2/7/2001
3.22
703.02
2/8/2001
3.14
703.10
2/9/2001
3.02
703.22
2/14/2001
3.40
702.84
2/21 /2001
2.50
703.74
8/16/2001
5.75
700.49
2/27/2002
3.80
702.44
8/28/2002
6.90
699.34
2/18/2003
2.30
703.94
2/19/2004
3.55
702.69
2/20/2004
4.55
701.69
8/17/2004
5.03
701.21
2/23/2005
3.54
702.70
MW-11
Abandoned
MW-12 (MW-12D)
1/31/2001
715.94
8.10
707.84
2/7/2001
8.37
707.57
2/8/2001
8.34
707.60
2/9/2001
8.35
707.59
2/14/2001
8.15
707.79
2/21 /2001
7.52
708.42
8/16/2001
9.77
706.17
2/27/2002
7.20
708.74
8/28/2002
10.87
705.07
2/18/2003
5.60
710.34
8/18/2003
6.25
709.69
2/19/2004
5.40
710.54
8/17/2004
9.25
706.69
2/23/2005
5.75
710.19
Page 8 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-13
1/31/2001
707.35
4.00
703.35
2/7/2001
4.63
702.72
2/8/2001
4.75
702.60
2/9/2001
4.75
702.60
2/14/2001
4.69
702.66
2/21 /2001
4.67
702.68
2/27/2002
4.85
702.50
8/28/2002
6.50
700.85
2/18/2003
4.66
702.69
8/18/2003
4.95
702.40
2/19/2004
4.15
703.20
8/17/2004
5.06
702.29
2/23/2005
4.25
703.10
8/16/2005
4.65
702.70
2/22/2006
4.02
703.33
8/16/2006
3.80
703.55
2/20/2007
4.30
703.05
8/15/2007
5.80
701.55
2/25/2008
3.90
703.45
8/27/2008
3.68
703.67
2/ 11 /2009
4.30
703.05
8/20/2009
5.36
701.99
2/4/2010
3.87
703.48
8/12/2010
4.91
702.44
2/15/2011
3.98
703.37
9/8/2011
5.10
702.25
2/13/2012
4.12
703.23
8/3/2012
NM
NM
2/4/2013
3.88
703.47
2/19/2014
3.86
703.49
8/25/2014
4.85
702.50
2/23/2015
4.65
702.70
8/18/2015
5.63
701.72
12/3/2015
3.55
703.80
2/16/2016
3.55
703.80
8/19/2016
4.99
702.36
2/7/2017
4.32
703.03
8/15/2017
4.71
702.64
2/1 /2018
3.69
703.66
8/16/2018
4.6
702.75
2/15/2019
3.91
703.44
8/8/2019
4.49
702.86
2/18/2020
3.62
703.73
8/6/2020
3.94
703.41
Page 9 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-14 (MW-17)
1/31/2001
707.15
4.02
703.13
2/7/2001
4.20
702.95
2/8/2001
4.25
702.90
2/9/2001
4.18
702.97
2/14/2001
4.05
703.10
2/21 /2001
4.15
703.00
8/16/2001
4.80
702.35
2/27/2002
4.35
702.80
8/28/2002
6.10
701.05
2/18/2003
4.00
703.15
8/18/2003
4.25
702.90
2/19/2004
4.50
702.65
8/17/2004
4.55
702.60
2/23/2005
3.53
703.62
12/3/2015
3.51
703.64
MW-15 (MW-17D)
1/31/2001
706.23
2.30
703.93
2/7/2001
23.10
683.13
2/8/2001
22.30
683.93
2/9/2001
16.82
689.41
2/14/2001
21.60
684.63
2/21 /2001
22.90
683.33
7/23/2001
15.15
691.08
8/16/2001
15.20
691.03
8/20/2001
3.60
702.63
8/22/2001
7.85
698.38
2/27/2002
11.00
695.23
2/18/2003
9.70
696.53
8/18/2003
5.90
700.33
2/19/2004
12.58
693.65
8/17/2004
4.00
702.23
2/23/2005
14.80
691.43
8/16/2005
12.20
694.03
2/22/2006
7.95
698.28
8/16/2006
12.20
694.03
2/20/2007
9.82
696.41
8/15/2007
11.90
694.33
8/27/2008
1 12.60
1 693.63
2/11/2009
1 3.04
1 703.19
Page 10 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-16 (Crowe Well)
1/31/2001
718.48
15.10
703.38
2/7/2001
18.40
700.08
2/8/2001
18.95
699.53
2/9/2001
18.60
699.88
2/14/2001
18.80
699.68
2/21 /2001
18.85
699.63
8/16/2001
20.05
698.43
8/20/2001
16.22
702.26
8/22/2001
18.07
700.41
2/27/2002
17.98
700.50
8/28/2002
20.78
697.70
2/18/2003
16.82
701.66
8/18/2003
13.60
704.88
2/19/2004
16.25
702.23
8/17/2004
15.24
703.24
2/23/2005
18.00
700.48
8/16/2005
18.40
700.08
2/22/2006
15.00
703.48
8/16/2006
18.65
699.83
2/20/2007
16.37
702.11
8/15/2007
19.48
699.00
2/25/2008
16.95
701.53
8/27/2008
19.30
699.18
MW-17 (MW-TR1 U)
2/23/2001
707.45
4.45
703.00
8/16/2001
5.10
702.35
2/27/2002
4.15
703.30
8/28/2002
6.35
701.10
2/18/2003
4.35
703.10
2/19/2004
4.00
703.45
8/17/2004
4.71
702.74
2/23/2005
3.68
703.77
12/3/2015
3.51
703.94
MW-18 (MW-TR1 D)
2/23/2001
706.79
3.88
702.91
8/16/2001
4.52
702.27
2/27/2002
4.10
702.69
8/28/2002
5.75
701.04
2/18/2003
3.75
703.04
2/19/2004
3.50
703.29
8/17/2004
4.12
702.67
2/23/2005
3.19
703.60
12/3/2015
3.32
703.47
MW-19 (MW-TR2U)
2/23/2001
707.97
5.18
702.79
8/16/2001
5.77
702.20
2/27/2002
5.45
702.52
8/28/2002
6.95
701.02
2/18/2003
5.05
702.92
2/19/2004
4.60
703.37
8/17/2004
5.62
702.35
2/23/2005
4.19
703.78
Page 11 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-20 (MW-TR2D)
2/23/2001
707.46
4.77
702.69
8/16/2001
5.71
701.75
2/27/2002
5.40
702.06
8/28/2002
7.00
700.46
2/18/2003
4.30
703.16
2/19/2004
4.18
703.28
8/17/2004
5.18
702.28
2/23/2005
4.42
703.04
8/19/2010
5.61
701.85
2/19/2014
4.93
702.53
8/25/2014
5.39
702.07
2/23/2015
4.74
702.72
MW-21 (MW-TR3U)
2/23/2001
711.47
7.46
704.01
8/16/2001
7.90
703.57
2/27/2002
7.00
704.47
8/28/2002
8.60
702.87
2/18/2003
6.85
704.62
2/19/2004
6.80
704.67
8/17/2004
6.86
704.61
2/23/2005
6.80
704.67
MW-22 (MW-TR3D)
2/23/2001
710.84
7.65
703.19
8/16/2001
8.13
702.71
2/27/2002
7.60
703.24
8/28/2002
9.00
701.84
2/18/2003
6.70
704.14
2/19/2004
6.50
704.34
8/17/2004
6.80
704.04
2/23/2005
6.73
704.11
MW-23
12/3/2015
726.70
7.72
718.98
2/16/2016
6.48
720.22
8/19/2016
8.82
717.88
2/7/2017
9.67
717.03
8/15/2017
9.49
717.21
2/1 /2018
11.11
715.59
8/16/2018
9.07
717.63
2/15/2019
6.03
720.67
8/8/2019
8.61
718.09
2/18/2020
5.66
721.04
8/6/2020
6.48
720.22
MW-24
12/3/2015
724.61
6.54
718.07
2/16/2016
6.16
718.45
8/19/2016
7.46
717.15
2/7/2017
8.49
716.12
8/15/2017
7.92
716.69
2/1/2018
9.07
715.54
8/16/2018
7.23
717.38
2/15/2019
5.91
718.70
8/8/2019
8.00
716.61
2/18/2020
5.26
719.35
8/6/2020
6.06
718.55
Page 12 of 13
Table 3
Summary of Groundwater Elevation Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well Number
Date
Elevation of TOC
(ft. MSL)
Depth to Water
(ft.)
Groundwater
Elevation
ft. MSL
MW-25
12/3/2015
724.32
8.34
715.98
2/16/2016
8.11
716.21
8/19/2016
9.28
715.04
2/7/2017
10.60
713.72
8/15/2017
10.28
714.04
2/1/2018
10.61
713.71
8/16/2018
8.91
715.41
2/15/2019
8.06
716.26
8/8/2019
9.97
714.35
2/18/2020
7.24
717.08
8/6/2020
8.20
716.12
MW-25D
12/3/2015
724.00
1
19.70
704.30
2/16/2016
19.13
704.87
8/19/2016
22.77
701.23
2/7/2017
20.57
703.43
8/15/2017
22.04
701.96
2/1/2018
11.80
712.20
8/16/2018
21.63
702.37
2/15/2019
18.99
705.01
8/8/2019
21.65
702.35
2/18/2020
18.74
705.26
8/6/2020
20.25
703.75
Notes:
TOC elevations obtained from ESP Associates survey (4/2001) and TWT survey (12/2015),
with the exception of MW-15.
Monitor well numbers modified January 2001. Former well designations in parenthesis.
TOC - Top of casing
ft. - Feet
ft. MSL - Feet above mean sea level
* Depth to water exceeds total well depth; wells MW-6 and MW-7 likely mislabeled on gauging notes.
^ Depth to water not consistent with historic values; wells MW-6 and MW-7 likely mislabeled on gauging notes.
Page 13 of 13
Table 4
Recovery Well Gauging Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well
Date
Top of
Casing
Elevation
(ft. MSL)
Well Depth
(ft. BLS)
Depth to
LNAPL
(ft. TOC
( )
Depth to
Water
(ft. TOC
( )
LNAPL
Thickness
(ft.)
(')
Groundwater
Elevation
(ft. MSL
( )
SB-1
8/14/2015
NM
5.0
2.67
4.03
1.36
-
8/15/2015
3.79
4.05
0.26
-
8/17/2015
3.60
4.10
0.50
-
8/18/2015
DRY
-
SB-2
8/14/2015
NM
5.0
2.16
3.78
1.62
-
8/15/2015
3.22
4.00
0.78
-
8/17/2015
3.65
3.85
0.20
-
8/18/2015
DRY
-
SB-3
8/14/2015
NM
5.0
0.99
4.03
3.04
-
8/15/2015
2.64
4.20
1.56
-
8/17/2015
3.99
4.20
0.21
-
8/18/2015
3.95
4.20
0.25
-
8/19/2015
DRY
-
SB-4
8/15/2015
722.57
13.55
7.13
13.27
6.14
713.72
8/17/2015
7.51
13.26
5.75
713.45
8/18/2015
8.48
9.42
0.94
713.83
8/19/2015
8.70
9.40
0.70
713.67
8/20/2015
8.59
9.40
0.81
713.75
8/21 /2015
8.80
9.10
0.30
713.69
8/24/2015
8.50
8.58
0.08
714.05
8/27/2015
8.84
9.01
0.17
713.68
12/16/2015
7.03
7.05
0.02
715.53
2/16/2016
ND
3.45
NA
719.12
8/19/2016
ND
4.42
NA
718.15
2/7/2017
ND
5.91
NA
716.66
8/15/2017
ND
5.64
NA
716.93
2/1/2018
ND
5.33
NA
717.24
8/16/2018
ND
4.21
NA
718.36
2/15/2019
ND
3.32
NA
719.25
8/8/2019
ND
5.12
NA
717.45
2/18/2020
ND
2.09
NA
720.48
8/6/2020
ND
2.50
NA
720.07
SB-5
(Converted to
RW-01)
8/15/2015
NM
11.43
7.11
9.57
2.46
-
8/17/2015
7.49
9.65
2.16
-
8/18/2015
8.61
9.66
1.05
-
8/19/2015
8.92
10.92
2.00
-
8/20/2015
2.50
3.90
1.40
-
8/21 /2015
1.45
1.95
1 0.50
1 -
Page 1 of 8
Table 4
Recovery Well Gauging Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well
Date
Top of
Casing
Elevation
(ft. MSL)
Well Depth
(ft. BLS)
Depth to
LNAPL
(ft. TOC
( )
Depth to
Water
(ft. TOC
( )
LNAPL
Thickness
(ft.)
(')
Groundwater
Elevation
(ft. MSL
( )
S113-6
8/15/2015
723.17
14.7
8.68
10.05
1.37
714.11
8/17/2015
8.44
11.92
3.48
713.76
8/18/2015
8.88
10.04
1.16
713.97
8/19/2015
9.31
9.55
0.24
713.79
8/20/2015
5.64
8.50
2.86
716.73
8/21 /2015
9.04
10.06
1.02
713.84
8/24/2015
8.92
10.47
1.55
713.82
8/27/2015
9.34
9.60
0.26
713.76
12/16/2015
7.03
7.05
0.02
716.13
2/16/2016
ND
5.73
NA
717.44
8/19/2016
6.76
6.77
0.01
716.41
2/7/2017
ND
8.10
NA
715.07
8/15/2017
8.45
8.56
0.11
714.69
2/1 /2018
8.01
8.02
0.01
715.16
8/16/2018
ND
6.32
NA
716.85
2/15/2019
ND
5.15
NA
718.02
8/8/2019
ND
7.52
NA
715.65
2/18/2020
4.69
4.73
0.04
718.44
8/6/2020
ND
5.44
NA
717.73
SB-7
8/15/2015
723.33
9.35
ND
7.50
NA
715.83
8/17/2015
7.68
7.72
0.04
715.64
8/18/2015
7.67
8.09
0.42
715.54
8/19/2015
8.23
8.24
0.01
715.10
8/20/2015
8.29
1 8.30
0.01
715.04
8/21/2015
ND
8.35
NA
714.98
8/24/2015
8.32
8.33
0.01
715.01
8/27/2015
ND
8.12
NA
715.21
12/16/2015
ND
6.05
NA
717.28
2/16/2016
ND
2.88
NA
720.45
8/19/2016
ND
3.32
NA
720.01
2/7/2017
ND
5.55
NA
717.78
Well
Abandoned
Page 2 of 8
Table 4
Recovery Well Gauging Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well
Date
Top of
Casing
Elevation
(ft.MSL)
Well Depth
(ft. BLS)
Depth to
LNAPL
(ft. TOC
( )
Depth to
Water
(ft. TOC
( )
LNAPL
Thickness
(ft.)
(')
Groundwater
Elevation
(ft. MSL
( )
SB-8
8/17/2015
722.60
12.76
ND
8.41
NA
714.19
8/18/2015
ND
8.49
NA
714.11
8/19/2015
ND
8.70
NA
713.90
8/20/2015
ND
8.60
NA
714.00
8/21 /2015
ND
8.62
NA
713.98
8/24/2015
ND
8.56
NA
714.04
8/27/2015
ND
8.75
NA
713.85
12/16/2015
ND
6.22
NA
716.38
2/16/2016
ND
4.70
NA
717.90
8/19/2016
ND
6.13
NA
716.47
2/7/2017
ND
6.89
NA
715.71
8/15/2017
ND
2.51
NA
720.09
2/1/2018
ND
3.60
NA
719.00
8/16/2018
ND
2.61
NA
719.99
2/15/2019
ND
2.68
NA
719.92
8/8/2019
ND
5.50
NA
717.1
2/18/2020
ND
2.16
NA
720.44
8/6/2020
ND
2.58
NA
720.02
SB-9
8/17/2015
722.62
9.75
7.45
9.75
2.30
714.53
8/18/2015
7.91
9.48
1.57
714.27
8/19/2015
8.41
1 9.48
1.07
713.91
8/20/2015
8.33
9.75
1.42
713.89
8/21 /2015
8.43
9.47
1.04
713.90
8/24/2015
8.37
9.54
1.17
713.92
8/27/2015
8.46
9.45
0.99
713.88
12/16/2015
ND
5.96
NA
716.66
2/16/2016
ND
3.60
NA
719.02
8/19/2016
ND
4.28
NA
718.34
2/7/2017
ND
5.64
NA
716.98
8/15/2017
ND
5.34
NA
717.28
2/1/2018
ND
6.37
NA
716.25
8/16/2018
ND
3.94
NA
718.68
2/15/2019
ND
3.63
NA
718.99
8/8/2019
ND
5.58
NA
717.04
2/18/2020
ND
2.92
NA
719.7
8/6/2020
ND
3.52
NA
719.1
Page 3 of 8
Table 4
Recovery Well Gauging Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well
Date
Top of
Casing
Elevation
(ft.MSL)
Well Depth
(ft. BLS)
Depth to
LNAPL
(ft. TOC
( )
Depth to
Water
(ft. TOC
( )
LNAPL
Thickness
(ft.)
(')
Groundwater
Elevation
(ft. MSL
( )
SB-10
8/17/2015
724.35
15.35
ND
10.53
NA
713.82
8/18/2015
ND
10.30
NA
714.05
8/19/2015
ND
10.45
NA
713.90
8/20/2015
ND
10.38
NA
713.97
8/21 /2015
ND
10.40
NA
713.95
8/24/2015
ND
10.32
NA
714.03
8/27/2015
ND
10.50
NA
713.85
12/16/2015
ND
7.99
NA
716.36
2/16/2016
ND
6.49
NA
717.86
8/19/2016
ND
7.75
NA
716.60
2/7/2017
ND
8.73
NA
715.62
8/18/2017
ND
9.49
NA
714.86
2/1/2018
ND
9.13
NA
715.22
8/16/2018
ND
7.34
NA
717.01
2/15/2019
ND
6.29
NA
718.06
8/8/2019
ND
8.51
NA
715.84
2/18/2020
ND
5.50
NA
718.85
8/6/2020
ND
4.94
NA
719.41
SB-11
8/18/2015
725.36
15.19
ND
11.18
NA
714.18
8/19/2015
ND
11.30
NA
714.06
8/20/2015
N D
12.27
NA
713.09
8/21 /2015
N D
11.35
NA
714.01
8/24/2015
N D
11.40
NA
713.96
8/27/2015
ND
11.55
NA
713.81
12/16/2015
ND
8.58
NA
716.78
2/16/2016
ND
6.29
NA
719.07
8/19/2016
ND
8.40
NA
716.96
2/7/2017
ND
8.90
NA
716.46
8/15/2017
ND
9.21
NA
716.15
2/1/2018
ND
9.58
NA
715.78
8/16/2018
ND
8.94
NA
716.42
2/15/2019
ND
6.07
NA
719.29
8/8/2019
ND
8.59
NA
716.77
2/18/2020
ND
5.61
NA
719.75
8/6/2020
ND
6.63
NA
718.73
Page 4 of 8
Table 4
Recovery Well Gauging Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well
Date
Top of
Casing
Elevation
(ft. MSL)
Well Depth
(ft. BLS)
Depth to
LNAPL
(ft. TOC
( )
Depth to
Water
(ft. TOC
( )
LNAPL
Thickness
(ft.)
(')
Groundwater
Elevation
(ft. MSL
( )
SB-12
8/18/2015
722.03
15.8
ND
7.75
NA
714.28
8/19/2015
ND
7.88
NA
714.15
8/20/2015
ND
7.36
NA
714.67
8/21/2015
ND
7.86
NA
714.17
8/24/2015
ND
7.89
NA
714.14
8/27/2015
ND
9.13
NA
712.90
12/16/2015
ND
5.96
NA
716.07
2/16/2016
ND
4.83
NA
717.20
8/19/2016
ND
6.46
NA
715.57
2/7/2017
ND
6.77
NA
715.26
8/15/2017
ND
7.14
NA
714.89
2/1/2018
ND
7.08
NA
714.95
8/16/2018
ND
6.13
NA
715.9
2/15/2019
ND
4.87
NA
717.16
8/8/2019
ND
6.88
NA
715.15
2/18/2020
ND
4.50
NA
717.53
8/6/2020
ND
5.61
NA
716.42
SB-13
8/19/2015
721.26
9
7.29
8.53
1.24
713.62
8/20/2015
7.33
8.45
1.12
713.62
8/21 /2015
7.58
8.65
1.07
713.38
8/24/2015
7.33
8.00
0.67
713.74
8/27/2015
7.45
8.55
1.10
713.50
12/16/2015
ND
5.30
NA
715.96
2/16/2016
ND
1.86
NA
719.40
8/19/2016
ND
3.10
NA
718.16
2/7/2017
ND
4.72
NA
716.54
Well Abandoned
SB-14
8/19/2015
721.69
1
18
7.81
8.10
0.29
713.80
8/20/2015
7.65
8.90
1.25
713.69
8/21 /2015
7.75
7.80
0.05
713.93
8/24/2015
7.86
8.28
0.42
713.71
8/27/2015
7.80
8.33
0.53
713.74
12/16/2015
ND
5.80
NA
715.89
2/16/2016
ND
3.23
NA
718.46
8/19/2016
4.48
4.65
0.17
717.16
2/7/2017
5.50
6.10
0.60
716.02
8/15/2017
ND
5.83
NA
715.86
2/1/2018
ND
5.41
NA
716.28
8/16/2018
ND
3.87
NA
717.82
2/15/2019
Well
not located
8/8/2019
ND 6.26 NA
715.43
2/18/2020
ND
3.39
NA
718.30
8/6/2020
ND
2.68
NA
719.01
Page 5 of 8
Table 4
Recovery Well Gauging Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well
Date
Top of
Casing
Elevation
(ft. MSL)
Well Depth
(ft. BLS)
Depth to
LNAPL
(ft. TOC
( )
Depth to
Water
(ft. TOC
( )
LNAPL
Thickness
(ft.)
(')
Groundwater
Elevation
(ft. MSL
( )
SB-15
8/19/2015
722.76
17.2
8.64
10.28
1.64
713.66
8/20/2015
8.68
9.33
0.65
713.90
8/21/2015
8.78
8.90
0.12
713.95
8/24/2015
8.79
8.84
0.05
713.96
8/27/2015
ND
8.95
NA
713.81
12/16/2015
ND
6.46
NA
716.30
2/16/2016
ND
5.00
NA
717.76
8/19/2016
ND
6.41
NA
716.35
2/7/2017
ND
7.47
NA
715.29
8/15/2017
ND
7.88
NA
714.88
2/1/2018
ND
7.60
NA
715.16
8/16/2018
ND
5.85
NA
716.91
2/15/2019
ND
4.52
NA
718.24
8/8/2019
ND
6.81
NA
715.95
2/18/2020
ND
3.71
NA
719.05
8/6/2020
ND
4.76
NA
718
SB-16
8/20/2015
722.88
12.5
ND
8.90
NA
713.98
8/21/2015
ND
8.85
NA
714.03
8/24/2015
ND
8.80
NA
714.08
8/27/2015
ND
9.00
NA
713.88
12/16/2015
ND
6.47
NA
716.41
2/16/2016
ND
3.24
NA
719.64
8/19/2016
ND
5.21
NA
717.67
2/7/2017
ND
7.21
NA
715.67
8/15/2017
ND
7.76
NA
715.12
2/1/2018
ND
7.53
NA
715.35
8/16/2018
ND
5.48
NA
717.40
2/15/2019
4.35
4.37
0.02
718.52
8/8/2019
ND
6.94
ND
715.94
2/18/2020
ND
2.75
ND
720.13
8/6/2020
ND
4.55
ND
718.33
SB-17
8/20/2015
722.88
13.8
ND
8.95
NA
713.93
8/21/2015
ND
8.95
NA
713.93
8/24/2015
ND
8.88
NA
714.00
8/27/2015
ND
9.09
NA
713.79
12/16/2015
ND
6.90
NA
715.98
2/16/2016
ND
5.79
NA
717.09
8/19/2016
ND
6.80
NA
716.08
2/7/2017
7.57
7.58
1 0.01
1 715.31
Well Abandoned
Page 6 of 8
Table 4
Recovery Well Gauging Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well
Date
Top of
Casing
Elevation
(ft. MSL)
Well Depth
(ft. BLS)
Depth to
LNAPL
(ft. TOC
( )
Depth to
Water
(ft. TOC
( )
LNAPL
Thickness
(ft.)
(')
Groundwater
Elevation
(ft. MSL
( )
SB-18
8/21/2015
721.87
15.8
ND
8.45
NA
713.42
8/24/2015
ND
8.38
NA
713.49
8/27/2015
ND
8.68
NA
713.19
12/16/2015
5.50
8.83
3.33
715.44
2/16/2016
4.20
4.21
0.01
717.67
8/19/2016
6.10
6.35
0.25
715.70
2/7/2017
6.06
6.89
0.83
715.58
8/15/2017
ND
3.20
NA
718.67
2/1/2018
ND
3.12
NA
718.75
8/16/2018
ND
2.32
NA
719.55
2/15/2019
ND
4.34
NA
717.53
8/8/2019
ND
4.34
NA
717.53
2/18/2020
ND
1.20
NA
720.67
8/6/2020
ND
1.65
NA
720.22
SB-19
8/21/2015
723.66
13.33
9.65
10.45
0.80
713.79
8/24/2015
9.67
10.06
0.39
713.88
8/27/2015
9.80
10.00
0.20
713.80
12/16/2015
7.52
7.57
0.05
1 716.13
2/16/2016
ND
4.42
NA
719.24
8/19/2016
5.80
5.95
0.15
717.82
2/7/2017
ND
7.43
NA
716.23
Well Abandoned
RW-1
8/24/2015
722.98
14.3
9.03
9.91
0.88
713.70
8/27/2015
9.20
10.20
1.00
713.50
12/16/2015
ND
6.86
NA
716.12
2/16/2016
ND
4.11
NA
718.87
8/19/2016
ND
5.10
NA
717.88
2/7/2017
ND
7.50
NA
715.48
8/15/2017
ND
6.90
NA
716.08
2/1/2018
ND
8.22
NA
714.76
8/16/2018
ND
4.96
NA
718.02
2/15/2019
ND
2.72
NA
720.26
8/8/2019
ND
6.49
NA
716.49
2/18/2020
ND
3.92
NA
719.06
8/6/2020
ND
5.22
NA
717.76
Page 7 of 8
Table 4
Recovery Well Gauging Data
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well
Date
Top of
Casing
Elevation
(ft. MSL)
Well Depth
(ft. BLS)
Depth to
LNAPL
ft TOC
( )
Depth to
Water
ft TOC
( )
LNAPL
Thickness
ft
(')
Groundwater
Elevation
ft MSL
( )
RW-2
8/24/2015
723.14
15
ND
9.25
NA
713.89
8/27/2015
ND
9.45
NA
713.69
12/16/2015
ND
7.05
NA
716.09
2/16/2016
ND
5.25
NA
717.89
8/19/2016
ND
6.63
NA
716.51
2/7/2017
ND
7.97
NA
715.17
8/15/817
ND
8.06
NA
715.08
2/1/2018
ND
8.53
NA
714.61
8/16/2018
Well
not located
2/15/2019
Well not located
8/8/2019
Well not located
2/18/2020
ND
2.56
NA
720.58
8/6/2020
ND
3.05
NA
720.09
Notes:
ft. - Feet
ft. TOC - Feet below top of casing
ft. BLS - Feet below ground surface
ft. MSL - Feet above mean sea level
LNAPL - Light non -aqueous phase liquid
ND - None detected
NA - Not applicable
1 - Corrected groundwater elevations calculated for wells with LNAPL detections
Page 8 of 8
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
L
Gi
W
(Q
Sample ID
Sample Data
3
m
a
°
.2
N
0
G>
i
K
r
d
Q.
t
t
E
I=
E
I=
N
++
G>
a
N
d
N
�,
W
R
V
`p
C
d
�'
�,
W
�,
�,
ca
G>
fC
+'
ca
Gf
M
�%
00
Ci
N
00
Ci
O
L)
U
N
N
U
N
d
m
d H
V
N
v
L
L.
a
,
m
w
H
X
a
C
a
d
M
t
U
An3
M
a
U-
U-
R
z
t
a
>+
a
t)
O)
0
01
U
t)
O>
V
U
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
125(S)
Surface Water Standard (Ng/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (2)
NE
NE
MW-1
2/25/1998
ND
ND
ND
ND
85
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/1998
ND
ND
ND
ND
97
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/1999
ND
ND
ND
ND
14
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/1999
ND
ND
ND
ND
110
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/2000
ND
ND
ND
ND
ND
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2000
<1.0
<1.0
<1.0
<3.0
160
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
<1.0
<1.0
<1.0
<3.0
9.2
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
<1.0
<1.0
<1.0
<3.0
58
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
<1.0
<1.0
<1.0
<3.0
58
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2002
<1.0
<1.0
<1.0
<1.0
17.8
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2003
<1.0
<1.0
<1.0
<1.0
1.7
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2003
<1.0
<1.0
<1.0
<3.0
40
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2004
<1.0
<1.0
<1.0
<3.0
19
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/17/2004
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2005
<1.0
<1.0
<1.0
<3.0
5.9
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2005
<1.0
<1.0
<1.0
<3.0
16
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/22/2006
<1.0
<1.0
<1.0
<3.0
8.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2006
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/20/2007
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2007
<1.0
<1.0
<1.0
<3.0
6.3
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/25/2008
<0.5
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2008
<0.5
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/3/2015
<1.0
<1.0
<1.0
<1.0
<1.0
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
NA
<100
<75
<75
<25
<100
(MW-2)
10/20/1997
ND
ND
ND
ND
59,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Abandoned
2/25/1998
ND
ND
ND
ND
110,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18-19/98
6
2
ND
ND
71,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/1999
ND
ND
ND
ND
61,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/1999
ND
ND
ND
ND
32,000
NA
NA
NA
NA
I
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/2000
ND
ND
ND
ND
38,000
NA
NA
NA
NA
I NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
3/6/2000
Abandoned
1 of 15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
L
Gi
W
(Q
Sample ID
Sample Data
3
m
a
°
.2
y
0
d
i
K
r
d
!C
Q-
!C
L
fC
t
U
f4
E
E
4)
t
d
N
>,4)
a
a
a
`N
y
4)
C
V
U0a0
CM
U
U
Oa
U
N N
Ua
4)
tW
V
L.
a
d
An
3
R
O)
01
f1
O>
r4)
w
H
M
o
U-
U-
z
a
a
U
0
U
U
U
U
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
12(2)
Surface Water Standard (Ng/L)
1.19
68 ()
11
2
670 ()
2
19 ()
,
70 ()
,
300 ()
0.0028
,
0.32 ()
9.50
,
20 ()
,
50 ()
12
NE
,
20 ()
S
2
180 (S) ()
2
180 (S) ()
NE
NE
MW-2 (MW-2D)
10/20/1997
ND
ND
ND
ND
2,100
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/25/1998
ND
ND
ND
ND
3,500
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18-19/98
ND
ND
ND
ND
2,700
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/1999
ND
ND
ND
ND
4,200
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/1999
ND
ND
ND
ND
3,800
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
11/23/1999
ND
ND
ND
ND
5,900
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/2000
ND
ND
ND
ND
6,300
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2000
<1.0
1.1
<1.0
6.5
4,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1/31/2001
<1.0
<1.0
<1.0
<3.0
1,400
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
<1.0
<1.0
<1.0
<3.0
430
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2002
<1.0
<1.0
<1.0
<1.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2003
<1.0
<1.0
<1.0
<1.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2003
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NNA
NA
NA
NA
NA
NA
NA
2/19/2004
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
N8/17/2004
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/3/2015
<1.0
<1.0
<1.0
<1.0
5.2
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
<75
<75
<100
2of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic
Compounds Method 6200B
Semi Volatile Organic
Compounds Method 625.1
MADEP-EPH/VPH
L
0)
W
(�
Sample ID
Sample Data
Q-
°
r
0
v,
2
41
�
X
r
<C
Q
IC
t
IC
t
�+
c0
E
r
n3
E
c
0
R
t
a
Q
a
a
t
n
0
0
N
C
t
++
41
a
C
0)
d
=
y
41
ar
Q
V
C
0)
�,
W
+,
0
C
fLC
C
M
+-
C
0)
M
:)
00
N
00
O
N
N
N
C
>%
d
3
C
Qi
t m
it L
C
(D
L
Y
N
r-
yT
L
C
0
0
a-
Q)
C
L
U
1
L)
1
U
1
U
1
U
r
0)
m
O
51
0) r
0
i
d
i
y
2
M
i
0)
M
LO
M
co
W
x
��
a
a
m
U
-0
o
U-
U-
z
a
a
U
U
U
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
12(zjS)
Surface Water Standard (fag/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (1)
NE
NE
MW-3
2/25/1998
ND
ND
ND
ND
21
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/1999
ND
ND
ND
ND
590
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/20/1999
ND
ND
ND
ND
170
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/2000
ND
ND
ND
ND
1,400
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2000
<1.0
<1.0
<1.0
<3.0
52
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
<1.0
<1.0
<1.0
<3.0
22
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2002
<1.0
<1.0
<1.0
<1.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2003
<1.0
<1.0
<1.0
<1.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2003
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2004
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/17/2004
<1
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2005
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/4/2015
<1.0
<1.0
<1.0
<1.0
0.83J
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
<75
<25
<100
3of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
Sample ID
Sample Data
d
y
N
�
m
y
c
C
w
d
d
3
IC
o
N
d
G>
x
L
n
i
co
�w _
W
�m
d H
2 2
C
d
R
c
V
a
d
U
R
C
a
m
L
t
`p
N
d
m
C
d
�'
t
U
Gi
t
a
x
41
�,
W
v
N
M
r
t
Q.
�,
�,
o
d
r
++
R
L
U-
G>
d
L
3
U-
M
R
z
d
P
+'
R
t
a
d
i+
a
.2
Q-
M
U
,
U
L
00
U
O)
U
t
N
r
U
�
U
y
U
l4
a
00
U
W)
U
�+
E
O
U
O>
U
r+
E
0
N
N
U
r
U
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
Surface Water Standard (Ng/L)
1.19
68 ()
11
2
670 ()
2
19 ()
,
70 ()
,
300 ()
0.0028
,
0.32 ()
9.50
,
20 ()
,
50 ()
12
NE
,
20 ()
S
2
180 (S) ()
2
180 (S) ()
12(2)
NE
NE
MW-4
1/31/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2002
<1.0
<1.0
<1.0
<1.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2003
<1.0
<1.0
<1.0
<1.0
15.7
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2003
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2004
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/17/2004
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2005
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2005
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/22/2006
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2006
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/20/2007
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2007
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/25/2008
<0.5
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/27/2008
<0.5
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/11/2009
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/20/2009
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/4/2010
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/12/2010
<1.0
<1.0
<1.0
<3.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/15/2011
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
9/8/2011
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/13/2012
<1.0
<1.0
<1.0
<3.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/3/2012
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
4of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
L
Gi
W
(Q
Sample ID
Sample Data
3
m
a
°
.2
y
o
d
i
K
r
d
!C
Q-
!C
L
fC
t
U
f4
E
E
4)
t
d
N
>,4)
a
a
VN
y
4)
4)4)
c
0a0
U
CM
U
ao
C)
Oa
C)
N
NLLI
U
N
4)
m
3
d
d~
c
V
4)w
H
X2
a
C
a
0)
M
t
U
N
M
o
U-
3
U-
R
z
t
a
�+
a
U
0)
C)
(1
U
W)
U
O)
U
C)
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
125(S)
Surface Water Standard (Ng/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (2)
NE
NE
MW-4 continued
2/4/2013
<1.0
<1.0
<1.0
<2.0
1 <1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/29/2013
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2014
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/25/2014
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2015
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2015
<0.5
<0.5
<0.5
<1.5
<0.5
<4.9
<4.9
<4.9
<4.9
<4.9
ND
<4.9
<4.9
NA
<4.9
<4.9
<200
<200
<100
<100
<100
<200
12/3/2015
<1.0
<1.0
<1.0
<1.0
<1.0
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
NA
<2.0
<2.0
<100
<100
151
<75
<25
<100
2/16/2016
<0.5
<0.5
<0.5
<0.5
<0.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/2016
<1.0
<1.0
<1.0
<3.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/7/2017
<1.0
<1.0
<1.0
<3.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2017
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/1/2018
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2018
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/15/2019
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/8/2019
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2020
<0.50
< 0.50
< 0.50
< 0.50
< 0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/6/2020
<0.50
< 0.50
< 0.50
< 0.50
< 0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MW-5
2/23/2005
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/3/2015
<1.0
<1.0
<1.0
I <1.0
<1.0
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
<75
<25
<100
5of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
Sample ID
Sample Data
N
w
H
4)
L
W
3
tW
d
d
V
a
a
m
i
`N
MU
y
Gi
(Q
a
K
4)
An
M
°
r
t
>,4)
o
d
U-
4)
L.
3
U-
R
z
d
a
a
C
a
.2
!C
Q-
V
U
!C
L
U0a0
O)
0
fC
t
a
CM
U
01
U
y
U
f4
a
U
f1
U
0
E
Oa
U
O>
U
E
a
N N
Ua
r4)
U
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
Surface Water Standard (Ng/L)
1.19
68 ()
11
2
670 ()
2
19 ()
,
70 ()
,
300 ()
0.0028
,
0.32 ()
9.50
,
20 ()
,
50 ()
12
NE
,
20 ()
S
2
180 (S) ()
2
180 (S) ()
12(2)
NE
NE
MW-6
2/17/2000
2,000
1500
7,300
14,000
1 30,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2000
2,000
700
3,200
12,000
29,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
9
37
27
240
8,100
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
160
27
32
570
2,600
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2002
<20.0
<20.0
<20.0
<20.0
3,500
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2003
354
<1.0
24.9
209
1,560
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2003
22
<1.0
<1.0
<3.0
400
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2004
260
13
4.6
4.4
410
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/17/2004
260
46
10
31
340
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2005
160
52
<10
<30
76
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2005
370
110
19
30
84
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/22/2006
110
47
<10
<30
120
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2006
240
33
9.8 J
17
58
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/20/2007
150
32
<10
<30
<50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2007
310
63
17
31
68
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/25/2008
130
37
4.5
14.9
95
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2008
170
28
3.3
8.9
230
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/11/2009
13.2
<1.0
<1.0
<2.0
23
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/20/2009
73.7
5
1.4
<2.0
33.1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/4/2010
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/12/2010
<1.0
<1.0
<1.0
<3.0
10.4
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/15/2011
6.5
<1.0
<1.0
<2.0
4.9
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
9/8/2011
NS
NS
NS
NS
NS
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/13/2012
3.6
<1.0
<1.0
<3.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/3/2012
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/4/2013
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/29/2013
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2014
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/25/2014
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2015
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/3/2015
<1.0
<1.0
<1.0
<1.0
<1.0
<2.0
<2.0
<2.0
<2.0
7.3J
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
10J
<25
<100
6of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
L
Gi
W
(Q
Sample ID
Sample Data
3
m
a
°
.2
y
o
d
i
K
r
d
!C
Q-
!C
L
fC
t
U
f4
E
E
4)
t
d
N
>,4)
a
a
VN
y
4)
4)4)
c
0a0
U
CM
U
ao
C)
Oa
C)
N
NLLI
U
N
4)
m
3
d
d~
c
V
4)w
C
0)
t
N
3
R
t
�+
0)
(1
W)
O)
H
X2
a
a
M
U
M
o
U-
U-
z
a
a
U
C)
U
U
U
C)
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
125(S)
Surface Water Standard (Ng/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (2)
NE
NE
MW-6 continued
2/16/2016
<0.5
<0.5
<0.5
<0.5
1 <0.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/2016
<1.0
<1.0
<1.0
<3.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/7/2017
<1.0
<1.0
<1.0
<3.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2017
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/1/2018
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2018
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/15/2019
<0.50
<0.50
<0.50
<0.50
1 <0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/8/2019
66
<0.50
1.0
1.5
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2020
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
j NA
NA
NA
NA
NA
8/6/2020
1 <0.50
<0.50
1 <0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
7of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
Sample ID
Sample Data
mN
4)
4)w
N
C
d
3
H
N
d
X
L
W
3
W
m
d~
d
V
a
C
a
m
i
VN
d
M
�
t
U
Gi
(Q
a
K
4)
v
An3
M
°
r
t
>,4)
o
d
U-
4)
L.
U-
R
z
d
a
t
a
�+
a
.2
!C
Q-
V
,
U
!C
L
C0a0i
O�
C)
fC
t
a
CM
01
U
y
U
f4
a
Ci
O
U
0
E
Oa
O>
U
E
a
N N
U
C)
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
Surface Water Standard (Ng/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (2)
125(S)
NE
NE
MW-7 (MW-6D)
10/25/1995
ND
ND
ND
ND
57,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/12/95
ND
ND
ND
ND
80,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
04/15/97
ND
ND
ND
ND
40,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
07/16/97
ND
ND
ND
ND
42,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
10/20/97
ND
ND
ND
ND
43,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
11/9/1999
ND
ND
ND
ND
25,900
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
11/23/1999
ND
ND
ND
ND
10,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
1/31/2001
<1.0
<1.0
<1.0
<3.0
17,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
<1.0
<1.0
<1.0
<3.0
22,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
4.0
<1.0
<1.0
<3.0
12,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
7.1
<1.0
<1.0
<3.0
15,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2002
<50.0
<50.0
<50.0
<50.0
4,120
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2003
5.1
<1.0
<1.0
<1.0
2,890
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2003
<1.0
<1.0
<1.0
<3.0
38
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2004
6.5
<1.0
<1.0
<3.0
1,800
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/17/2004
<1.0
<1.0
<1.0
<3.0
2.7 J
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2005
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2005
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/22/2006
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2006
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/20/2007
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2007
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NNA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/25/2008
<0.5
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2008
<0.5
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/4/2015
<1.0
<1.0
<1.0
<1.0
2.8
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
12J
<25
<100
8of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic
Compounds Method 6200B
Semi Volatile Organic
Compounds Method 625.1
MADEP-EPH/VPH
N
C
N
C
0)
co
c
C
0)
>%
m
W
d
=
d
3
O
0
y
41
C
Qi
51
x
L
W
R
ar
t m
it L
0) r
��
41
t
Q
C
(D
C1
a
L
Y
i
a
�
V
N
r-
d
m
C
0)
yT
L
i
U
0)
(�
Q-
X
t
�,
W
y
-0
°
r
a
+,
0
C
o
++
C
fLC
0
U-
41
C
0
2
U-
M
a-
M
z
+-
C
Q)
i
a
0)
C
L
a
r
<C
Q
Q
M
:)
IC
t
a
00
U
1
0)
0
IC
t
a
N
L)
1
M
v,
�+
t
n
a
00
U
1
LO
U
2
c0
E
0
O
U
1
M
U
r
n3
E
0
N
N
U
r
U
Sample ID
Sample Data
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
Surface Water Standard (fag/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (1)
12(zjS)
NE
NE
MW-8
2/17/2000
ND
ND
ND
ND
13,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2000
<1.0
<1.0
<1.0
<3.0
26,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
<1.0
<1.0
<1.0
<3.0
500
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
<1.0
<1.0
<1.0
<3.0
69
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
<1.0
<1.0
<1.0
<3.0
680
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2002
<1.0
<1.0
<1.0
<1.0
68.7
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2003
<1.0
<1.0
<1.0
<1.0
2,200
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2003
<1.0
<1.0
<1.0
<3.0
13,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2004
<1.0
<1.0
<1.0
<3.0
80
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/17/2004
<1.0
<1.0
<1.0
<3.0
340
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2005
<10
<10
<10
<30
130
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2005
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/22/2006
<1.0
<1.0
<1.0
<3.0
9,600
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2006
<1.0
<1.0
<1.0
<3.0
860
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/20/2007
<1.0
<1.0
<1.0
<3.0
2,800
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2007
<1.0
<1.0
<1.0
<3.0
1,600
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/25/2008
<0.5
<1.0
<1.0
<3.0
580
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2008
<0.5
<1.0
<1.0
<3.0
640
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/11/2009
<1.0
<1.0
<1.0
<2.0
722
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/20/2009
<1.0
<1.0
<1.0
<2.0
475
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/4/2010
<1.0
<1.0
<1.0
<2.0
231
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/12/2010
<2.0
<2.0
<2.0
<6.0
215
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/15/2011
<1.0
<1.0
<1.0
<2.0
404
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
9/8/2011
<1.0
<1.0
<1.0
<2.0
37.9
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/13/2012
<1.0
<1.0
<1.0
<3.0
28.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/3/2012
<1.0
<1.0
<1.0
<2.0
43.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/4/2013
<1.0
<1.0
<1.0
<2.0
27.1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/29/2013
<1.0
<1.0
<1.0
<2.0
22.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2014
<1.0
<1.0
<1.0
<2.0
3.3
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/25/2014
<1.0
<1.0
<1.0
<2.0
27.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2015
<1.0
<1.0
<1.0
<2.0
24.4
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
9of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
L
Gi
W
(Q
Sample ID
Sample Data
3
m
a
°
.2
y
o
d
i
K
r
d
!C
Q-
!C
L
fC
t
U
f4
E
E
4)
t
d
N
C
>,4)
a
a
a
mN
N
W
VN
�
4)
V
C0a0i
CM
Ci
Oa
N N
U
4)
d
3
d
m
d~
V
v
L.
a
,
4)w
H
X
a
C
a
d
M
t
U
An3
M
o
U-
U-
R
z
t
a
�+
a
U
O�
C)
01
U
O
U
O>
U
C)
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
125(S)
Surface Water Standard (Ng/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (2)
NE
NE
MW-8 continued
8/18/2015
<0.5
<0.5
<0.5
<1.5
1 <0.5
<5.0
<5.0
<5.0
<5.0
<5.0
ND
<5.0
<5.0
ND
<5.0
<5.0
<200
<200
<100
<100
<100
<200
12/4/2015
<1.0
<1.0
<1.0
<1.0
18
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
191
<25
<100
2/16/2016
<0.5
<0.5
<0.5
<0.5
16
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/2016
<1.0
<1.0
<1.0
<3.0
7.9
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/7/2017
<1.0
<1.0
<1.0
<3.0
9.7
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2017
<0.50
<0.50
<0.50
<0.50
7.2
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/1/2018
<0.50
<0.50
<0.50
<0.50
11
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2018
<0.50
<0.50
<0.50
<0.50
6.6
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/15/2019
<0.50
<0.50
<0.50
<0.50
10
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/8/2019
<0.50
1 <0.50
<0.50
<0.50
6.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2020
<0.50
<0.50
<0.50
<0.50
9.8
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/6/2020
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
MW-13
10/20/1997
ND
ND
ND
ND
23,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/25/1998
190
ND
ND
ND
31,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18-19/98
3
ND
ND
ND
4,300
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/1999
9
ND
ND
ND
10,000
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/1999
ND
ND
ND
ND
530
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/2000
ND
ND
ND
ND
1,200
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2000
1.8
<1.0
<1.0
<3.0
510
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
2.9
<1.0
<1.0
<3.0
410
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
5.2
<1.0
<1.0
<3.0
290
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
1.2
<1.0
<1.0
<3.0
160
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2002
3.3
<1.0
<1.0
<1.0
134
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2003
<1.0
<1.0
<1.0
<1.0
1.1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2003
8.3
<1.0
<1.0
<3.0
45
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2004
1.0
<1.0
<1.0
<3.0
3.8 J
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/17/2004
<1.0
<1.0
<1.0
<3.0
18
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2005
1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/17/2005
2.6
<1.0
<1.0
<3.0
5.4
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/22/2006
86
3.5
2.4
1.2
14.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2006
<1.0
<1.0
<1.0
<3.0
2.6 J
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
10 of 15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
Sample ID
Sample Data
mN
4)
4)w
N
C
d
3
H
N
d
X
L
W
3
W
m
d~
d
V
a
C
a
m
i
VN
d
m
�
t
U
Gi
(Q
a
K
4)
v
An3
M
°
r
t
>,4)
o
d
U-
4)
L.
U-
R
z
d
a
t
a
�+
a
.2
!C
Q-
V
,
U
!C
L
C0a0i
O�
C)
fC
t
a
CM
01
U
y
U
f4
a
Ci
O
U
0
E
Oa
O>
U
E
a
N N
U
C)
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
Surface Water Standard (Ng/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (2)
125(S)
NE
NE
MW-13 continued
2/20/2007
3.5
<1.0
<1.0
<3.0
1 6.1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2007
31
<1.0
<1.0
<3.0
6.2
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/25/2008
10
<1.0
<1.0
<3.0
2.9J
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/28/2008
7.6
<1.0
<1.0
<3.0
3.8J
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/11/2009
<1.0
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/20/2009
5.7
<1.0
<1.0
<2.0
1.8
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/4/2010
2.1
<1.0
<1.0
<2.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/12/2010
8.3
<1.0
<1.0
<3.0
3.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/15/2011
7.8
<1.0
<1.0
<2.0
6.8
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
9/8/2011
25.4
<1.0
<1.0
<2.0
1.4
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/13/2012
27.5
<1.0
<1.0
<3.0
3.1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/3/2012
NS
NS
NS
NS
NS
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/4/2013
17.6
<1.0
<1.0
<2.0
2.4
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/29/2013
1.4
<1.0
<1.0
<2.0
1.4
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/19/2014
6.6
<1.0
<1.0
<2.0
3.8
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/25/2014
14.0
<1.0
<1.0
<2.0
4.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2015
4.6
<1.0
<1.0
<2.0
5.1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/18/2015
6.4
<0.5
<0.5
<1.5
1.0
<5.0
<5.0
<5.0
<5.0
<5.0
ND
<5.0
<5.0
ND
<5.0
<5.0
<200
<200
<100
53.9J
<100
<200
12/4/2015
7.1
<1.0
<1.0
<1.0
9.0
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
191
130
<25
<100
2/16/2016
32
1.3
0.85
1.00
5.3
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/2016
6.6
<1.0
<1.0
<3.0
<1.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/7/2017
1.3
<1.0
<1.0
<3.0
3.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/15/2017
0.69
<0.50
<0.50
<0.50
8.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/1/2018
1.9
<0.50
<0.50
<0.50
0.87
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2018
5.2
<0.50
<0.50
<0.50
2.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/15/2019
48
1.6
1.4
2.0
2.7
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/8/2019
2.8
<0.50
<0.50
<0.50
2.8
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/18/2020
4.8
<0.50
<0.50
<0.50
11.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/6/2020
0.45J
<0.50
<0.50
<0.50
7.2
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
11 of 15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic
Compounds Method 6200B
Semi Volatile Organic
Compounds Method 625.1
MADEP-EPH/VPH
L
0)
W
(�
Sample ID
Sample Data
Q-
°
r
0
v,
2
41
�
X
r
<C
Q
IC
t
IC
t
�+
c0
E
r
n3
E
c
0
R
t
a
Q
a
a
t
n
0
0
N
C
t
++
41
a
C
0)
d
=
y
41
ar
Q
L
V
C
0)
yT
�,
W
+,
0
C
fLC
C
M
+-
C
0)
C
M
:)
00
U
N
L)
00
U
O
U
N
N
U
N
C
>%
m
d
3
C
Qi
t m
it L
r
C
(D
Y
N
r-
L
C
0
0
a-
Q)
L
1
1
1
1
r
0)
co
W
O
51
x
0)
��
C1
a
i
a
d
m
i
U
y
-0
o
U-
2
U-
M
z
i
a
a
0)
M
LO
U
M
U
U
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
12(zjS)
Surface Water Standard (fag/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (1)
NE
NE
MW-17 (MW-TR1U)
8/18/1998
38
ND
ND
ND
3,500
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/1999
57
ND
ND
ND
2,400
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/1999
23
ND
ND
ND
370
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/2000
86
18
6
ND
170
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2000
50
7.9
2.2
<3.0
100
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
21
1.9
1.6
<3.0
21
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
16
1.4
<1.0
<3.0
20
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
11
<1.0
<1.0
<3.0
12
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/4/2015
<1.0
<1.0
<1.0
<1.0
0.55J
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
110
<75
71J
<25
<100
MW-18 (MW-TR1D)
8/18-19/98
ND
ND
ND
ND
240
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/1999
ND
ND
ND
ND
70
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/1999
ND
ND
ND
ND
20
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/17/2000
ND
ND
ND
ND
5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
2/27/2002
<1.0
<1.0
<1.0
<3.0
<5.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
12/4/2015
<1.0
<1.0
<1.0
<1.0
0.43J
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
<75
<25
<100
MW-23
12/3/2015
<1.0
<1.0
<1.0
<1.0
<1.0
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
140
<75
<75
<25
<100
MW-24
12/4/2015
1.01
14
<5.0
<5.0
<5.0
14
4.3J
1.9J
1.2J
<50
ND
9.3J
2.8J
ND
7.4J
7.3J
<100
160
640
1,100
750
410
2/16/2016
8.7
8.7
2.0 J
3.9
<2.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/2016
4.2
4.1
1.4
<3.0
NA
10.2
4.9J
<0.33
<0.21
<0.79
ND
11.5
2.1J
ND
8.7
6.3
<100
<100
393
2,050
730
276
2/7/2017
4.7
4.8
1.3
<3.0
NA
9.2
4.8J
1.OJ
<0.21
<0.79
ND
10.6
1.5J
ND
7.3
6.6
<100
101
564
1,520
783
244
8/15/2017
1.4
3.9
0.53
0.88
NA
4.8J
1.9J
0.77J
0.29J
<8.0
ND
6.8J
<8.0
ND
1.5J
5.5J
<120
<120
340
660
280
1 180
2/1/2018 t
1.7
1.8
0.63
0.75
NA
8.6J
2.4J
<16
<16
<16
ND
8.9J
<16
ND
<16
7.1J
<100
<100
280
620
280
160
8/16/2018
2.0
1.8
0.64
1.2
NA
5.7J
2.2J
<16
<16
<16
ND
4.1J
<16
ND
2.1J
3.1J
<100
<100
410
740
330
130
2/15/2019
13
14
3.3
7.4
NA
7.0
2.9 J
<3.2
<3.2
<16
ND
7.9
<3.2
ND
2.3 J
6.2
190
260
400
1,900
520
320
8/8/2019
0.45J
<0.50
<0.50
<0.50
NA
<8.0
<8.0
<8.0
<8.0
<40
ND
<8.0
<8.0
ND
<8.0
<8.0
<110
160
100
150
81
290
2/18/2020 t
8.3
16
2.2
7.9
NA
7.1 J
<8.0
<8.0
<8.0
<8.0
<8.0
6.2J
<8.0
5.3J
<8.0
6.1 J
180
230
500
1700
490
290
8/6/2020
4.9
2.0
1.1
2.7
NA
<8.0
<8.0
<8.0
<8.0
<40
<8.0
5.2J
<8.0
<8.0
<8.0
4.7J
<100
<100
200
790
220
140
12 of 15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
L
Gi
W
(Q
Sample ID
Sample Data
3
m
a
°
.2
y
0
d
i
K
r
d
!C
Q-
!C
L
fC
t
U
f4
E
E
4)
t
d
N
>,4)
a
a
VN
y
4)
4)4)
c
0a0
U
CM
U
ao
C)
Oa
C)
N
NLLI
U
N
4)
m
3
d
d~
c
V
4)w
H
X2
a
C
a
0)
M
t
U
N
M
o
U-
3
U-
R
z
t
a
�+
a
U
0)
C)
(1
U
W)
U
O)
U
C)
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
125(S)
Surface Water Standard (Ng/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (2)
NE
NE
MW-25
12/4/2015
<1.0
<1.0
<1.0
<1.0
1 1.1
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
<75
<25
<100
2/16/2016
<0.5
<0.5
<0.5
<0.5
1.1
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/2016
<1.0
<1.0
<1.0
<3.0
NA
<0.25
<0.14
<0.33
<0.21
<0.79
ND
<0.21
<0.21
ND
<0.22
<0.19
<100
<100
<50.0
<50.0
<50.0
<100
2/7/2017
<1.0
<1.0
<1.0
<3.0
NA
<0.25
<0.14
<0.33
<0.21
<0.79
ND
<0.21
<0.21
ND
<0.22
<0.19
<100
<100
<50.0
<50.0
<50.0
<100
8/15/2017
0.61
<0.50
<0.50
<0.50
NA
<1.6
<1.6
<1.6
<1.6
<1.6
ND
<1.6
<1.6
ND
<1.6
0.62J
<110
<110
<75
<75
<25
<110
2/1/2018
<0.50
<0.50
<0.50
<0.50
NA
<8.0
<8.0
<8.0
<8.0
<8.0
ND
<8.0
<8.0
ND
<8.0
0.68J
<100
<100
<75
<75
<25
<100
8/16/2018
<0.50
<0.50
<0.50
<0.50
NA
<8.0
<8.0
<8.0
<8.0
<8.0
ND
<8.0
<8.0
ND
<8.0
0.51J
<100
<100
<75
<75
<25
<100
2/15/2019
<0.50
<0.50
<0.50
<0.50
NA
<1.6
<1.6
<1.6
<1.6
<8.0
ND
<1.6
<1.6
ND
<1.6
<1.6
<100
<100
<75
<75
<25
<100
8/8/2019
<0.50
<0.50
<0.50
<0.50
NA
<1.6
<1.6
<1.6
<1.6
<8.0
1.5J
<1.6
<1.6
ND
<1.6
<1.6
<100
<100
<75
<75
<25
<100
2/18/2020
<0.50
<0.50
<0.50
<0.50
NA
<1.6
<1.6
<1.6
<1.6
<8.0
<1.6
<1.6
<1.6
ND
<1.6
<1.6
<100
<100
<75
<75
<25
<100
8/6/2020
<0.50
<0.50
<0.50
<0.50
NA
<1.6
1 <1.6
<1.6
1 <1.6
<8.0
0.86J
<1.6
<1.6
ND
1 <1.6
<1.6
<100
<100
<75
<75
<25
<100
MW-25D
12/4/2015
<1.0
<1.0
<1.0
<1.0
1.2
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
100
<75
<75
<25
<100
2/16/2016
<0.5
<0.5
<0.5
<0.5
1.3
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
8/19/2016
<1.0
<1.0
<1.0
<3.0
NA
<0.25
<0.14
<0.33
<0.21
<0.79
ND
<0.21
<0.21
ND
<0.22
<0.19
<100
<100
<50.0
<50.0
<50.0
<100
2/7/2017
<1.0
<1.0
<1.0
<3.0
NA
<0.25
<0.14
<0.33
<0.21
<0.79
ND
<0.21
<0.21
ND
<0.22
<0.19
<100
<100
<50.0
<50.0
<50.0
<100
8/15/2017
<0.50
<0.50
<0.50
<0.50
<0.50
<1.6
<1.6
<1.6
<1.6
<1.6
ND
<1.6
<1.6
ND
<1.6
<1.6
<100
<100
<75
<75
<25
<100
2/1/2018
<0.50
<0.50
<0.50
<0.50
<0.50
<1.6
<1.6
<1.6
<1.6
0.75J
0.44J
<1.6
<1.6
ND
<1.6
<1.6
<100
<100
<75
<75
<25
<100
8/16/2018
<0.50
<0.50
<0.50
<0.50
NA
<1.6
<1.6
<1.6
<1.6
<8.0
ND
<1.6
<1.6
ND
<1.6
<1.6
<100
<100
<75
<75
<25
<100
2/15/2019
<0.50
<0.50
<0.50
<0.50
NA
<1.6
<1.6
<1.6
<1.6
<8.0
ND
<1.6
<1.6
ND
<1.6
<1.6
NA
NA
<75
<75
<25
NA
8/8/2019 t
<0.50
<0.50
<0.50
<0.50
5.4
<1.6
<1.6
<1.6
<1.6
<8.0
1.4J
<1.6
<1.6
ND
<1.6
<1.6
<100
<100
<75
<75
<25
<100
2/18/2020
<0.50
<0.50
<0.50
<0.50
NA
<1.6
<1.6
<1.6
<1.6
<8.0
<1.6
<1.6
<1.6
ND
<1.6
<1.6
<100
<100
<75
<75
<25
<100
8/6/2020
<0.50
<0.50
<0.50
<0.50
NA
<1.6
<1.6
<1.6
<1.6
<8.0
0.93J
<1.6
<1.6
ND
<1.6
1 <1.6
<100
<100
<75
<75
<25
<100
13 of 15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic
Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
L
0)
W
(�
Sample ID
Sample Data
Q-
°
r
0
v,
2
41
�
X
r
<C
Q
IC
t
IC
t
�+
c0
E
r
n3
E
c
0
R
t
a
Q
a
a
t
n
0
0
N
C
t
++
41
a
C
0)
d
=
y
41
ar
Q
L
V
C
0)
yT
�,
W
+,
0
C
fLC
C
M
+-
C
0)
C
M
:)
00
U
N
L)
00
U
O
U
N
N
U
N
C
>%
m
d
3
C
Qi
t m
it L
r
C
(D
Y
N
r-
L
C
0
0
a-
Q)
L
1
1
1
1
r
0)
co
W
O
51
x
0)
��
C1
a
i
a
d
m
i
U
y
-0
o
U-
2
U-
M
z
i
a
a
0)
U
M
U
LO
U
M
U
U
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
125(S)
Surface Water Standard (fag/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (Z)
180 (S) (2)
NE
NE
Quality Assurance / Quality Control Samples
Dup-1 (MW-4)
8/18/2015
<0.5
<0.5
<0.5
<1.5
<0.5
<4.8
<4.8
<4.8
<4.8
<4.8
ND
<4.8
<4.8
ND
<4.8
<4.8
<190
<190
<100
<100
<100
<190
Dup120415 (MW-25D)
12/4/2015
<1.0
<1.0
<1.0
<1.0
1.1
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
<100
<75
<75
<25
<100
Dup12032015 (MW-2)
12/3/2015
<1.0
<1.0
<1.0
<1.0
5.2
<2.0
<2.0
<2.0
<2.0
<10
ND
<2.0
<2.0
ND
<2.0
<2.0
<100
100
<75
<75
<25
<100
KSDUP (MW-24)
2/16/2016
7.7
12
2.1 J
3.8
<2.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DUP081916 (MW-8)
8/19/2016
<1.0
<1.0
<1.0
<3.0
7.2
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DUP020717 (MW-8)
2/7/2017
<1.0
<1.0
<1.0
<3.0
9.5
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DUP08152017(MW-13)
8/15/2017
0.75
<0.50
<0.50
<0.50
7.9
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DUP-1 (MW-8)
2/1/2018
<0.50
<0.50
<0.50
1 <0.50
9.7
NA
I NA
I NA
I NA
I NA
I NA
I NA
I NA
I NA
I NA
I NA
I NA
NA
NA
NA
NA
I NA
14of15
Table 5
Groundwater Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Volatile Organic Compounds Method 6200B
Semi Volatile Organic Compounds Method 625.1
MADEP-EPH/VPH
L
Gi
W
(Q
Sample ID
Sample Data
3
m
a
°
.2
y
0
G>
t4
G>
i
K
r
d
!a
Q-
cc
L
cc
t
U
l4
t4
E
fC
E
t
d
N
C
VN
a,
>,N
CO),
Go
CM a
a
Oa
a
N
W
�
d
L.
C
Ci
N
U
d~
V
C
d
t
to
3
R
a
t
�+
O�
01
O
O>
m
w
H
X
a
a
m
U
M
o
U-
U-
z
a
a
U
U
U
U
U
U
NCAC 2L Standard (Ng/L)
1
600
600
500
20
80
2,000
0.05
5
3
700
300
300
6
200
200
10,000*
700*
400*
200*
12(5ZjS)
Surface Water Standard (Ng/L)
1.19
68 (')
11
670 (2)
19 (2)
70 (')
300 (')
0.0028
0.32 (')
9.50
20 (')
50 (')
12
NE
20 (')
S
180 (S) (2)
180 (S) (z)
NE
NE
DUP-1(MW-24)
8/16/2018
1.8
1.9
0.61
1.1
1 <0.50
5.9J
2.1J
<16
<16
<80
ND
3.7J
<16
ND
1.9J
28J
<100
<100
340
700
360
110
DUP21519(MW-13)
02/15/19
48
1.6
1.3
2.0
3.0
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DUP-1 (MW-24)
8/8/2019
<0.50
<0.50
<0.50
<0.50
5.4
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
I NA
NA
NA
I NA
DUP-1 (MW-8)
2/18/2020
<0.50
<0.50
<0.50
<0.50
9.6
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
DUP-1 (MW-4)
8/6/2020
<0.50
<0.50
<0.50
<0.50
<0.50
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Notes:
All concentrations reported in micrograms per liter (pg/L)
MADEP = Massachusetts Department of Environmental Protection
EPH = Extractable Petroleum Hydrocarbons
VPH = Volatile Petroleum Hydrocarbons
WS-II = Water Supply Class II
HQW = High Quality Waters
NE = No standard established
NA = Not analyzed
ND = Not detected
Bold = Detection exceeds North Carolina Administrative Code (NCAC) 2L Groundwater Standard
Gray fill indicates detection above the applicable Surface Water Standards (Indicated with superscript numerals 1 and 2)
No superscript numeral indicates the NCAC 26 Surface Water Standard for Water Supply (WS) II, High Quality Waters (HQW) classification
(') = Environmental Protection Agency Nationally Recommended Water Quality Criteria for Aquatic Life and Human Health.
(Z) = North Carolina Protective Values for Surface Waters
"<" = Analyte was not detected at or above the reporting limit shown.
Final and interim groundwater quality standards
"J" = Estimated concentration between the method detection limit and the reporting limit.
"S" = Solubility exceeds toxicity; therefore, standard is met if no sheen is present on water surface or shoreline
t = Additional analytes were detected in these wells during the sampling event flagged:
MW-24, 2/1/2018: Benzo(a)pyrene at an estimated concentration of 1.0 pg/L which is above the 2L Standard of 0.005 pg/L and 26 Standard of 0.0028 pg/L for Total PAHs combined.
MW-25D, 8/8/2019: Diethylphthalate at an estimated concentration of 1.4 pg/L which is below the 2L Standard of 6,000 pg/L and the 213 Standard of 600 tag/L.
MW-25D, 8/8/2019: Phenol at a concentration of 11 pg/L which is below the 2L Standard of 30 tag/L and the 2B Standard of 4,000 pg/L.
MW-24, 2/18/2020: 1-Methylnaphthalene at an estimated concentration of 5.2 pg/L, which is above the Interim Maximum Allowable Concetration of 1.0 µg/L
MW-24, 8/6/2020: 1-Methylnaphthalene at an estimated concentration of 2.6J pg/L, which is above the Interim Maximum Allowable Concetration of 1.0 pg/L.
Monitor Well naming convention was modified January 2001. Former well designation in parentheses.
15 of 15
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
12/20/1999
<1.0
<1.0
<1.0
<3.0
<5.0
4/10/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Allen
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/22/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/23/1999
<1.0
<1.0
<1.0
<3.0
<5.0
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
4/26/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/25/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
DW-Bethpage-
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
Church
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<1.0
<5.0
DW-Boan
5/8/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
DW-Brasington
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Brooks
6/27/2000
<2.0
<2.0
<2.0
<4.0
<2.0
9/11/2014
<0.5
<0.5
8.6
<3.0
<5.0
DW-Buchanan
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
DW-Cain
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Cain-Influent
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
8/25/2014
<0.5
<0.5
<0.5
<3.0
<5.0
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
-
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
DW-Cain-Effluent
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
DW-Cheeseman
6/27/2000
<2.0
<2.0
<2.0
<4.0
<2.0
1 -
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Childers
7/31/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Childers-
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
Influent
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
1 <5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
Page 1 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
11/23/1999
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Clark
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/14/2002
<1.0
<1.0
<1.0
<3.0
<5.0
8/22/2017
Not Sampled - Could not contact owner
DW-Cook
11/23/1999
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Cook-Effluent
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
DW-Cook-
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
Influent
8/29/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
<5.0
-
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
8/23/2018
<1.0
<1.0
<1.0
<3.0
<1.0
<1.0
8/22/2019
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
10/16/2020
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
11/23/1999
<1.0
<1.0
<1.0
<3.0
<5.0
-
DW-Coren
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
DW-Coren-
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
Influent
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
-
8/22/2017
<0.50
<0.50
1.3
<3.0
1 <5.0
<1.0
8/23/2018
<1.0
<1.0
<1.0
<3.0
<1.0
<1.0
8/22/2019
<0.50
<0.50
1.6
2.01
<5.0
<1.0
10/16/2020
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
12/7/1999
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Crainshaw
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/22/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/9/1999
<1.0
<1.0
<1.0
<3.0
116
11/19/1999
<1.0
<1.0
<1.0
<3.0
990
1/6/2000
<1.0
<1.0
<1.0
<3.0
600
8/16/2000
<1.0
<1.0
<1.0
<3.0
200
2/6/2001
<1.0
<1.0
<1.0
<3.0
1 69
3/1/2001
<1.0
<1.0
<1.0
<3.0
42
8/16/2001
<1.0
<1.0
<1.0
<3.0
19
DW-Crowe
2/27/2002
<1.0
<1.0
<1.0
<3.0
5
(MW-16)1"
8/28/2002
<1.0
<1.0
<1.0
<1.0
<1.0
2/18/2003
<1.0
<1.0
<1.0
<1.0
<1.0
8/18/2003
<1.0
<1.0
<1.0
<3.0
<5.0
2/19/2004
<1.0
<1.0
<1.0
<3.0
<5.0
8/17/2004
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2005
<1.0
<1.0
<1.0
<3.0
<5.0
8/17/2005
<1.0
<1.0
<1.0
<3.0
<5.0
2/22/2006
<1.0
<1.0
<1.0
1 <3.0
1 <5.0
5/21/2009
<1.0
<1.0
<1.0
1 <3.0
1 <5.0
Page 2 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
DW-Daughtery
12/20/1999
<1.0
<1.0
<1.0
<3.0
<5.0
-
12/20/1999
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Deaton
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/22/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
DW-Ellis
8/27/2015
<0.5
<0.5
2.0
<3.0
<5.0
<1.0
1/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
-
DW-Elwood
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Elwood-D
5/7/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Elwood
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
9/28/2006
<1.0
I <1.0
<1.0
<3.0
<5.0
11/23/1999
<1.0
<1.0
<1.0
<3.0
<5.0
12/27/1999
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Emerson
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
4/26/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/25/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Emerson-
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
Effluent
3/14/2002
<1.0
I <1.0
<1.0
<3.0
<5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Emerson-
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
Influent
2/27/2002
<1.0
<1.0
<1.0
<3.0
<5.0
3/14/2002
<1.0
<1.0
<1.0
<3.0
1 <5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
1 <5.0
9/11/2014
<0.5
<0.5
<0.5
<3.0
<5.0
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
DW-Gaultney
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
-
DW-Goodnight-
3/29/2000
<1.0
<1.0
<1.0
<3.0
72.4
New
4/17/2000
<1.0
<1.0
<1.0
<3.0
32
7/6/2000
<1.0
<1.0
2.2
<3.0
<5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
DW-Goodnight-
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
New-CV-1
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Goodnight-
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
New-CV-2
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
-
8/27/2015
<1.0
<1.0
<1.0
<3.0
<5.0
<1.0
8/29/2215
<1.0
<1.0
<1.0
<3.0
<5.0
<1.0
8/29/2016
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
Page 3 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
7/18/2000
<1.0
<1.0
18
<3.0
6.2
8/16/2000
<1.0
<1.0
3
<3.0
<5.0
9/28/2000
<1.0
<1.0
4.7
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/27/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
DW-Goodnight-
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
New -Influent
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
<5.0
9/2/2004
<1.0
<1.0
<1.0
<2.0
<1.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
11/22/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
<5.0
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2013
<0.5
<0.5
<0.5
<3.0
<5.0
8/25/2014
<0.5
<0.5
<0.5
<3.0
<5.0
-
8/27/2015
<0.5
<0.5
<0.5
<3.0
1 <5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
0.99J
<1.0
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
8/23/2018
<1.0
<1.0
<1.0
<3.0
<1.0
<1.0
8/22/2019
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
10/16/2020
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
11/19/1999
<1.0
<1.0
<1.0
<3.0
<5.0
12/22/1999
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Goodnight-
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
Old
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
4/26/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/25/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Goodnight-
Old-CV-1
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Goodnight-
Old-CV-2
6/15/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
DW-Goodnight-
Old -Influent
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Harwood
6/27/2000
<2.0
<2.0
<2.0
<4.0
<2.0
DW-Johnson
12/20/1999
<1.0
<1.0
<1.0
<3.0
<5.0
6/6/2007
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<1.0
<1.0
<1.0
<3.0
1 <5.0
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2013
<0.5
<0.5
<0.5
<3.0
<5.0
-
DW-Kann-Station
8/29/2016
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
8/23/2018
<1.0
<1.0
<1.0
<3.0
<1.0
<1.0
8/22/2019
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
10/16/2020
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
DW-Keasler
10/2/2000
<1.0
<1.0
<1.0
<3.0
<5.0
-
11/23/1999
<1.0
<1.0
<1.0
<3.0
<5.0
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Keenan
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
4/26/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/25/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
Page 4 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Keenan-
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
Influent
3/14/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
<5.0
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
DW-Kissiah
4/19/2000
<1.0
<1.0
<1.0
<3.0
<5.0
-
1/5/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Laws
5/22/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
7/31/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/6/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Laws-
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
Influent
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
12/28/2004
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2011
<1.0
<1.0
<1.0
<3.0
<5.0
9/11/2014
<0.5
<0.5
<0.5
<3.0
<5.0
DW-Lunsford-D
6/28/2000
<2.0
<2.0
<2.0
<4.0
<2.0
11/23/1999
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Luther
4/26/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/25/2000
<1.0
<1.0
<1.0
<3.0
<5.0
-
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
-
8/11/2000
<5.0
<5.0
<5.0
<1.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/11/2000
<5.0
<5.0
<5.0
<1.0
<5.0
9/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Luther-
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
Effluent
6/22/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/22/2004
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
<5.0
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
Page 5 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-MacAnulty-
Influent
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/14/2002
<1.0
<1.0
<1.0
<3.0
1 <5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
9/11/2014
<0.5
<0.5
<0.5
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/4/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
6.3
5/1/2001
<1.0
<1.0
<1.0
<3.0
5.4
6/21/2001
<1.0
<1.0
<1.0
<3.0
1 31
DW-Maurer-
7/6/2001
<1.0
<1.0
<1.0
<3.0
<5.0
CV-1
8/20/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
6.1
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
5.8
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
1 <5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
<5.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
9/5/2007
<1.0
<1.0
<1.0
<3.0
<5.0
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/4/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
5/25/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Maurer-
8/20/2001
<1.0
<1.0
<1.0
<3.0
<5.0
CV-2
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
1 <5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
<5.0
9/2/2004
<1.0
<1.0
<1.0
<2.0
<1.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
9/5/2007
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
<5.0
-
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
Page 6 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
DW-Maurer
12/27/1999
<1.0
<1.0
<1.0
<3.0
<5.0
1/5/2000
<1.0
<1.0
<1.0
<3.0
<5.0
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
10
5/4/2000
<1.0
<1.0
<1.0
<3.0
28
5/25/2000
<1.0
<1.0
<1.0
<3.0
31
6/15/2000
<1.0
<1.0
<1.0
<3.0
32
7/18/2000
<1.0
<1.0
<1.0
<3.0
12
8/16/2000
<1.0
<1.0
<1.0
<3.0
40
9/28/2000
<1.0
<1.0
<1.0
<3.0
40
11/14/2000
<1.0
<1.0
<1.0
<3.0
33
12/13/2000
<1.0
<1.0
<1.0
<3.0
1 40
1/18/2001
<1.0
<1.0
<1.0
<3.0
34
2/23/2001
<1.0
<1.0
<1.0
<3.0
38
3/30/2001
<1.0
<1.0
<1.0
<3.0
39
5/1/2001
<1.0
<1.0
<1.0
<3.0
23
6/21/2001
<1.0
<1.0
<1.0
<3.0
31
8/20/2001
<1.0
<1.0
<1.0
<3.0
19
10/24/2001
<1.0
<1.0
<1.0
<3.0
28
3/1/2002
<1.0
<1.0
<1.0
<3.0
1 18
5/14/2002
<1.0
<1.0
<1.0
<1.0
21
DW-Maurer-
7/10/2002
<1.0
<1.0
<1.0
<1.0
28
Influent
11/6/2002
<1.0
<1.0
<1.0
<1.0
24
3/11/2003
<1.0
<1.0
<1.0
<3.0
12
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
16
9/2/2004
<1.0
<1.0
<1.0
<2.0
8.7
3/9/2005
<1.0
<1.0
<1.0
<3.0
1 6.9
8/29/2005
<1.0
<1.0
<1.0
<3.0
7.4
9/28/2006
<1.0
<1.0
<1.0
<3.0
5.2
9/5/2007
<1.0
<1.0
<1.0
<3.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
<5.0
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2013
<0.5
<0.5
<0.5
<3.0
<5.0
8/25/2014
<0.5
<0.5
<0.5
<3.0
1 <5.0
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
2.OJ
<1.0
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
8/23/2018
<1.0
<1.0
<1.0
<3.0
1.9
<1.0
8/22/2019
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
10/16/2020
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
DW-Mesimer-D
6/27/2000
<2.0
<2.0
<2.0
<4.0
<2.0
-
DW-Mesimer-H
6/27/2000
<2.0
<2.0
<2.0
1 <4.0
<2.0
DW-Mesimer-K
6/27/2000
<2.0
<2.0
<2.0
<4.0
<2.0
DW-Michael
7/31/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Murphy
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
12/6/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
1 <5.0
6/5/2007
<1.0
<1.0
<1.0
<1.0
<5.0
12/20/1999
<1.0
<1.0
<1.0
<3.0
48
DW-Myers
12/22/1999
<1.0
<1.0
<1.0
<3.0
81
1/5/2000
<1.0
<1.0
<1.0
<3.0
51
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Myers-CV-1
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Myers-CV-2
1/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
2/16/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
1/18/2000
<1.0
<1.0
<1.0
<3.0
66
2/16/2000
<1.0
<1.0
<1.0
<3.0
62
DW-Myers-Influent
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/27/2002
<1.0
<1.0
<1.0
<3.0
<5.0
2/19/2004
<1.0
<1.0
<1.0
<3.0
<5.0
12/27/1999
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
10/2/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Owens
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<1.0
<5.0
Page 7 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
12/20/1999
<1.0
<1.0
<1.0
<3.0
<5.0
4/10/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Parker
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/22/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
DW-Porter
6/28/2000
<2.0
<2.0
<2.0
<4.0
<2.0
DW-Poteat
2/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Preslar
5/22/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Reynolds
4/10/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/28/2000
<2.0
<2.0
<2.0
<4.0
<2.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Rhodes
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/14/2002
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/11/2014
<0.5
<0.5
<0.5
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
DW-Schaffner-
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
Influent
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
1 <5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Schroeder
6/27/2000
<2.0
<2.0
<2.0
<4.0
<2.0
DW-Shinn
8/11/2000
<5.0
<5.0
<5.0
<1.0
<5.0
11/23/1999
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Smith
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
-
10/16/2020
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
5/22/2000
<1.0
<1.0
<1.0
<3.0
1 <5.0
-
DW-Smith-David
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
9/11/2014
<0.5
<0.5
<0.5
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Smith-Influent
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
1 <5.0
8/29/2005
<1.0
<1.0
<1.0
<1.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
-
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
7/6/2000
<1.0
<1.0
<1.0
<1.0
<1.0
-
DW-Snyder
9/17/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/18/2007
<1.0
<1.0
<1.0
<3.0
<5.0
8/25/2014
<0.5
<0.5
<0.5
<3.0
15
DW-Teal
8/25/2014(4)
<0.5
<0.5
<0.5
<3.0
7.4
DW-Teal-Effluent
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
DW-Teal-Influent
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
1 <0.5
1 <0.5
<0.5
<3.0
<5.0
1 <1.0
Page 8 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
12/27/1999
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Tucker
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
4/26/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/25/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
19
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
27
7/6/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Tucker-CV-1
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
14
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
7.5
9/2/2004
<1.0
<1.0
<1.0
<2.0
<1.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<1.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
1 <1.0
9/5/2007
<1.0
<1.0
<1.0
<3.0
<1.0
9/5/2007
<1.0
<1.0
<1.0
<3.0
<1.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/6/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Tucker-CV-2
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
5.5
9/2/2004
<1.0
<1.0
<1.0
<2.0
<1.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
9/5/2007
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
<5.0
8/27/2015
<0.5
<1.0
<1.0
<3.0
<5.0
<1.0
8/29/2016
<0.5
<1.0
<1.0
<3.0
<5.0
<1.0
Page 9 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
1 8.4
11/14/2000
<1.0
<1.0
<1.0
<3.0
16
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
23
2/23/2001
<1.0
<1.0
<1.0
<3.0
23
3/30/2001
<1.0
<1.0
<1.0
<3.0
24
5/1/2001
<1.0
<1.0
<1.0
<3.0
24
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/6/2001
<1.0
<1.0
<1.0
<3.0
1 36
8/16/2001
<1.0
<1.0
<1.0
<3.0
24
10/24/2001
<1.0
<1.0
<1.0
<3.0
20
3/1/2002
<1.0
<1.0
<1.0
<3.0
13
5/14/2002
<1.0
<1.0
<1.0
<1.0
11
DW-Tucker-
7/10/2002
<1.0
<1.0
<1.0
<1.0
14
Influentl3l
11/6/2002
<1.0
<1.0
<1.0
<1.0
15
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
1 <5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
7.1
9/2/2004
<1.0
<1.0
<1.0
<2.0
3.9
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
2.8 J
9/5/2007
<1.0
<1.0
<1.0
<3.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
1 <5.0
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
8/25/2014
<1.0
<1.0
<1.0
<3.0
<5.0
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
1.91
<1.0
8/24/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
8/23/2018
<1.0
<1.0
<1.0
<3.0
1.3
<1.0
DW-Wally
6/28/2000
<2.0
<2.0
<2.0
<4.0
<2.0
-
DW-Ware
2/28/2001
<1.0
<1.0
<1.0
<3.0
1 <5.0
12/22/1999
<1.0
<1.0
<1.0
<3.0
26
DW-Watts
12/27/1999
<1.0
<1.0
<1.0
<3.0
<5.0
1/5/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/4/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
11
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
10/2/2000
<1.0
<1.0
<1.0
1 <3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/7/2001
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Watts-CV-1
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
19
9/2/2004
<1.0
<1.0
<1.0
<2.0
<1.0
3/9/2005
<1.0
<1.0
I <1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
9/5/2007
<1.0
<1.0
<1.0
<3.0
<5.0
Page 10 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
2/2/2000
<1.0
<1.0
<1.0
<3.0
<5.0
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/4/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/25/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/15/2000
<1.0
<1.0
<1.0
<3.0
<5.0
7/18/2000
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2000
<1.0
<1.0
<1.0
<3.0
<5.0
9/28/2000
<1.0
<1.0
<1.0
<3.0
<5.0
11/14/2000
<1.0
<1.0
<1.0
<3.0
<5.0
12/13/2000
<1.0
<1.0
<1.0
<3.0
<5.0
1/18/2001
<1.0
<1.0
<1.0
<3.0
<5.0
2/23/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/30/2001
<1.0
<1.0
<1.0
<3.0
<5.0
5/1/2001
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Watts-CV-2
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
<5.0
3/1/2002
<1.0
<1.0
<1.0
<3.0
<5.0
5/14/2002
<1.0
<1.0
<1.0
<1.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
11/6/2002
<1.0
<1.0
<1.0
<1.0
<5.0
3/11/2003
<1.0
<1.0
<1.0
<3.0
<5.0
7/17/2003
<1.0
<1.0
<1.0
<3.0
6.3
7/30/2003
<1.0
<1.0
<1.0
<3.0
<5.0
3/11/2004
<1.0
<1.0
<1.0
<3.0
<5.0
9/2/2004
<1.0
<1.0
<1.0
<2.0
<1.0
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
1 <5.0
9/28/2006
<1.0
<1.0
<1.0
<3.0
<5.0
9/5/2007
<1.0
<1.0
<1.0
<3.0
<5.0
-
DW-Watts-New-CV2
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
2/2/2000
<1.0
<1.0
<1.0
<3.0
15
3/27/2000
<1.0
<1.0
<1.0
<3.0
<5.0
5/4/2000
<1.0
<1.0
<1.0
<3.0
19
5/25/2000
<1.0
<1.0
<1.0
<3.0
21
6/15/2000
<1.0
<1.0
1.5
<3.0
17
7/18/2000
<1.0
<1.0
<1.0
<3.0
30
8/16/2000
<1.0
<1.0
<1.0
<3.0
30
9/28/2000
<1.0
<1.0
<1.0
<3.0
51
11/14/2000
<1.0
<1.0
<1.0
<3.0
46
12/13/2000
<1.0
<1.0
<1.0
<3.0
49
1/18/2001
<1.0
<1.0
<1.0
<3.0
65
2/23/2001
<1.0
<1.0
<1.0
<3.0
73
3/30/2001
<1.0
<1.0
<1.0
<3.0
81
5/1/2001
<1.0
<1.0
<1.0
<3.0
75
DW-Watts-Influent
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
8/16/2001
<1.0
<1.0
<1.0
<3.0
<5.0
10/24/2001
<1.0
<1.0
<1.0
<3.0
61
3/1/2002
<1.0
<1.0
<1.0
<3.0
24
5/14/2002
<1.0
<1.0
<1.0
<1.0
13
7/10/2002
<1.0
<1.0
<1.0
<1.0
69
11/6/2002
<1.0
<1.0
<1.0
<1.0
1 35
3/11/2003
<1.0
<1.0
<1.0
<3.0
30
7/17/2003
<1.0
<1.0
<1.0
<3.0
13
3/11/2004
<1.0
<1.0
<1.0
<3.0
23
9/2/2004
<1.0
<1.0
<1.0
<2.0
6.2
3/9/2005
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2005
<1.0
<1.0
<1.0
<3.0
10
9/28/2006
R0
<1.0
<1.0
<3.0
4.4 J
9/5/2007
<1.0
<1.0
<1.0
<3.0
8.6
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
Page 11 of 12
Table 6
Water Supply Well Sample Analytical Results
Colonial Pipeline Company
Kannapolis Booster Station
Concord, North Carolina
Well ID
Date
Benzene
Ethylbenzene
Toluene
Xylenes
MTBE
Naphthalene
NCAC 2L Standard (pg/L)
1
600
600
500
20
6
2/25/2008
<0.5
<1.0
<1.0
<3.0
<5.0
5/21/2009
<1.0
<1.0
<1.0
<3.0
<5.0
5/24/2011
<0.5
<1.0
<1.0
<3.0
<5.0
5/17/2012
<1.0
<1.0
<1.0
<3.0
<5.0
8/29/2013
<0.5
<0.5
<0.5
<3.0
<5.0
DW-Watts-New-
8/25/2014
<0.5
<0.5
<0.5
<3.0
<5.0
-
Influent
8/27/2015
<0.5
<0.5
<0.5
<3.0
<5.0
<1.0
8/29/2016
<0.5
<0.5
<0.5
<3.0
UJI
<1.0
8/22/2017
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
8/23/2018
<1.0
<1.0
<1.0
<3.0
<1.0
<1.0
8/22/2019
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
10/16/2020
<0.50
<0.50
<0.50
<3.0
<5.0
<1.0
2/2/2000
<1.0
<1.0
<1.0
<3.0
<5.0
DW-Wilkinson
10/2/2000
<1.0
<1.0
<1.0
<3.0
<5.0
6/21/2001
<1.0
<1.0
<1.0
<3.0
<5.0
7/10/2002
<1.0
<1.0
<1.0
<1.0
<5.0
DW-Wright
6/28/2000
<2.0
<2.0
<2.0
<4.0
<2.0
Notes:
All concentrations reported in micrograms per liter (pg/1)
2L Groundwater Quality Standard = NCAC 15A 2L .0202 Groundwater Quality Standard
MTBE = Methyl-tert-butyl ether
BTEX, MTBE, and naphthalene analyses by USEPA Method 8260D.
< = Not detected above reporting limit.
J = Estimated value below reporting limit.
Bold values indicate constituent detection.
CV-1 = 1 st carbon vessel effluent.
CV-2 = 2nd carbon vessel effluent.
Influent = for point -of -entry system.
Effluent = for point -of -entry system.
(1) DW-Crowe (MW-16) used as monitoring well only.
(2) New well installed in 2010.
(3) Tucker sold to Stief 3/2014.
(4) Sample re -run.
Page 12 of 12
FIGURES
�1
APEX
r
N
USGS The National Map: National Boundaries Dataset, 3DEP Elevation
Program, Geographic Names Information System, National Hydrography
Dataset, National Land Cover Database, National Structures Dataset, and
National Transportation Dataset; USGS Global Ecosystems; U.S. Census
Bureau TIGER/Line data; USFS Road Data; Natural Earth Data; U.S.
0 1,000 2,000
Departme'rt`bf.State Humanitarian Information Unit; and NOAA National
Centers for Environmental Information, U.S. Coastal Relief Model. Data
Feet
refreshed October 2018.
CHECK BY: AS
SITE LOCATION MAP
COLONIAL PIPELINE COMPANY
KANNAPOLIS BOOSTER STATION
CONCORD, NORTH CAROLINA
� r„
APEX
L X
FIGURE
DRAWN BY: SP
DATE: 10/19/2020
SCALE: AS SHOWN
CAD NO.: CPC19014.001
PRJ NO.: CPC20107.001
Jilt
et
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40
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tIN
,,, .i�', m a ..� �,::• I�, �„ ,yc. �..• POTABLE WATER SUPPLY WELL MW_1 • •
' ' `'" �• C a 1 `' • :7 `� MW-17 d Vf Wr13 r.
i
CHECK BY AS
•�� '•^� - t - » DRAWN BY BM SITE PLAN
DATE 10/19/20
COLONIAL PIPELINE COMPANY
CAD NO. CPC19014.001 KANNAPOLIS BOOSTER STATION
PRJ NO. CPC20107.001 CONCORD, NORTH CAROLINA
LEGEND
- - PROPERTY LINE
x FENCE LINE
COLONIAL PIPELINEI
ANCILLARY PIPING
Q5 MW-1 SHALLOW MONITORING WELL
MW-2 DEEP MONITORING WELL
MW-11 ABANDONED MONITORING WELL
PW RW-15 RECOVERY WELL
PZ-1 PIEZOMETER
® PIG -SIGNAL
SCALE IN FEET
0 40 80 160
WELL DESIGNATION
UPDATE
FORMER WELL NAME
NEW WELL NAME
MW-1
MW-1
MW-2
ABANDONED
—
MW-2D
MW-2
MW-3
MW-3
MW-4
MW-4
MW-5
MW-5
MW-6
MW-6
MW-6D
MW-7
MW-7
ABANDONED
—
MW-8
MW-8
MW-9D
MW-9
MW-10D
MW-10
MW-11
ABANDONED
MW-11 ABANDONED
MW-12D
MW-12
MW-13
MW 13
MW-14
ABANDONED
—
MW-15
ABANDONED
MW-16
ABANDONED
—
MW-17
MW-14
MW-17D
RECOVERY WELL
MW-15
CROWE WELL
MW-16
TR-1U
MW-17
TR-11)
MW-18
TR-2U
iMW-19
TR-2D
MW-20
TR-3U
MW-21
TR-3D
MW-22
NOTES: 1. ANCILLARY PIPING AND COLONIAL PIPELINE
LOCATIONS ARE APPROXIMATE AND ARE FOR FIGURE
PURPOSES ONLY.
2. MAP BASED OFF DRAWING ENTITLED "FACILITY MAP"
DATED APRIL 1, 2014 COMPLETED BY PROGRESSIVE
ENGINEERING AND CONSTRUCTION, INC.
APEX'
FIGURE
2
ASPHALT PAVED
U
U
CD11
CHECK BY AS
DRAWN BY BM
DATE 10/19/20
SCALE AS SHOWN
CAD NO. CPC19014.001
PRJ NO. CPC20107.001
LEGEND
- - - PROPERTY LINE
x FENCE LINE
COLONIAL PIPELINE
ANCILLARY PIPING
SB-1 RECOVERY WELL
SB-7 RECOVERY WELL ABANDONED
BV-1 BIO-VENTING WELL
BS-1 BIO-SPARGE WELL
B-9
SCALE IN FEET
0 10 20 40
-5 RW-01
-1
NOTES: 1. ANCILLARY PIPING AND COLONIAL PIPELINE
LOCATIONS ARE APPROXIMATE AND ARE FOR FIGURE
PURPOSES ONLY.
2. MAP BASED OFF DRAWING ENTITLED "FACILITY MAP"
z
DATED APRIL 1, 2014 COMPLETED BY PROGRESSIVE
ENGINEERING AND CONSTRUCTION, INC.
SB-12
FIGURE
RECOVERY WELL LOCATIONS
AUGUST 6, 2020
COLONIAL PIPELINE COMPANY
•
3
KANNAPOLIS BOOSTER STATION
r
APEX
CONCORD, NORTH CAROLINA
DUKE POWER COMPANY
------ ------ ------ ------
I
I X
1
11
x
1
I � x O MW-23
1 x �
1
Ix ASPHALT PAYED
I
1
I O
m
1 MW
1 x SUB STATION d Q5
I LINE 2
MANIFOLD
1 3
rn
I
I O
X- �m
" OW
1 O
24" CMP MW-5
1
LINE 1
- - - - - MANIFOLD
x
L T77
1 MW-6 M 7
I x
1
1
I
1
1 x
I MW-1
1
1 ,1ph
I MW-12
1
1-RETENTION POND )UNE
G SIGNAL
x POTABLE WATER /
1 SUPPLY WELL
1 QQQ
1 x
MW-15
(RW-15)
x
5MW-1�X
1
PRJ NO. CPC20107.001
I 1
1
I
1
1
x
I
Fe Mol
LEGEND
— — PROPERTY LINE
x FENCE LINE
COLONIAL PIPELINE'
ANCILLARY PIPING'
Q5 MW-1 SHALLOW MONITORING WELL
MW-2 DEEP MONITORING WELL
MW-11 ABANDONED MONITORING WELL
9 RW-15 RECOVERY WELL
O PZ-1 PIEZOMETER
® PIG —SIGNAL
5—FOOT GROUNDWATER
-7A5 POTENTIOMETRIC CONTOUR
INTERVAL (FT. MSL)
(DASHED WHERE INFERRED)
717.00 GROUNDWATER ELEVATION
(FT. MSL)
ESTIMATED GROUNDWATER
FLOW DIRECTION
SCALE IN FEET
0 40 80 160
WELL DESIGNATION UPDATE
FORMER WELL NAME
NEW WELL NAME
MW-1
MW-1
MW-2
ABANDONED
-
MW-2D
MW-2
MW-3
MW-3
MW-4
MW-4
MW-5
MW-5
MW-6
MW-6
MW-6D
MW-7
MW-7
ABANDONED
MW-8
MW-8
MW-9D
MW-9
MW-10D
MW-10
MW-11
ABANDONED
MW-11 ABANDONED
MW-12D
MW-12
MW-13
MW-13
MW-14
ABANDONED
MW-15
ABANDONED
-
MW-16
ABANDONED
-
MW-17
MW-14
MW-17D RECOVERY WELL
MW-15
CROWE WELL
MW-16
TR-1U
MW-17
TR-iD
MW-18
TR-2U
MW-19
TR-2D
MW-20
TR-3U
MW-21
TR-30
MW-22
NOTES: 1. ANCILLARY PIPING AND COLONIAL PIPELINE
LOCATIONS ARE APPROXIMATE AND ARE FOR FIGURE
PURPOSES ONLY.
2. MAP BASED OFF DRAWING ENTITLED "FACILITY MAP"
DATED APRIL 1, 2014 COMPLETED BY PROGRESSIVE
ENGINEERING AND CONSTRUCTION, INC.
GROUNDWATER POTENTIOMETRIC SURFACE MAP
SURFICIAL SAPROLITE UNIT — AUGUST 6, 2020
COLONIAL PIPELINE COMPANY
KANNAPOLIS BOOSTER STATION
CONCORD, NORTH CAROLINA
APEX
FIGURE
4
LEGEND
1 —
I
1 x
1 �x -
I X
x
x �x�
1
1
MW-4
I
<0.50
MW-23
1 I X ASPHALT PAYED
� I
� 1
DUKE POWER COMPANY I o i1
V-1
1 BS-1
1 h SUB STATION �r MW-24 BV-2
I o 4.9
U MANI 2 E
1 3 BV15 i
I N
----� BS-3----fir
I x vS 0
�m BV-3 (SVE-5)
cW
'III I MW-5 1
1 24" CMP
1 _
LINE 1 --o -
- - — - - MANIFOLD %
1 M -7
I MW-6<0.5 —
x
1
1
I
1
> 1 x
3 I MW-1 SP
� snT
611
TREATMENT
_= 1 SYSTEM PAD
(9
� x
I MW-12
a 1 UNE 1
r 1 RETENTION POND Pic SIGNAL
I & o
x POTABLE WATER SUPPLY WELL1;e* p� o
Io 4 ..4 MaW-17
1 b0 }
1 X o `✓/�1
i
I MW-15
(RW-15�
/x
jPU.4bJ � i
W-18
IMW-14
�x
DATE 10/19/20
SCALE AS SHOWN
CAD NO. CPC19014.001
PRJ NO. CPC20107.001
MW-11
e
6 Mol
BENZENE ISOCONCENTRATION MAP
AUGUST 6, 2020
COLONIAL PIPELINE COMPANY
KANNAPOLIS BOOSTER STATION
CONCORD, NORTH CAROLINA
0 MW-1
MW-2
MW-11
9 RW-1
O PZ-1
Q5 BV-1
Q5 BS-1
—1
4.9
<0.50
PROPERTY LINE
FENCE LINE
COLONIAL PIPELINE'
ANCILLARY PIPING'
SHALLOW MONITORING WELL
DEEP MONITORING WELL
ABANDONED MONITORING WELL
RECOVERY WELL
PIEZOMETER
PIG —SIGNAL
BIO—VENTING WELL
BIO—SPARGE WELL
BENZENE ISOCONTOUR (DASHED
WHERE INFERRED)
BENZENE CONCENTRATION (Ng/L)
2B STANDARD FOR BENZENE IS
1.19 MICROGRAM PER LITER (pg/L)
2L STANDARD FOR BENZENE
IS 1 Ng/L
BENZENE NOT DETECTED AT OR
ABOVE REPORTING LIMIT
ESTIMATED CONCENTRATION
BETWEEN METHOD DETECTION LIMIT
AND REPORTING LIMIT
SCALE IN FEET
0 40 80 160
WELL DESIGNATION UPDATE
FORMER WELL NAME
NEW WELL NAME
MW-1
MW-1
MW-2
ABANDONED
MW-2D
MW-2
MW-3
MW-3
MW-4
MW-4
MW-5
MW-5
MW-6
MW-6
MW-6D
MW-7
MW-7
ABANDONED
MW-8
MW-8
MW-9D
MW-9
MW-10D
MW-10
MW-11
ABANDONED
MW-11 ABANDONED
MW-12D
MW-12
MW-13
MW-13
MW-14
ABANDONED
-
MW-15
(ABANDONED)-
MW-16
ABANDONED
MW-17
MW-14
MW-17D RECOVERY WELL
MW-15
CROWE WELL
MW-16
TR-1U
MW-17
TR-1D
MW-18
TR-2U
MW-19
TR-2D
MW-20
TR-3U
MW-21
TR-3D
MW-22
NOTES: 1. ANCILLARY PIPING AND COLONIAL PIPELINE
LOCATIONS ARE APPROXIMATE AND ARE FOR FIGURE
PURPOSES ONLY.
2. MAP BASED OFF DRAWING ENTITLED "FACILITY MAP"
DATED APRIL 1, 2014 COMPLETED BY PROGRESSIVE
ENGINEERING AND CONSTRUCTION, INC.
FIGURE
5
APEX
APPENDIX A
GROUNDWATER SAMPLING FIELD LOGS
r,
APEX
A
APEX
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: Wzp Time: /Zw Monitor Well Number:
Apex Personnel: Purpose of Sampling Event:
Location (Site/Facility Name): Weatherrremp: �O
circle:
Measuring Point (MP): top of casing top cf ground Low Flow purge rate: _ mumin Well Type: surface completion, ahoueg e
Depth to Product (MP): Well Cover Bolted: Yes to Well Screen Length (feet): 5, 10, 15, Q Other.
Depth to Water (MP): %- Well Cap Condition: cod Replaced Pump Intake depth (Feet above TD):
Total Depth of Well (MP):J9. 77- (0.1') Well Cap Locked: Y No Replaced Purging/Sampling Device: � Peristaltic, Monsoon, Grundfos;
Water Column thickness MY IZ.07 Well Tag Present: No OTHER: ,
Well Material: PV Stainless Steel, Other: Well Info. On Tag: No Noticeable Odor.
Well pad condition: Cracked Replace Well Diameter (inches) 78 Sample Color.
Time
Depth to
Water
(MP) I
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
erQualityComments
Field Comments/Site ConditionA-tgtc.:
5vol c L•zA
1 v o ( Z
min.
Feet
Gallons
Liters
•0 c '.
m5/cm r to
SU
mV
mg/L
NTU
Initial
g, q
Zg
Z/-Z 7
6. 62
95.7-
IV?
Z9.1
11
El
'f3N
g?
.L
,q
(O
'0-12
C,
it, 1
!
!03
.z
-Criteria
0.33'
0.2-0.5 Umin
+/_ 1.0
+/-.3%
Purge Volume Conversions 1"= 0.04. 1.5" = 0c9, 2" = 0.11, 3" = 0.38, 4" = 0.66, 6" =1.5, 8" = 2.6, 10" =4.1
Water quality parameters Collected with: YSI 556, Hodba U-52, anna turbidity; Other:
Parameters Stabilized (circle): YES NO If no, why?
Samples collected Analysis Bottle Type Preservative
MLu-N VX (10Z. VO IC H L�
mli )k
Lab Sample date
SW&kl 2-1b-2Uzo
Sample Time
/Z:Z5
Page_ of Pages Version 1.2020
i`
APFX
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: I% Time: Z Monitor Well Number: '
Apex Personnel: Purpose of Sampling Event:
Location (SitefFacility Name): r Weather/Temp:
Measuring Point (MP): to of casing top of ground Low Flow purge rate: mUmin Well Type: surface completion, <2!ve m
Depth to Product (MP): — Well Cover Bolted: Yes N® Well Screen Length (feet): 5, 10 15,, 20, Other.
Depth to Water (MP): 16 - ! ZJ. Well Cap Condition: ZD ^^'' �Replaced Pump Intake depth (Feet above TD): --
Total Depth of Well (MP): / t%, 7 5 (0 1') Well Cap Locked: Yes Np_JReplaced Purging/Sampling Devioe:yjr, PedstaltiG Monsoon, Grundfos;
Water Column thickness (ft): Ll • 33r Well Tag Present: Yes No OTHER:
Well Material: 10Stainless Steel, Other. Well Info. On Tag: t Yes No Noticeable Odor.
Well pad condition: .20 Cracked Replace Well Diameter (inches) 2 Sample Color t/t
Time
Depth to
Water
(MP)
Well volume
gaited
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
I SS
` V0) = ,p� C, r+U'
15
3 Ju\ = Z.50
�I:yU
min.
Feet
Gallons
Liters
Crde.F
C
m5 c cm,lm-
SU
mV
mg/L
NTU
Initial
�Z
30
1 fit
•SS
7-
6
-7s
!bp
2.oS
-t-)
Criteria
0.33'
0.2-0.5 Umin
+/-1.0
1 +/- 3%
1 - 0.1
+/-10 mV
+/- 33m L
+
Purge Volume Conversions: 1"= 0.04, 1. = 0.09, T' = o.11, s" = u.an, a-= u.., a" = ia, o-= <.o, -iu
Water quality parameters Collected with: YSI 556, Horiba U-52, a turbidi Other.
Parameters Stabilized (circle): YES NO If no,
Samples collected Analysis r}
Page of Pages
Bottle Type Preservative Lab
"P, 14 c.1- 15wx41
Sample date Sample Time
Zf(SIZino /I"clo
Version 1.2020
��
APEX
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: .Z 41142is 2d r Time: q%$S Monitor Well Number:
Apex Personnel: /J p�: ryt&= Purpose of Sampling Event:
per
Location (Site/Facility Name): dwi Weather/Temp:
Measuring Point (MP): of das' top of ground Low Flow purge rate: mUmin Well Type: surface completion, above gratle
Well Cover Bolted: Yes o
Depth to Product (MP): _ Well Screen Length (feet): 5, 62 15, 20, Other.
Depth to Water MP : 6o. 16 Well Cap Condition: Replaced —
P ( ) � Pump Intake depth (Feet above TD):
Total Depth of Well (MP): 17-- 1 (0.1Well Cap Locked: Yes .9 Replaced Purging/Sampling Device: ai Peristaltic, Monsoon, Grundfos;
Water Column thickness (ft): 17 , jf5 Well Tag Present: Yes ® OTHER:
Well Material: <&� Stainless Steel, Other. Well Info. On Tag: Yes GO -)Noticeable Odor.
Well pad condition: J' Cracked Replace Well Diameter (inches) 2 Sample Color. r&."
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
3 Va1 rrj , (orc
i Vol
z vat =
min.
Feet
Gallons
Liters
.Crtl..F
m5/c1C'e-S/c
SU
mV
mg/L
NTU
Initial
6-
2m'�
/.7y
/t%%
z Fi
11•
►0:
s
r.
ty 7
ASZ
-5s
r.Y
%.7
0
3•15
(,.75
A.-S
3.1d
z 3
10:
.5Z
S• 7S
Orq7,23,
L , g
((,
Z,v
Criteria 1
Pume Volume
0.33' 1
ponvemions:
10.2-0.5
P' = 0,0 . 1.s' =
Umin
0.09. 9 = 0.1]. 3"
= 0 38. 4-= p86
1
6" =1 .9 8" = o a
+/- 0.1
1n" = e 1
+/_ 10 mV
+/_ 0.3m L
+/_ 10%
Water quality parameters Collected with: YSI 556, Horiba U-52, �lianna tur Other:
Parameters Stabilized (circle): YES NO If no, why?
Samples collected Analysis Bottle Type
MW-S (3s�5) voc 662 I/6A
POMM
Page of Pages
Preservative Lab Sample date
YCL 5keal 7-/1s17b
Sample Time
10: ZS
Version 1.2020
®�
APCX
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: 207o Time: WS0 Monitor Well Number: —13
Apex Personnel: K I Cmu i r.--f z Purpose of Sampling
Location (Site/Facility Name): CPC weather/Temp: ('7^
Measuring Point (MP): of resin top of ground Low Flow purge rate: mUmin Well Type: surface completion,
Depth to Product (MP): Well Cover Bolted: Yes 6 Well Screen Length (feet): 5, 10, 15, d0, Other.
Depth to Water (MP): �. �o Z- Well Cap Condition: Go //CC Replaced Pump Intake depth (Feet above TD):
Well Cap Locked: Yes l-NW Replaced
Total Depth of Well (MP): iv•51% (0.1 Purging/Sampling Device: der Peristaltic, Monsoon, Grundfos;
Water Column thickness(ft): 2D.4� Well Tag Present Yes OTHER: II,,
Well Material: C Stainless Steel, Other. Well Info. On Tag: Yes No Noticeable Odor. '7Ci
Well pad wntlitiom Goo Cracked Replace Well Diameter (inches) 2 Sample Color. p
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
3v0(_
IVO` = �.�
�voF :� 7.Ov
min.
Feet
Gallons
Liters
.c •F
m5/an
SU
mV
mg/L
NTU
Initial
SjS
12.
539
7.16
7•
is
Z
o
ra't
4
— 1.'f
1.
?$
lt.
DFS
o
k7
-
Criteria
P.m.VNume 0onv.M.ns l'=u.ua, l.J"=V.(n,z V.1/,J=u.x,v=u. ,
Water quality parameters Collected with: YSI 556, Honba U-52, -Hama turbid+ty;
Parameters Stabilized (circle): YES NO If no,
Samples collected
MW I's (3"I-S)
Other:
Analysis Bottle Tyne
VC44 cooz Vol h
�C-xrn
Preservative Lab Sample date
k-L 56j l 211s zo
Sample Time
v� -ZZ;
Page_ of Pages Version 1.2020
Art
A Dry
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: I t$IZcI Time: i i rU Monitor Well Number: IMN 24-
Apex Personnel: _l.•r.. m.e<a,...wr_ Purpose of Sampling Event: in.,•,' 4H n
Location (Site/Facility Name): CfC- IZuw -W7 Weather/Temp: C (/+1 C (,,I -j
it e:
Measuring Point (MP): o ms n top of ground Low Flow purge rate: mUm/i�in� Well Type: surface completion, ve gra
Depth to Product (MP): Well Cover Bolted: Yes c1Yo+ Well Screen Length (feet): 5,015, 20, Other (G - Z U
Depth to Water (MP): 5 • u Well Cap Condition: Replaced Pump Intake depth (Feet above TD): —
Total Depth of Well (MP): 2.2• a a (0.1') Well Cap Locked: Y i No Replaced Purging/Sampling Device: <jBail , Peristaltic, Monsoon, Grundfos:
Water Column thickness (ft)Well Tag Present No OTHER:
Well Material:<5�,>Stainless Steel, Other. Well Info. On Tag: VTgY, No Noticeable Odor: St. o.W-- rk, Sur e.
Well pad condition: � Cracked Replace Well Diameter (inches) Sample Color.. C i .,.d tj rat.
Field Comments/Site Conditions, etc.:
Time
Depth to
Water
Well volume
Low Flow
Temp.
S c Cond.
pH
ORP
DO
Turbidity
(MP)
gaited
Vol Purged
Water Quality Comments
v
1JL 1 p , y/
Y
Feet
Gallons
Liters
Grde:
Circle:
SU
mV
mg/L
NTU
min.
•C 'P
ms cm S/
Initial
C-,(g
12f4
� 30
3
—
w.sG
3z (
G 141.—>
6
! . 41
or-
—
Z(.a
3Z
CZ,;--Sir-.l..S'3
0tZ,.
12i
I r
2.2t
t Zs
—
ZI.Zt
St4
I G•4t
-Ge.(
'z.o:
vrc
io.yk
1
Criteria
0.33'
0.2-0.5 Umin
+/- 1.0
+/- 3%
+/- 0.1
+/-10 mV
+/- 0.3m
+/-10%
Purge Volume conversions: 1=p.pg1.C"=u.un, z"=unq s=uao, n-=u.ao,o =w,o -. <.o, io
Water quality parameters Collected with:
�=
YSI 556, Hod��+
ba U-52, ha turbidity;
Other:
Parameters Stabilized (circle): YES
(g� If no, why? Z U ✓>
Samples collected
Analysis
Bottle Type
Preservative Lab Sample date Sample Time
J'P�e
v ^
' Z No `e {Zu r-L 1,
uytw- z4
s1/a
3,tN
a�
Page of Pages
\3 �A.-
W
� Version 1.2020
Ark
APrX
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Tme: 1140 Monitor Well Number: 'I9kr Z S^
Date: I b 2U Purpose of Sampling Event: S(-...' >_.-_n
Apex Pers^^^.�t9LGr 4if
'
Location (Site/Facility Name): G Weather/Temp: Cc` r c r" /y
i e:
Measuring Point (MP): t of ce i top of ground Low Flow purge rate: mUmWell Type: surface completion, a ve grad
Depth to Product (MP): Well Cover Bolted: Yes � Well Screen Length (feet): 5, (1 7 15, 20, Other.
Depth to Water (MP): �{• Z4 Well Cap Condition: V29g� Replaced Pump Intake depth (Feet above TD):
Total Depth of Well (MP): 21, Z S (0.1') Well Cap Locked: es No Replaced Purging/Sampling Device: ilea Peristaltic, Monsoon, Grundfos,
Water Column thickness (ft): ILL. US Well Tag Present: (!92 No OTHER:
Well Material: Ko Stainless Steel, Other. Well Info. On Tag: !f3? No Noticeable Odor.A[r
Well pad condition: 60 Cracked Replace Well Diameter (inches) 2 Sample Color. C (4 q Y-
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Tem P
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
'�• / (. S_,
b.,o�w
min.
Feet
Gallons
Liters
Grde:
c ' ,F
0mle:
MS/cm S/cm
SU
mV
mg/L
NTU
Initial
�• �'�
�y
i b: Eq
;
G, 6
Z5. I
1. 15
(3.8
IWS7
33
s�
—
I%S-4
44el
(,,43
53.3
11,3341413�srrzh
litm
�I✓I�+
S'
—
20,o�.j
43h
6.7-9
Ce3:z
1,W,
1 41-7-
usr
Za1Z
441
G-ZI
717
1.53
7o
v:
E.sc
Criteria
0.33'
0.2-0.5 Umin
+/-1-0
+/- 3%
+/- 0.1
+/-10 mV
+/- 0.3m
+/-10%
Purge volume conversionsn-=UA4, ix'=u.ue,z=u.igs=v.00, 4 =u.
Water quality parameters Collected with: YSI 556, Horiba U-52, ann idity;
Parameters Stabilized (circle): YES If no, why. S tY
Samples collected Analysis Bottle Type Preservative Lab Sample date
r
V,luo-2�— VoL vt4uL Sti wt. 2�rSl-to
Suu.
i �v\
vey�-
Page of Pages r4
Sample Time
IZLO
Version 1.2020
AN
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: Z(t $ U Time: 64. S- Monitor Well Number. tM� -- Z Y+A
Apex Personnel: , (. - wtcc- •'A; Purpose of Sampling Event: L.,f
Location(Site/Faclity Name): Gpk_ K'-wMal•A Weather(remp: (�( 6(�,jV
Measuring Point (MP): p ofcasi [op of ground Low Flow purge rate: mL/min Well Type: surface completion, hove g e
Depth to Product (MP): Well Cover Bolted: Yes o Well Screen Length (feet): 010, 15, 20, Other. G k -
Depth to Water (MP): / S . 44 Well Cap Condition: pod Replaced Pump Intake depth (Feet above TD): —
Total Depth of Well (MP): 76 • -�' 5 (0.1) Well Cap Locked: 'es it No Replaced purging/Sampling Device: edstaltic, Monsoon, Grundfos;
Water Column thickness (ft): 5 t � U 6_Well Tag Present es `' No OTHER:
Well Material: 'C0) Stainless Steel, Other. Well Info. On Tag: No Noticeable Odor. AI
Well pad condition: Cracked Replace Well Diameter (inches) Z - Sample Color r af(L
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
P-
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments(Site Conditions, etc.:
w(= Ze7. Ci 5„cv)
min.
Feet
Gallons
Liters
f�rtle:
•C "P
Circle:
cos cm S/c
SU
mV
m L
�
NTU
Initial
Zo,A+s
54`7
(,•(ry
-c13.�
`L,fi3
Z�-4
(A u L
l
I U
Z0• I ti
4 (0 -7
(" 2-
5 �G
Z.
T 1. 0
(6)
tS,ox
Zo
Z0,1
S
S4
-31f,
Z.47-
;IZ6
14.06
Za U
GF °I
6.14
-GG.(,
2.e.
3Z.5'
Criteria
0.33'
0.2-0.5 L/min
+/-1.0
+/_ 30�
+/- 0.1
+/- 10 mV
Purge Volume Convereons: 1-=0.04.15=0.0e, 2"=U.L,a=U.ao,ti=U.00,o =i.D. 0 -C.o, w - »'
Water quality parameters Collected with: YSI 556, Hodba U-52, Han a turbidity;
Parameters Stabilized (cirUe): YES C) If no, why?-3 U0n
Samples collected
Analysis
Bottle Type
Preservative
Lab
Sample date Sample Time
iVIW-2S �J
VDc.
1;oA
f'(`k
UU,
Svcx
)
�'u
Page__�__of
Version 1.2020
_Pages
'Awk
A fD1= Y
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: August 6, 2020 Time: r b i -S Monitor Well Number: I ��
Apex Personnel: Coatta Finlon, Naomi Fretz Purpose of Sampling Event: Semi -Annual
Location (Site/Facility Name): CPC Kannapolis Weather/Temp: St1.
Circle:
Measuring Point (MP K. p of casi top of ground Low Flow purge rate: N/A mUmin Well Type: surface completion, ve rad
Depth to Product (MP): Well Cover Bolted: Yes Well Screen Length (feet): 5, 10, 15, 20, Other:
Depth to Water (MP): :ct)d Well Cap Condition: Replaced Pump Intake depth (Feet above TD):
&No
apocPurTotal Depth of Well (MP): (0.1') 9 9 pWell CLked: Replaced in/Sam lin9 Device Peristaltic, Monsoon, Grundfos;
2g
Water Column thickness (ft): Well Tag Present: es No OTHER:
Well Material: QZI) Stainless Steel, Other: Well Info. On Tag: No Noticeable Odor:
Well pad condition: oo Cracked Replace Well Diameter (inches) Z Sample Color:
Time
Depth to
Water
(MP)
Well volume
gaited
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
min.
Feet
Gallons
Liters
�CCircle:
mS/cm Circle: S/
SU
mV
mg/L
NTU
Initial
Gr.
`y
;�
. (-
3 3►�
L�� ,�j
�• bs
12. 62
2610.1
6. bb
M.
(9a S
z
Mal
1.60
l
Criteria
0.33'
0.2-0.5 L/min
1 +/- 1.0
1 +/- 3%
+/- 0.1
+/- 10 mV
+/- 0.3m /L
+/- 10%
Y'Urye VVIUrIIC VVIIVCr SIVIIJ. I - V.V4, I.V -V.Vz�, L - V. I /, J - V.00,' - V.VV, V - I.V, O - L.V, IV - V. I
Water quality parameters Collected with: Horiba U-52, Hanna turbidity; Other:
Parameters Stabilized (circle): YES NO If no, why?
Samples collected Analysis
Name: BTEX (8260B) Other
Napthalene (6200B) Other 13
uk MTBE (8260B) 12
Bottle Type Preservative Lab Sample date Sample Time
VOA HCI Shealy(Pace)t�="�
Other Other
Other Other
Other Other
Page of Pages Version 1.2020
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: August 6, 2020 Time: 127.S Monitor Well Number:_ ow
Apex Personnel: Coatta Finlon, Naomi Fretz Purpose of Sampling Event: Semi -Annual
Location (Site/Facility Name): CPC Kannapolis Weather/Temp: fS SOIL
-
Circle:
Measuring Point (MP): of ca in top of ground Low Flow purge rate: N/A mUmin Well Type: surface completion,
Depth to Product (MP): Well Cover Bolted: Yes No Well Screen Length (feet): 5, 10, 15, 20, Other:
Depth to Water (MP): Well Cap Condition: Replaced Pump Intake depth (Feet above TD):
e0l
Total Depth of Well (MP): �3 (0.1') Well Cap Locked: No Replaced Purging/Sampling Device: Peristaltic, Monsoon, Grundfos;
Water Column thickness (ft): �. 7_0 Well Tag Present: No OTHER: Hydrasleeve
,Well Material: Stainless Steel, Other: Well Info. On Tag: Yes No Noticeable Odor:
Well pad condition: Good Cracked Replace Well Diameter (inches) Z—� Sample Color.
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
min.
Feet
Gallons
Liters
oCircle:
ms/cm Circle:
S/c
SU
mV
mg/L
NTU
Initial
v
r
UV
."
9
Criteria
0.33'
0.2-0.5 L/min
+/- 1.0
+/- 3%
+/- 0.1
+/- 10 mVI
0.3mg/L
+T 10%
Purge Volume Conversions 1" = U.U4, I.b" = U.Ua, z = U.1 1, 5 = U.su, 4' = U.bb, b = 1.0, 0 = L.0, I = 4. 1
Water quality parameters Collected with: 1556 oriba U-52, Hanna turbidity
Parameters Stabilized (circle): YES NO If no, why?
Samples collected Analysis
Name: BTEX (8260B) Other
Napthalene (6200B) Other
3!§�k95 MTBE (8260B)
Other:
Bottle Type Preservative Lab Sampled te Sample Time
VOA HCI Shealy(Pace) Z C/h_
Other Other
Other Other
Other Other
Page of Pages Version 1.2020
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
`- Date: August 6, 2020 Time: 17-5 In Monitor Well Number:
Apex Personnel: Coatta Finlon, Naomi Fretz Purpose of Sampling Event: Semi -Annual
Location (Site/Facility Name): CPC Kannapolis Weather/Temp: IsS —
rc e:
Measuring Point (MP): top of casing top of ground Low Flow purge rate: N/A mL/min Well Type: surface completion, nrasle
Depth to Product (MP): Well Cover Bolted: Yes No Well Screen Length (feet): 5, 10, 15, 20, Other:
Depth to Water (MP): ('0 . Well Cap Condition: G Replaced Pump Intake depth (Feet above TD):
Total Depth of Well (MP): • rJ� (0.1') Well Cap Locked: Yes No Replaced Purging/Sampling Devic Bail Peristaltic, Monsoon, Grundfos;
Water Column thickness (ft): %. 8 7 Well Tag Present: Yes No OTHER: Hydrasleeve
Well Material: �tainless Steel, Other: Well Info. On Tag: Yes No Noticeable Odor:
Well pad condition-ED Cracked Replace Well Diameter (inches) Z.`Sample Color:
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
min.
Feet
Gallons
Liters
Circle: �C
°F
Circle:
mS/cm S/Cm
Su
mV
mg/L
NTU
Initial
7'
c )
, G
g
,fitb+ y
24.7
319.37
.S
Criteria
i 0.33'
0.2-0.5 Umin
+/- 1.0
1 +/- 3%
1 +/- 0.1
+/- 10 mV
+/- 0.3mg/L
+/- 10%
Purge Volume Conversions: 1" = 0.04, 1.5' = 0.09, 2" = 0.17, 3" = 0.3b, 4" = U.bb, b" = 1.b, b.. = 2.b, ]U" = 4.1
Water quality parameters Collected with: � Horiba U-52, Hanna turbidity;
Parameters Stabilized (circle): YES NO If no, why?
Samples collected Analysis
Name: e BTEX (8260B) Othere
;z
GNapthalene (6200B)12
Other MTBE (8260B)
Other:
Bottle Type Preservative Lab Sample date Sample Time
VOA HCI Shealy(Pace) (_ Z.0 13 0 j
Other Other
Other Other
Other Other
Page 1 of 1 Pages Version 1.2020
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: August 6, 2020 Time: 131.95 Monitor Well Number:
Apex Personnel: Coatta Finlon, Naomi Fretz Purpose of Sampling Event: Semi -Annual
Location (Site/Facility Name): CPC Kannapolis Weather/Temp: 5 S
Circle:
Measuring Point (MP): o sin top of ground Low Flow purge rate: N/A mL/min Well Type: surface completion, bove grade
Depth to Product (MP): Well Cover Bolted: Yes Well Screen Length (feet): 5, 10, 15, 20, Other:
Depth to Water (MP): ,q Well Cap Condition: oo Replaced Pump Intake depth (Feet above TD):
Total Depth of Well (MP):? 2 (0.1') Well Cap Locked: Ye No Replaced Purging/Sampling Device: ai Peristaltic, Monsoon, Grundfos;
Water Column thickness (ft): Well Tag Present: No OTHER:
Well Material: VC, Stainless Steel, Other: Well Info. On Tag: Yes o Noticeable Odor:
Well pad condition: CDCracked Replace Well Diameter (inches) 2'µ Sample Color:
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
min.
Feet
Gallons
Liters
Circle:
mS/cm Circle: S/c
SU
mV
mg/L
NTU
Initial
�. 0
�
O• g
o (o
/
yy
�1. 66
5�
23 .
g55.5
-7
�1.
a
p
Criteria
0.33'
0.2-0.5 Umin
+/- 1.0
+/- 3%
+/- 0.1
+/- 10 mV
+/- 0.3mg/L
+/- 10%
Purge Volume Conversions: 1" = 0.04, 1.5" = 0.09, 2" = 0.17, 3" = 0.38, 4" = 0.66, 6" = 1.5, 8" = 2.6, 10" = 4.1
Water quality parameters Collected with: SI 556 Horiba U-52, Hanna turbidity; Other:
Parameters Stabilized (circle): YES NO
If no, why?.
Samples collected
NAnalysis
Name: 1' 1� -137 BTEX (8260B) Other
Napthalene (6200B) Othere
5 MTBE (8260B)
Bottle Type Preservative Lab
VOA HCI Shealy(Pace)
Other Other
Other Other
Other Other
Sample date Sample Time
Z- t •--Lo j 33 �) .
Page of Pages Version 1.2020
A rDF-Z '*k/
A IIZ20
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: -August 6, 2020 Time: ICAS Monitor Well Number: Mt A
Apex Personnel: Coatta Finlon, Naomi Fretz Purpose of Sampling Event: Semi -Annual
Location (Site/Facility Name): CPC Kannapolis Weather/Temp:
Circle:
Measuring Point (MP): p of cas _ top of ground Low Flow purge rate: N/A mL/min Well Type: surface completion, ab�grade
Depth to Product (MP): Well Cover Bolted: Yes No Well Screen Length (feet): 5, 10, 15, 20, Other:
Depth to Water (MP): C0.06 Well Cap Condition: Replaced Pump Intake depth (Feet above TD):
Total Depth of Well (MP): 2-0 (0.1') Well Cap Locked: No Replaced Purging/Sampling Device: Bailer Peristaltic, Monsoon, Grundfos;
Water Column thickness (ft). 3. Well Tag Present: ® No OTHER: Hydrasleeve
Well Material: VC, Stainless Steel, Other: Well Info. On Tag: Yes No Noticeable Odor:
Well pad condition:(B Cracked Replace Well Diameter (inches) " Sample Color: CY bAdit C
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
min.
Feet
Gallons
Liters
ircle:
°F
Circle:
mS/cm S/cm
SU
mV
mg/L
NTU
Initial
�.�
®�
� 7
`S•Z
I i.
-.4-1
2, 40
-
to-11✓
2y.3
4.7
-V7.q
2.71
-
�-l/7q-
i/C.S
2. b
-
Criteria
0.33'
0.2-0.5 L/min
+/- 1.0
+/- 3%
+/- 0.1
1 +/- 10 mV
+/- 0.3mg/L
1 10%
rurge volume conversions: i = u.u4, i.o = u.ua, c = u. it, o = u.Jo, 4 = V.00, o = 1.0, 0 = L.o, I V = 4. I
Water quality parameters Collected with: ( L D Horiba U-52, Hanna turbidity; Other:
Parameters Stabilized (circle): YES NO If no, why?
Samples collected Analysis Bottle Type Preservative Lab Sample date Sample Time
Name: rn U,_ Zq BTEX (82606) Other ® S: (X, ;-c l,t jVOA HCI 9C Shealy(Pace) --
Napthalene (6200B) Other fl?Ik Other x Other
Je5 MTBE (8260B) Other X Other
Other Other
Page_ of __� Pages Version 1.2020
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
AD i_V
Date: August 6, 2020 Time: IlIV Monitor Well Number: cao - 7G
Apex Personnel: Coatta Finlon, Naomi Fretz Purpose of Sampling Event: Semi -Annual
Location (Site/Facility Name): CPC Kannapolis Weather/Temp:
Circle:
Measuring Point (MP): t casl top of ground Low Flow purge rate: N/A mUmin Well Type: surface completion,0tv&-g-ralle
Depth to Water (MP): No Well Screen Length (feet): 5, 10, 15, 20, Other:
j .` Well Cap Condition: Replaced Pump Intake depth (Feet above TD):
Depth to Product (MP): Well Cover Bolted: WYe
Total Depth of Well (MP): (0.1') Well Cap Locked: No Replaced Purging/Sampling Device ai r, Peristaltic, Monsoon, Grundfos;
Water Column thickness (ft): Well Tag Present: No OTHER: u.,e
Well Material: � Stainless Steel, Other: Well Info. On Tag: No Noticeable Odor:
�t
Well pad condition(_2opA Cracked Replace Well Diameter (inches) 2 Sample Color:
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
<�
min.
Feet
Gallons
Liters
Circle:
°F
Circle:
MS/cm S/Cm
SU
mV
mg/L
NTLI
Initial
f�
nix
2L;•
�I
�7Z•3
3a g
J I
�.SS
�-
Criteria
0.33'
0.2-0.5 L/min
+/- 1.0
1 +/- 3%
1 +/- 0.1
+/- 10 mV
+/- 0.3mg/L
+T 10%
i✓urge voiume conversions: I = U.v4, 1.0 = U.Utl, L = U. 1 1, J - UAo, '4 - U.00, O - 1.0, 0 - L.O, IV - Y. I
Water quality parameters Collected with: YSI 556, Horiba U-52, Hanna turbidity; Other:
Parameters Stabilized (circle): YES NO If no, why?
Samples collected Analysis
Name: MW .2S BTEX (8260B) Other
Napthalene (620013) Other
MTBE (8260B)
Bottle Type Preservative Lab Sample date Sample Time
VOA HCI. Shealy(Pace) _ fe - r 130
Other "L Other
Other X ' Other
Other Other
Page of Pages
Version 1.2020
1
6'
APEX
APEX COMPANIES, LLC
GROUND -WATER SAMPLING LOG
Date: August 6, 2020 Time: Monitor Well Number:_Mw
Apex Personnel: Coatta Finlon, Naomi Fretz Purpose of Sampling Event: Semi -Annual
Location (Site/Facility Name): CPC Kannapolis Weather/Temp:
irc e:
Measuring Point (MP): top of casing top of ground Low Flow purge rate: N/A mL/min Well Type: surface completion, above grade
Depth to Product (MP): Well Cover Bolted: Yes 6) Well Screen Length (feet): 6 10, 15, 20, Other:
Depth to Water (MP): 2—o ms Well Cap Condition: P15V Replaced Pump Intake depth (Feet ab TD):
Total Depth of Well (MP): 74 (0.1') Well Cap Locked: e No Replaced Purging/Sampling Device: ail Peristaltic, Monsoon, Grundfos;
C Well Tag Present: e No OTHER: Hydrasleeve
Z �� Water Column thickness (ft): J
Well Material: % Stainless Steel, Other: Well Info. On Tag: No Noticeable Odor:
Well pad condition: O{o Cracked Replace Well Diameter (inches) �Sample Color:1:�a_or
Time
Depth to
Water
(MP)
Well volume
Bailed
Low Flow
Vol Purged
Temp.
Spec. Cond.
pH
ORP
DO
Turbidity
Water Quality Comments
Field Comments/Site Conditions, etc.:
min.
Feet
Gallons
Liters
Circle:
°C °F
Circle:
mS/cm S/cm
SU
mV
mg/L
NTU
Initial
LID
V-PAs
�•
Lb l
�, i
�/�
Criteria
i 0.33'
1
0.2-0.5 L/min
+/- 1.0
i +/- 3%
+/- 0.1
+/- 10 MV1
0.3mg/L
+/- 10%
Purge Volume Conversions: 1" = 0.04, 1.5" = 0.09, 2" = 17, 3" = 0.38, 4" = 0.66, 6" = 1.5, 8" = 2.6, 10" = 4.1
Water quality parameters Collected with: Y56, Horiba U-52, Hanna turbidity;
Parameters Stabilized (circle): 6 NO If no, why?
Other:
Samples c Ilected Analysis Bottle Type Preservative Lab Sample date S m le Time
Name: ffiW-W
BTEX (8260B) Other M VOA HCI Shealy(Pace)
Napthafene (6200B) Other® Other Other
f Other Other
Other Other
Page of Pages
Version 1.2020
APPENDIX B
LABORATORY ANALYTICAL REPORTS
r,
APEX
0
aceAnalytical
Report of Analysis
Apex Companies, LLC
10610 Metromont Parkway
Suite 206
Charlotte, NC 28269
Attention: Andrew Street
Project Name: CPC Kannapolis
Project Number: CPC20107
Lot Number:VB20090
Date Completed:03/04/2020
03/05/2020 3:43 PM
Approved and released by:
Lab Director - Greenville: Lucas Odom
pCC/►F�
24r�A
SOA
ANSI National Accreditation Board
A C C R E D I T E D
TESTING LABORATORY
The electronic signature above is the equivalent of a handwritten signature.
This report shall not be reproduced, except in its entirety, without the written approval of Pace Analytical Services, LLC.
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172
Tel:803-791-9700 Fax:803-791-9111 www.pacelabs.com
Page 1 of 46
PACE ANALYTICAL SERVICES, LLC
SC DHEC No: 32010001 NELAC No: E87653 NC DENR No: 329 NC Field Parameters No: 5639
Case Narrative
Apex Companies, LLC
Lot Number: VB20090
This Report of Analysis contains the analytical result(s) for the sample(s) listed on the Sample Summary
following this Case Narrative. The sample receiving date is documented in the header information
associated with each sample.
All results listed in this report relate only to the samples that are contained within this report.
Sample receipt, sample analysis, and data review have been performed in accordance with the most
current approved NELAC standards, the Pace Analytical Services, LLC ("Pace") Quality Assurance
Management Plan (QAMP), standard operating procedures (SOPS), and Pace policies. Any exceptions to
the NELAC standards, the QAMP, SOPS or policies are qualified on the results page or discussed below.
If you have any questions regarding this report please contact the Pace Project Manager listed on the
cover page.
SVOCs by GC/MS
The following sample was diluted due to the nature of the sample matrix: VB20090-005. The LOQ has
been elevated to reflect the dilution.
Pace Analytical Services, LLC (formerly Shealy Environmetal Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 2 of 46
PACE ANALYTICAL SERVICES, LLC
Sample Summary
Apex Companies, LLC
Lot Number: VB20090
Sample Number
Sample ID
Matrix
Date Sampled
Date Received
001
MW-4
Aqueous
02/18/20201225
02/20/2020
002
MW-6
Aqueous
02/18/20201140
02/20/2020
003
MW-8
Aqueous
02/18/20201025
02/20/2020
004
MW-13
Aqueous
02/18/20201125
02/20/2020
005
MW-24
Aqueous
02/18/20201230
02/20/2020
006
MW-25
Aqueous
02/18/20201200
02/20/2020
007
MW-25D
Aqueous
02/18/20201130
02/20/2020
008
DUP-1
Aqueous
02/18/2020
02/20/2020
009
EB-1
Aqueous
02/18/20201230
02/20/2020
010
TB-1
Aqueous
02/18/2020
02/20/2020
(10 samples)
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 3 of 46
PACE ANALYTICAL SERVICES, LLC
Detection Summary
Apex Companies, LLC
Lot Number: VB20090
Sample Sample ID
Matrix
Parameter
Method
Result
Q
Units
Page
003
MW-8
Aqueous
Methyl tertiary butyl ether
SM 6200B-
9.8
ug/L
7
004
MW-13
Aqueous
Benzene
SM 6200B-
4.8
ug/L
8
004
MW-13
Aqueous
Methyl tertiary butyl ether
SM 6200B-
11
ug/L
8
005
MW-24
Aqueous
Benzene
SM 6200B-
8.3
ug/L
9
005
MW-24
Aqueous
Ethylbenzene
SM 6200B-
16
ug/L
9
005
MW-24
Aqueous
Toluene
SM 6200B-
2.2
ug/L
9
005
MW-24
Aqueous
Xylenes (total)
SM 6200B-
7.9
ug/L
9
005
MW-24
Aqueous
Acenaphthene
625.1
7.1
J
ug/L
9
005
MW-24
Aqueous
Fluoranthene
625.1
6.2
J
ug/L
10
005
MW-24
Aqueous
1-Methylnaphthalene
625.1
5.2
J
ug/L
10
005
MW-24
Aqueous
Naphthalene
625.1
5.3
J
ug/L
10
005
MW-24
Aqueous
Pyrene
625.1
6.1
J
ug/L
10
005
MW-24
Aqueous
C11 - C22 Aromatics
MADEP-EPH-
290
ug/L
11
005
MW-24
Aqueous
C9 - C18 Aliphatics
MADEP-EPH-
230
ug/L
11
005
MW-24
Aqueous
C19 - C36 Aliphatics
MADEP-EPH-
180
ug/L
11
005
MW-24
Aqueous
C5 - C8 Aliphatics
MADEP-VPH-
1700
ug/L
11
005
MW-24
Aqueous
C9 - C12 Aliphatics
MADEP-VPH-
500
ug/L
11
005
MW-24
Aqueous
C9 - C10 Aromatics
MADEP-VPH-
490
ug/L
12
008
DUP-1
Aqueous
Methyl tertiary butyl ether
SM 6200B-
9.6
ug/L
21
(19 detections)
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Page 4 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-001
Description: MW-4 Matrix: Aqueous
Date Sampled:02/18/2020 1225
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 02/22/2020 0049 JTH 45799
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 6200B-
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
ND
0.50
0.40
ug/L
1
Run Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
95 70-130
1,2-Dichloroethane-d4
93 70-130
Toluene-d8
93 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 5 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-002
Description: MW-6 Matrix: Aqueous
Date Sampled:02/18/2020 1140
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 02/22/2020 0113 JTH 45799
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 6200B-
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
ND
0.50
0.40
ug/L
1
Run Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
94 70-130
1,2-Dichloroethane-d4
91 70-130
Toluene-d8
92 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 6 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-003
Description: MW-8 Matrix: Aqueous
Date Sampled:02/18/2020 1025
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 02/22/2020 0136 JTH 45799
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 6200B-
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 6200B-
9.8
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
ND
0.50
0.40
ug/L
1
Run Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
96 70-130
1,2-Dichloroethane-d4
93 70-130
Toluene-d8
93 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 7 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-004
Description: MW-13 Matrix: Aqueous
Date Sampled:02/18/2020 1125
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 620013- SM 620OB-2011 1 02/22/2020 0200 JTH 45799
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 6200B-
4.8
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620013-
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 6200B-
11
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620013-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620013-
ND
0.50
0.40
ug/L
1
Run Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
97 70-130
1,2-Dichloroethane-d4
90 70-130
Toluene-d8
93 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 8 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-005
Description: MW-24 Matrix: Aqueous
Date Sampled:02/18/2020 1230
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 SM 620013-
SM 620OB-2011 1 02/22/2020 0223 JTH
45799
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Benzene
71-43-2 SM 6200B-
8.3
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
16
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
2.2
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
7.9
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
98 70-130
1,2-Dichloroethane-d4
91 70-130
Toluene-d8
94 70-130
Semivolatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 625.1
625.1 5 02/28/2020 1436 SCD
02/25/2020 1807 46063
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Acenaphthene
83-32-9 625.1
7.1 J
8.0
4.0
ug/L
1
Acenaphthylene
208-96-8 625.1
ND
8.0
4.0
ug/L
1
Anthracene
120-12-7 625.1
ND
8.0
4.0
ug/L
1
Benzo(a)anthracene
56-55-3 625.1
ND
8.0
4.0
ug/L
1
Benzo(a)pyrene
50-32-8 625.1
ND
8.0
4.0
ug/L
1
Benzo(b)fluoranthene
205-99-2 625.1
ND
8.0
4.0
ug/L
1
Benzo(g,h,i)perylene
191-24-2 625.1
ND
8.0
4.0
ug/L
1
Benzo(k)fluoranthene
207-08-9 625.1
ND
8.0
4.0
ug/L
1
Benzyl alcohol
100-51-6 625.1
ND
16
10
ug/L
1
4-Bromophenyl phenyl ether
101-55-3 625.1
ND
8.0
4.0
ug/L
1
Butyl benzyl phthalate
85-68-7 625.1
ND
8.0
4.0
ug/L
1
bis (2-Chloro-1-methylethyl) ether
108-60-1 625.1
ND
8.0
4.0
ug/L
1
4-Chloro-3-methyl phenol
59-50-7 625.1
ND
8.0
4.0
ug/L
1
bis(2-Chloroethoxy)methane
111-91-1 625.1
ND
8.0
4.0
ug/L
1
bis(2-Chloroethyl)ether
111-44-4 625.1
ND
8.0
4.0
ug/L
1
2-Chloronaphthalene
91-58-7 625.1
ND
8.0
4.0
ug/L
1
2-Chlorophenol
95-57-8 625.1
ND
8.0
4.0
ug/L
1
4-Chlorophenyl phenyl ether
7005-72-3 625.1
ND
8.0
4.0
ug/L
1
Chrysene
218-01-9 625.1
ND
8.0
4.0
ug/L
1
Dibenzo(a,h)anthracene
53-70-3 625.1
ND
8.0
4.0
ug/L
1
Dibenzofuran
132-64-9 625.1
ND
8.0
5.0
ug/L
1
3,3'-Dichlorobenzidine
91-94-1 625.1
ND
40
4.0
ug/L
1
2,4-Dichlorophenol
120-83-2 625.1
ND
8.0
4.0
ug/L
1
Diethylphthalate
84-66-2 625.1
ND
8.0
4.0
ug/L
1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range DL =
Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result <
LOQ and > DL
H = Out of holding time W =
Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 9 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-005
Description: MW-24 Matrix: Aqueous
Date Sampled:02/18/2020 1230
Date Received:02/20/2020
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 625.1 625.1 5 02/28/2020 1436 SCD 02/25/2020 1807 46063
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Dimethyl phthalate
131-11-3
625.1
ND
8.0
4.0
ug/L
2,4-Dimethylphenol
105-67-9
625.1
ND
8.0
4.0
ug/L
Di-n-butyl phthalate
84-74-2
625.1
ND
8.0
4.1
ug/L
4,6-Dinitro-2-methylphenol
534-52-1
625.1
ND
40
4.0
ug/L
2,4-Dinitrophenol
51-28-5
625.1
ND
40
4.0
ug/L
Di-n-octylphthalate
117-84-0
625.1
ND
8.0
4.0
ug/L
1,2-Diphenylhydrazine(as azobenzene)
103-33-3
625.1
ND
8.0
4.0
ug/L
bis(2-Ethylhexyl)phthalate
117-81-7
625.1
ND
40
20
ug/L
Fluoranthene
206-44-0
625.1
6.2
J
8.0
4.0
ug/L
Fluorene
86-73-7
625.1
ND
8.0
4.0
ug/L
Hexachlorobenzene
118-74-1
625.1
ND
8.0
4.0
ug/L
Hexachlorobutadiene
87-68-3
625.1
ND
8.0
4.0
ug/L
Hexachlorocyclopentadiene
77-47-4
625.1
ND
40
20
ug/L
Hexachloroethane
67-72-1
625.1
ND
8.0
4.0
ug/L
Indeno(1,2,3-c,d)pyrene
193-39-5
625.1
ND
8.0
4.0
ug/L
Isophorone
78-59-1
625.1
ND
8.0
4.0
ug/L
1-Methylnaphthalene
90-12-0
625.1
5.2
J
8.0
2.0
ug/L
2-Methylnaphthalene
91-57-6
625.1
ND
8.0
2.0
ug/L
2-Methylphenol
95-48-7
625.1
ND
8.0
3.4
ug/L
3+4-Methylphenol
106-44-5
625.1
ND
8.0
7.5
ug/L
Naphthalene
91-20-3
625.1
5.3
J
8.0
4.0
ug/L
Nitrobenzene
98-95-3
625.1
ND
8.0
4.0
ug/L
2-Nitrophenol
88-75-5
625.1
ND
16
4.0
ug/L
4-Nitrophenol
100-02-7
625.1
ND
40
20
ug/L
N-Nitrosodi-n-propylamine
621-64-7
625.1
ND
8.0
4.0
ug/L
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
625.1
ND
8.0
4.0
ug/L
Pentachlorophenol
87-86-5
625.1
ND
40
20
ug/L
Phenanthrene
85-01-8
625.1
ND
8.0
4.0
ug/L
Phenol
108-95-2
625.1
ND
8.0
4.0
ug/L
Pyrene
129-00-0
625.1
6.1
J
8.0
4.0
ug/L
1,2,4-Trichlorobenzene
120-82-1
625.1
ND
8.0
4.0
ug/L
2,4,6-Trichlorophenol
88-06-2
625.1
ND
8.0
4.0
ug/L
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 10 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-005
Description: MW-24 Matrix: Aqueous
Date Sampled:02/18/2020 1230
Date Received:02/20/2020
Run 1 Acceptance
Surrogate
Q % Recovery Limits
2-Fluorobiphenyl
84 37-129
2-Fluorophenol
53 24-127
Nitrobenzene-d5
87 38-127
Phenol-d5
87 28-128
Terphenyl-d14
68 10-148
2,4,6-Tribromophenol
111 41-144
MADEP EPH (aromatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 03/03/2020 1530 DAL1 02/25/2020 1325 46030
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C11 - C22 Aromatics
MADEP-EPH- 290
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
o - Terphenyl (aromatic)
61 40-140
2-Fluorobiphenyl (fractionation 1)
70 40-140
2-Bromonaphthalene (fractionation
2) 68 40-140
MADEP EPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 03/03/2020 1229 DAL1 02/25/2020 1325 46029
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C9 - C18 Aliphatics
MADEP-EPH- 230
100
100 ug/L 1
C19 - C36 Aliphatics
MADEP-EPH- 180
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
1-Chloro-octadecane (aliphatic)
47 40-140
MADEP VPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 VPH
MADEP-VPH-18-2.1 1 02/27/20201223 JJG
46412
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C5 - C8 Aliphatics
MADEP-VPH- 1700
75
15 ug/L 1
C9 - C12 Aliphatics
MADEP-VPH- 500
75
15 ug/L 1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range
DL = Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 %
J = Estimated result <
LOQ and > DL
H = Out of holding time W
= Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 11 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-005
Description: MW-24 Matrix: Aqueous
Date Sampled:02/18/2020 1230
Date Received:02/20/2020
Run 1 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (FID) 73 70-130
MADEP VPH (aromatics)
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 VPH MADEP-VPH-18-2.1 1 02/27/20201223 JJG 46411
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
C9 - C10 Aromatics MADEP-VPH- 490 25 5.0 ug/L 1
Run 1 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (PID) 88 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 12 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-006
Description: MW-25 Matrix: Aqueous
Date Sampled:02/18/2020 1200
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 SM 6200B-
SM 620OB-2011 1 02/22/2020 0247 JTH
45799
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Benzene
71-43-2 SM 6200B-
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
97 70-130
1,2-Dichloroethane-d4
92 70-130
Toluene-d8
92 70-130
Semivolatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 625.1
625.1 1 02/28/2020 1500 SCD
02/25/2020 1807 46063
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Acenaphthene
83-32-9 625.1
ND
1.6
0.80
ug/L
1
Acenaphthylene
208-96-8 625.1
ND
1.6
0.80
ug/L
1
Anthracene
120-12-7 625.1
ND
1.6
0.80
ug/L
1
Benzo(a)anthracene
56-55-3 625.1
ND
1.6
0.80
ug/L
1
Benzo(a)pyrene
50-32-8 625.1
ND
1.6
0.80
ug/L
1
Benzo(b)fluoranthene
205-99-2 625.1
ND
1.6
0.80
ug/L
1
Benzo(g,h,i)perylene
191-24-2 625.1
ND
1.6
0.80
ug/L
1
Benzo(k)fluoranthene
207-08-9 625.1
ND
1.6
0.80
ug/L
1
Benzyl alcohol
100-51-6 625.1
ND
3.2
2.0
ug/L
1
4-Bromophenyl phenyl ether
101-55-3 625.1
ND
1.6
0.80
ug/L
1
Butyl benzyl phthalate
85-68-7 625.1
ND
1.6
0.80
ug/L
1
bis (2-Chloro-1-methylethyl) ether
108-60-1 625.1
ND
1.6
0.80
ug/L
1
4-Chloro-3-methyl phenol
59-50-7 625.1
ND
1.6
0.80
ug/L
1
bis(2-Chloroethoxy)methane
111-91-1 625.1
ND
1.6
0.80
ug/L
1
bis(2-Chloroethyl)ether
111-44-4 625.1
ND
1.6
0.80
ug/L
1
2-Chloronaphthalene
91-58-7 625.1
ND
1.6
0.80
ug/L
1
2-Chlorophenol
95-57-8 625.1
ND
1.6
0.80
ug/L
1
4-Chlorophenyl phenyl ether
7005-72-3 625.1
ND
1.6
0.80
ug/L
1
Chrysene
218-01-9 625.1
ND
1.6
0.80
ug/L
1
Dibenzo(a,h)anthracene
53-70-3 625.1
ND
1.6
0.80
ug/L
1
Dibenzofuran
132-64-9 625.1
ND
1.6
1.0
ug/L
1
3,3'-Dichlorobenzidine
91-94-1 625.1
ND
8.0
0.80
ug/L
1
2,4-Dichlorophenol
120-83-2 625.1
ND
1.6
0.80
ug/L
1
Diethylphthalate
84-66-2 625.1
ND
1.6
0.80
ug/L
1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range DL =
Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result <
LOQ and > DL
H = Out of holding time W =
Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 13 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-006
Description: MW-25 Matrix: Aqueous
Date Sampled:02/18/2020 1200
Date Received:02/20/2020
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 625.1 625.1 1 02/28/2020 1500 SCD 02/25/2020 1807 46063
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Dimethyl phthalate
131-11-3
625.1
ND
1.6
0.80
ug/L
2,4-Dimethylphenol
105-67-9
625.1
ND
1.6
0.80
ug/L
Di-n-butyl phthalate
84-74-2
625.1
ND
1.6
0.81
ug/L
4,6-Dinitro-2-methylphenol
534-52-1
625.1
ND
8.0
0.80
ug/L
2,4-Dinitrophenol
51-28-5
625.1
ND
8.0
0.80
ug/L
Di-n-octylphthalate
117-84-0
625.1
ND
1.6
0.80
ug/L
1,2-Diphenylhydrazine(as azobenzene)
103-33-3
625.1
ND
1.6
0.80
ug/L
bis(2-Ethylhexyl)phthalate
117-81-7
625.1
ND
8.0
4.0
ug/L
Fluoranthene
206-44-0
625.1
ND
1.6
0.80
ug/L
Fluorene
86-73-7
625.1
ND
1.6
0.80
ug/L
Hexachlorobenzene
118-74-1
625.1
ND
1.6
0.80
ug/L
Hexachlorobutadiene
87-68-3
625.1
ND
1.6
0.80
ug/L
Hexachlorocyclopentadiene
77-47-4
625.1
ND
8.0
4.0
ug/L
Hexachloroethane
67-72-1
625.1
ND
1.6
0.80
ug/L
Indeno(1,2,3-c,d)pyrene
193-39-5
625.1
ND
1.6
0.80
ug/L
Isophorone
78-59-1
625.1
ND
1.6
0.80
ug/L
1-Methylnaphthalene
90-12-0
625.1
ND
1.6
0.40
ug/L
2-Methylnaphthalene
91-57-6
625.1
ND
1.6
0.40
ug/L
2-Methylphenol
95-48-7
625.1
ND
1.6
0.67
ug/L
3+4-Methylphenol
106-44-5
625.1
ND
1.6
1.5
ug/L
Naphthalene
91-20-3
625.1
ND
1.6
0.80
ug/L
Nitrobenzene
98-95-3
625.1
ND
1.6
0.80
ug/L
2-Nitrophenol
88-75-5
625.1
ND
3.2
0.80
ug/L
4-Nitrophenol
100-02-7
625.1
ND
8.0
4.0
ug/L
N-Nitrosodi-n-propylamine
621-64-7
625.1
ND
1.6
0.80
ug/L
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
625.1
ND
1.6
0.80
ug/L
Pentachlorophenol
87-86-5
625.1
ND
8.0
4.0
ug/L
Phenanthrene
85-01-8
625.1
ND
1.6
0.80
ug/L
Phenol
108-95-2
625.1
ND
1.6
0.80
ug/L
Pyrene
129-00-0
625.1
ND
1.6
0.80
ug/L
1,2,4-Trichlorobenzene
120-82-1
625.1
ND
1.6
0.80
ug/L
2,4,6-Trichlorophenol
88-06-2
625.1
ND
1.6
0.80
ug/L
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 14 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-006
Description: MW-25 Matrix: Aqueous
Date Sampled:02/18/2020 1200
Date Received:02/20/2020
Run 1 Acceptance
Surrogate
Q % Recovery Limits
2-Fluorobiphenyl
91 37-129
2-Fluorophenol
91 24-127
Nitrobenzene-d5
88 38-127
Phenol-d5
108 28-128
Terphenyl-d14
73 10-148
2,4,6-Tribromophenol
92 41-144
MADEP EPH (aromatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 03/03/2020 1600 DAL1 02/25/2020 1325 46030
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C11 - C22 Aromatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
o - Terphenyl (aromatic)
60 40-140
2-Fluorobiphenyl (fractionation 1)
72 40-140
2-Bromonaphthalene (fractionation
2) 60 40-140
MADEP EPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 03/03/2020 1259 DAL1 02/25/2020 1325 46029
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C9 - C18 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
C19 - C36 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
1-Chloro-octadecane (aliphatic)
45 40-140
MADEP VPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 VPH
MADEP-VPH-18-2.1 1 02/27/20201251 JJG
46412
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C5 - C8 Aliphatics
MADEP-VPH- ND
75
15 ug/L 1
C9 - C12 Aliphatics
MADEP-VPH- ND
75
15 ug/L 1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range
DL = Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 %
J = Estimated result <
LOQ and > DL
H = Out of holding time W
= Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 15 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-006
Description: MW-25 Matrix: Aqueous
Date Sampled:02/18/2020 1200
Date Received:02/20/2020
Run 1 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (FID) 102 70-130
MADEP VPH (aromatics)
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 VPH MADEP-VPH-18-2.1 1 02/27/20201251 JJG 46411
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
C9 - C10 Aromatics MADEP-VPH- ND 25 5.0 ug/L 1
Run 1 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (PID) 106 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 16 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-007
Description: MW-25D Matrix: Aqueous
Date Sampled:02/18/2020 1130
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 SM 6200B-
SM 620OB-2011 1 02/22/2020 0311 JTH
45799
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Benzene
71-43-2 SM 6200B-
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
95 70-130
1,2-Dichloroethane-d4
92 70-130
Toluene-d8
92 70-130
Semivolatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 625.1
625.1 1 02/28/2020 1523 SCD
02/25/2020 1807 46063
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Acenaphthene
83-32-9 625.1
ND
1.6
0.80
ug/L
1
Acenaphthylene
208-96-8 625.1
ND
1.6
0.80
ug/L
1
Anthracene
120-12-7 625.1
ND
1.6
0.80
ug/L
1
Benzo(a)anthracene
56-55-3 625.1
ND
1.6
0.80
ug/L
1
Benzo(a)pyrene
50-32-8 625.1
ND
1.6
0.80
ug/L
1
Benzo(b)fluoranthene
205-99-2 625.1
ND
1.6
0.80
ug/L
1
Benzo(g,h,i)perylene
191-24-2 625.1
ND
1.6
0.80
ug/L
1
Benzo(k)fluoranthene
207-08-9 625.1
ND
1.6
0.80
ug/L
1
Benzyl alcohol
100-51-6 625.1
ND
3.2
2.0
ug/L
1
4-Bromophenyl phenyl ether
101-55-3 625.1
ND
1.6
0.80
ug/L
1
Butyl benzyl phthalate
85-68-7 625.1
ND
1.6
0.80
ug/L
1
bis (2-Chloro-1-methylethyl) ether
108-60-1 625.1
ND
1.6
0.80
ug/L
1
4-Chloro-3-methyl phenol
59-50-7 625.1
ND
1.6
0.80
ug/L
1
bis(2-Chloroethoxy)methane
111-91-1 625.1
ND
1.6
0.80
ug/L
1
bis(2-Chloroethyl)ether
111-44-4 625.1
ND
1.6
0.80
ug/L
1
2-Chloronaphthalene
91-58-7 625.1
ND
1.6
0.80
ug/L
1
2-Chlorophenol
95-57-8 625.1
ND
1.6
0.80
ug/L
1
4-Chlorophenyl phenyl ether
7005-72-3 625.1
ND
1.6
0.80
ug/L
1
Chrysene
218-01-9 625.1
ND
1.6
0.80
ug/L
1
Dibenzo(a,h)anthracene
53-70-3 625.1
ND
1.6
0.80
ug/L
1
Dibenzofuran
132-64-9 625.1
ND
1.6
1.0
ug/L
1
3,3'-Dichlorobenzidine
91-94-1 625.1
ND
8.0
0.80
ug/L
1
2,4-Dichlorophenol
120-83-2 625.1
ND
1.6
0.80
ug/L
1
Diethylphthalate
84-66-2 625.1
ND
1.6
0.80
ug/L
1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range DL =
Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result <
LOQ and > DL
H = Out of holding time W =
Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 17 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-007
Description: MW-25D Matrix: Aqueous
Date Sampled:02/18/2020 1130
Date Received:02/20/2020
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 625.1 625.1 1 02/28/2020 1523 SCD 02/25/2020 1807 46063
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Dimethyl phthalate
131-11-3
625.1
ND
1.6
0.80
ug/L
2,4-Dimethylphenol
105-67-9
625.1
ND
1.6
0.80
ug/L
Di-n-butyl phthalate
84-74-2
625.1
ND
1.6
0.81
ug/L
4,6-Dinitro-2-methylphenol
534-52-1
625.1
ND
8.0
0.80
ug/L
2,4-Dinitrophenol
51-28-5
625.1
ND
8.0
0.80
ug/L
Di-n-octylphthalate
117-84-0
625.1
ND
1.6
0.80
ug/L
1,2-Diphenylhydrazine(as azobenzene)
103-33-3
625.1
ND
1.6
0.80
ug/L
bis(2-Ethylhexyl)phthalate
117-81-7
625.1
ND
8.0
4.0
ug/L
Fluoranthene
206-44-0
625.1
ND
1.6
0.80
ug/L
Fluorene
86-73-7
625.1
ND
1.6
0.80
ug/L
Hexachlorobenzene
118-74-1
625.1
ND
1.6
0.80
ug/L
Hexachlorobutadiene
87-68-3
625.1
ND
1.6
0.80
ug/L
Hexachlorocyclopentadiene
77-47-4
625.1
ND
8.0
4.0
ug/L
Hexachloroethane
67-72-1
625.1
ND
1.6
0.80
ug/L
Indeno(1,2,3-c,d)pyrene
193-39-5
625.1
ND
1.6
0.80
ug/L
Isophorone
78-59-1
625.1
ND
1.6
0.80
ug/L
1-Methylnaphthalene
90-12-0
625.1
ND
1.6
0.40
ug/L
2-Methylnaphthalene
91-57-6
625.1
ND
1.6
0.40
ug/L
2-Methylphenol
95-48-7
625.1
ND
1.6
0.67
ug/L
3+4-Methylphenol
106-44-5
625.1
ND
1.6
1.5
ug/L
Naphthalene
91-20-3
625.1
ND
1.6
0.80
ug/L
Nitrobenzene
98-95-3
625.1
ND
1.6
0.80
ug/L
2-Nitrophenol
88-75-5
625.1
ND
3.2
0.80
ug/L
4-Nitrophenol
100-02-7
625.1
ND
8.0
4.0
ug/L
N-Nitrosodi-n-propylamine
621-64-7
625.1
ND
1.6
0.80
ug/L
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
625.1
ND
1.6
0.80
ug/L
Pentachlorophenol
87-86-5
625.1
ND
8.0
4.0
ug/L
Phenanthrene
85-01-8
625.1
ND
1.6
0.80
ug/L
Phenol
108-95-2
625.1
ND
1.6
0.80
ug/L
Pyrene
129-00-0
625.1
ND
1.6
0.80
ug/L
1,2,4-Trichlorobenzene
120-82-1
625.1
ND
1.6
0.80
ug/L
2,4,6-Trichlorophenol
88-06-2
625.1
ND
1.6
0.80
ug/L
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 18 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-007
Description: MW-25D Matrix: Aqueous
Date Sampled:02/18/2020 1130
Date Received:02/20/2020
Run 1 Acceptance
Surrogate
Q % Recovery Limits
2-Fluorobiphenyl
92 37-129
2-Fluorophenol
71 24-127
Nitrobenzene-d5
87 38-127
Phenol-d5
98 28-128
Terphenyl-d14
111 10-148
2,4,6-Tribromophenol
88 41-144
MADEP EPH (aromatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 03/03/2020 1630 DAL1 02/25/2020 1325 46030
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C11 - C22 Aromatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
o - Terphenyl (aromatic)
64 40-140
2-Fluorobiphenyl (fractionation 1)
61 40-140
2-Bromonaphthalene (fractionation
2) 49 40-140
MADEP EPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 03/03/2020 1329 DAL1 02/25/2020 1325 46029
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C9 - C18 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
C19 - C36 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
1-Chloro-octadecane (aliphatic)
84 40-140
MADEP VPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 VPH
MADEP-VPH-18-2.1 1 02/27/20201320 JJG
46412
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C5 - C8 Aliphatics
MADEP-VPH- ND
75
15 ug/L 1
C9 - C12 Aliphatics
MADEP-VPH- ND
75
15 ug/L 1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range
DL = Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 %
J = Estimated result <
LOQ and > DL
H = Out of holding time W
= Reported on wet weight basis
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Page 19 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-007
Description: MW-25D Matrix: Aqueous
Date Sampled:02/18/2020 1130
Date Received:02/20/2020
Run 1 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (FID) 107 70-130
MADEP VPH (aromatics)
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 VPH MADEP-VPH-18-2.1 1 02/27/20201320 JJG 46411
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
C9 - C10 Aromatics MADEP-VPH- ND 25 5.0 ug/L 1
Run 1 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (PID) 109 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 20 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-008
Description: DUP-1 Matrix: Aqueous
Date Sampled:02/18/2020
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 02/22/2020 0334 JTH 45799
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 6200B-
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 6200B-
9.6
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
ND
0.50
0.40
ug/L
1
Run Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
96 70-130
1,2-Dichloroethane-d4
93 70-130
Toluene-d8
93 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 21 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-009
Description: EB-1 Matrix: Aqueous
Date Sampled:02/18/2020 1230
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 02/22/2020 0002 JTH 45799
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 6200B-
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
ND
0.50
0.40
ug/L
1
Run Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
95 70-130
1,2-Dichloroethane-d4
93 70-130
Toluene-d8
92 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 22 of 46
Client:Apex Companies, LLC Laboratory ID: VB20090-010
Description: TB-1 Matrix: Aqueous
Date Sampled:02/18/2020
Date Received:02/20/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 02/22/2020 0025 JTH 45799
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 6200B-
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 6200B-
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 6200B-
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 6200B-
ND
0.50
0.40
ug/L
1
Run Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
96 70-130
1,2-Dichloroethane-d4
92 70-130
Toluene-d8
93 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 23 of 46
QC Summary
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Page 24 of 46
Volatile Organic Compounds by GC/MS - MB
Sample ID: VQ45799-001 Matrix: Aqueous
Batch:45799 Prep Method: SM 620OB-2011
Analytical Method: SM 620OB-2011
Parameter
Result
Q Dil
LOQ
DL
Units
Analysis Date
Benzene
ND
1
0.50
0.40
ug/L
02/21/2020 2306
Ethylbenzene
ND
1
0.50
0.40
ug/L
02/21/2020 2306
Methyl tertiary butyl ether (MTBE)
ND
1
0.50
0.40
ug/L
02/21/2020 2306
Toluene
ND
1
0.50
0.40
ug/L
02/21/2020 2306
Xylenes (total)
ND
1
0.50
0.40
ug/L
02/21/2020 2306
Acceptance
Surrogate
Q % Rec
Limit
Bromofluorobenzene 96 70-130
1,2-Dichloroethane-d4 91 70-130
Toluene-d8 93 70-130
LOQ = Limit of Quantitation P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL + = RPD is out of criteria
LOD = Limit of Detection ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 25 of 46
Volatile Organic Compounds by GC/MS - LCS
Sample ID: VQ45799-002
Matrix: Aqueous
Batch:45799
Prep Method: SM 620OB-2011
Analytical Method: SM 620OB-2011
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L) Q
Dil % Rec
Limit
Analysis Date
Benzene
50
50
1 99
70-130
02/21/2020 2139
Ethylbenzene
50
50
1 100
70-130
02/21/2020 2139
Methyl tertiary butyl ether (MTBE)
50
49
1 98
70-130
02/21/2020 2139
Toluene
50
50
1 100
70-130
02/21/2020 2139
Xylenes (total)
100
100
1 101
70-130
02/21/2020 2139
Surrogate
Q % Rec
Acceptance
Limit
Bromofluorobenzene 95 70-130
1,2-Dichloroethane-d4 98 70-130
Toluene-d8 100 70-130
LOQ = Limit of Quantitation P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL + = RPD is out of criteria
LOD = Limit of Detection ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 26 of 46
Volatile Organic Compounds by GC/MS - LCSD
Sample ID: VQ45799-003
Matrix: Aqueous
Batch:45799
Prep
Method: SM 620OB-2011
Analytical Method: SM 620OB-2011
Spike
Amount
Result
% Rec
% RPD
Parameter
(ug/L)
(ug/L) Q
Dil
% Rec % RPD
Limit
Limit
Analysis Date
Benzene
50
50
1
100 1.1
70-130
20
02/21/2020 2203
Ethylbenzene
50
52
1
103 3.3
70-130
20
02/21/2020 2203
Methyl tertiary butyl ether (MTBE)
50
48
1
96 2.7
70-130
20
02/21/2020 2203
Toluene
50
52
1
104 4.1
70-130
20
02/21/2020 2203
Xylenes (total)
100
110
1
108 6.8
70-130
20
02/21/2020 2203
Acceptance
Surrogate Q % Rec Limit
Bromofluorobenzene 99 70-130
1,2-Dichloroethane-d4 92 70-130
Toluene-d8 93 70-130
LOQ = Limit of Quantitation P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL + = RPD is out of criteria
LOD = Limit of Detection ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 27 of 46
Semivolatile Organic Compounds by GC/MS - MB
Sample ID: VQ46063-001 Matrix: Aqueous
Batch:46063 Prep Method: 625.1
Analytical Method: 625.1 Prep Date: 02/25/2020 1807
Parameter
Result Q
Dil
LOQ
DL
Units
Analysis Date
Acenaphthene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Acenaphthylene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Anthracene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Benzo(a)anthracene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Benzo(a)pyrene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Benzo(b)fluoranthene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Benzo(g,h,i)perylene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Benzo(k)fluoranthene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Benzyl alcohol
ND
1
3.2
2.0
ug/L
02/28/2020 1349
4-Bromophenyl phenyl ether
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Butyl benzyl phthalate
ND
1
1.6
0.80
ug/L
02/28/2020 1349
bis (2-Chloro-1-methylethyl) ether
ND
1
1.6
0.80
ug/L
02/28/2020 1349
4-Chloro-3-methyl phenol
ND
1
1.6
0.80
ug/L
02/28/2020 1349
bis(2-Chloroethoxy)methane
ND
1
1.6
0.80
ug/L
02/28/2020 1349
bis(2-Chloroethyl)ether
ND
1
1.6
0.80
ug/L
02/28/2020 1349
2-Chloronaphthalene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
2-Chlorophenol
ND
1
1.6
0.80
ug/L
02/28/2020 1349
4-Chlorophenyl phenyl ether
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Chrysene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Dibenzo(a,h)anth race ne
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Dibenzofuran
ND
1
1.6
1.0
ug/L
02/28/2020 1349
3,3'-Dichlorobenzidine
ND
1
8.0
0.80
ug/L
02/28/2020 1349
2,4-Dichlorophenol
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Diethylphthalate
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Dimethyl phthalate
ND
1
1.6
0.80
ug/L
02/28/2020 1349
2,4-Dimethylphenol
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Di-n-butyl phthalate
ND
1
1.6
0.81
ug/L
02/28/2020 1349
4,6-Dinitro-2-methyl phenol
ND
1
8.0
0.80
ug/L
02/28/2020 1349
2,4-Dinitrophenol
ND
1
8.0
0.80
ug/L
02/28/2020 1349
Di-n-octylphthalate
ND
1
1.6
0.80
ug/L
02/28/2020 1349
1,2-Diphenylhydrazine(as azobenzene)
ND
1
1.6
0.80
ug/L
02/28/2020 1349
bis(2-Ethylhexyl)phthalate
ND
1
8.0
4.0
ug/L
02/28/2020 1349
Fluoranthene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Fluorene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Hexachlorobenzene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Hexachlorobutadiene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Hexachlorocyclopentadiene
ND
1
8.0
4.0
ug/L
02/28/2020 1349
Hexachloroethane
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Indeno(1,2,3-c,d)pyrene
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Isophorone
ND
1
1.6
0.80
ug/L
02/28/2020 1349
1-Methyl naphthalene
ND
1
1.6
0.40
ug/L
02/28/2020 1349
2-Methyl naphthalene
ND
1
1.6
0.40
ug/L
02/28/2020 1349
2-Methylphenol
ND
1
1.6
0.67
ug/L
02/28/2020 1349
3+4-Methylphenol
ND
1
1.6
1.5
ug/L
02/28/2020 1349
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 28 of 46
Semivolatile Organic Compounds by GC/MS - MB
Sample ID: VQ46063-001 Matrix: Aqueous
Batch:46063 Prep Method: 625.1
Analytical Method: 625.1 Prep Date: 02/25/2020 1807
Parameter
Result Q
Dil
LOQ
DL
Units
Analysis Date
Naphthalene
ND
1
1.6
0.80
ug/L
02/28/20201349
Nitrobenzene
ND
1
1.6
0.80
ug/L
02/28/20201349
2-Nitrophenol
ND
1
3.2
0.80
ug/L
02/28/20201349
4-Nitrophenol
ND
1
8.0
4.0
ug/L
02/28/20201349
N-Nitrosodi-n-propylamine
ND
1
1.6
0.80
ug/L
02/28/20201349
N-Nitrosodiphenylamine (Diphenylamine)
ND
1
1.6
0.80
ug/L
02/28/2020 1349
Pentachlorophenol
ND
1
8.0
4.0
ug/L
02/28/20201349
Phenanthrene
ND
1
1.6
0.80
ug/L
02/28/20201349
Phenol
ND
1
1.6
0.80
ug/L
02/28/20201349
Pyrene
ND
1
1.6
0.80
ug/L
02/28/20201349
1,2,4-Trichlorobenzene
ND
1
1.6
0.80
ug/L
02/28/20201349
2,4,6-Trichlorophenol
ND
1
1.6
0.80
ug/L
02/28/20201349
Surrogate Q /o Rec Acceptance
0
Limit
2-Fluorobiphenyl
88
37-129
2-Fluorophenol
60
24-127
Nitrobenzene-d5
88
38-127
Phenol-d5
70
28-128
Terphenyl-d 14
114
10-148
2,4,6-Tribromophenol
69
41-144
LOQ = Limit of Quantitation P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL + = RPD is out of criteria
LOD = Limit of Detection ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 29 of 46
Semivolatile Organic Compounds by GC/MS - LCS
Sample ID: VQ46063-002
Matrix: Aqueous
Batch:46063
Prep Method:
625.1
Analytical Method: 625.1
Prep Date: 02/25/2020 1807
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L)
Q Dil
% Rec
Limit
Analysis Date
Acenaphthene
20
18
1
91
47-145
02/28/2020 1412
Acenaphthylene
20
20
1
99
33-145
02/28/2020 1412
Anthracene
20
18
1
90
27-133
02/28/2020 1412
Benzo(a)anthracene
20
18
1
88
33-143
02/28/2020 1412
Benzo(a)pyrene
20
19
1
94
17-163
02/28/2020 1412
Benzo(b)fluoranthene
20
18
1
92
24-159
02/28/2020 1412
Benzo(g,h,i)perylene
20
20
1
101
1-219
02/28/2020 1412
Benzo(k)fluoranthene
20
21
1
105
11-162
02/28/2020 1412
Benzyl alcohol
20
21
1
106
30-130
02/28/2020 1412
4-Bromophenyl phenyl ether
20
16
1
80
53-127
02/28/2020 1412
Butyl benzyl phthalate
20
17
1
85
1-152
02/28/2020 1412
bis (2-Chloro-1-methylethyl) ether
20
17
1
86
36-166
02/28/2020 1412
4-Chloro-3-methyl phenol
20
18
1
89
22-147
02/28/2020 1412
bis(2-Chloroethoxy)methane
20
16
1
79
33-184
02/28/2020 1412
bis(2-Chloroethyl)ether
20
20
1
99
12-158
02/28/2020 1412
2-Chloronaphthalene
20
17
1
87
60-120
02/28/2020 1412
2-Chlorophenol
20
17
1
83
23-134
02/28/2020 1412
4-Chlorophenyl phenyl ether
20
17
1
85
25-158
02/28/2020 1412
Chrysene
20
19
1
93
17-168
02/28/2020 1412
Dibenzo(a,h)anth race ne
20
20
1
101
1-227
02/28/2020 1412
Dibenzofuran
20
17
1
86
48-118
02/28/2020 1412
3,3'-Dichlorobenzidine
20
13
1
65
1-262
02/28/2020 1412
2,4-Dichlorophenol
20
16
1
82
39-135
02/28/2020 1412
Diethylphthalate
20
19
1
96
1-120
02/28/2020 1412
Dimethyl phthalate
20
19
1
96
1-120
02/28/2020 1412
2,4-Dimethylphenol
20
16
1
78
32-120
02/28/2020 1412
Di-n-butyl phthalate
20
20
1
102
1-120
02/28/2020 1412
4,6-Dinitro-2-methyl phenol
20
17
1
86
1-181
02/28/2020 1412
2,4-Dinitrophenol
40
31
1
77
1-191
02/28/2020 1412
Di-n-octylphthalate
20
17
1
85
4-146
02/28/2020 1412
1,2-Diphenylhydrazine(as azobenzene)
20
18
1
90
1-150
02/28/2020 1412
bis(2-Ethylhexyl)phthalate
20
17
1
84
8-158
02/28/2020 1412
Fluoranthene
20
19
1
94
26-137
02/28/2020 1412
Fluorene
20
19
1
93
59-121
02/28/2020 1412
Hexachlorobenzene
20
17
1
86
1-152
02/28/2020 1412
Hexachlorobutadiene
20
15
1
73
24-120
02/28/2020 1412
Hexachlorocyclopentadiene
100
80
1
80
1-150
02/28/2020 1412
Hexachloroethane
20
15
1
76
40-120
02/28/2020 1412
Indeno(1,2,3-c,d)pyrene
20
20
1
98
1-171
02/28/2020 1412
Isophorone
20
17
1
87
21-196
02/28/2020 1412
1-Methyl naphthalene
20
17
1
86
42-126
02/28/2020 1412
2-Methyl naphthalene
20
16
1
82
40-132
02/28/2020 1412
2-Methylphenol
20
20
1
99
30-130
02/28/2020 1412
3+4-Methylphenol
20
21
1
105
30-130
02/28/2020 1412
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 30 of 46
Semivolatile Organic Compounds by GC/MS - LCS
Sample ID: VQ46063-002
Matrix: Aqueous
Batch:46063
Prep Method: 625.1
Analytical Method: 625.1
Prep Date: 02/25/2020 1807
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L) Q
Dil % Rec
Limit
Analysis Date
Naphthalene
20
15
1 75
21-133
02/28/20201412
Nitrobenzene
20
17
1 85
35-180
02/28/20201412
2-Nitrophenol
20
16
1 82
29-182
02/28/20201412
4-Nitrophenol
40
35
1 88
1-132
02/28/20201412
N-Nitrosodi-n-propylamine
20
23
1 116
1-230
02/28/20201412
N-Nitrosodiphenylamine (Diphenylamine) 20
18
1 88
1-150
02/28/2020 1412
Pentachlorophenol
40
32
1 79
14-176
02/28/20201412
Phenanthrene
20
18
1 89
54-120
02/28/20201412
Phenol
20
17
1 85
5-120
02/28/20201412
Pyrene
20
20
1 99
52-120
02/28/20201412
1,2,4-Trichlorobenzene
20
14
1 72
44-142
02/28/20201412
2,4,6-Trichlorophenol
20
19
1 97
37-144
02/28/20201412
Acceptance
Surrogate
0
Q /o Rec
Limit
2-Fluorobiphenyl
95
37-129
2-Fluorophenol
53
24-127
Nitrobenzene-d5
87
38-127
Phenol-d5
82
28-128
Terphenyl-d 14
110
10-148
2,4,6-Tribromophenol
92
41-144
LOQ = Limit of Quantitation P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL + = RPD is out of criteria
LOD = Limit of Detection ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 31 of 46
MADEP EPH (aliphatics) - MB
Sample ID: VQ46029-001 Matrix: Aqueous
Batch:46029 Prep Method: MADEP-EPH-04
Analytical Method: MADEP-EPH-04 Prep Date: 02/25/2020 1325
Parameter Result Q Dil LOQ DL Units Analysis Date
C9 - C18 Aliphatics ND 1 100 100 ug/L 03/03/2020 1059
C19 - C36 Aliphatics ND 1 100 100 ug/L 03/03/2020 1059
Surrogate
Acceptance
Q % Rec Limit
1-Chloro-octadecane (aliphatic) 83 40-140
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 32 of 46
MADEP EPH (aliphatics) - LCS
Sample ID: VQ46029-002
Matrix: Aqueous
Batch:46029
Prep Method: MADEP-EPH-04
Analytical Method: MADEP-EPH-04
Prep Date: 02/25/2020 1325
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L)
Q Dil % Rec
Limit Analysis Date
C9 - C18 Aliphatics
300
130
1 44
40-140 03/03/2020 1129
C19 - C36 Aliphatics
400
370
1 92
40-140 03/03/2020 1129
Surrogate
Acceptance
Q % Rec Limit
1-Chloro-octadecane (aliphatic) 83 40-140
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 33 of 46
MADEP EPH (aliphatics) - LCSD
Sample ID: VQ46029-003
Matrix: Aqueous
Batch:46029
Prep Method: MADEP-EPH-04
Analytical Method: MADEP-EPH-04
Prep Date: 02/25/2020 1325
Spike
Amount
Result
% Rec
% RPD
Parameter
(ug/L)
(ug/L) Q
Dil % Rec % RPD Limit
Limit Analysis Date
C9 - C18 Aliphatics
300
180 +
1 60 30 40-140
25 03/03/2020 1159
C19 - C36 Aliphatics
400
390
1 98 6.3 40-140
25 03/03/2020 1159
Surrogate
Acceptance
Q % Rec Limit
1-Chloro-octadecane (aliphatic) 89 40-140
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 34 of 46
MADEP EPH (aromatics) - MB
Sample ID: VQ46030-001 Matrix: Aqueous
Batch:46030 Prep Method: MADEP-EPH-04
Analytical Method: MADEP-EPH-04 Prep Date: 02/25/2020 1325
Parameter Result Q Dil LOQ DL Units Analysis Date
C11 - C22 Aromatics ND 1 100 100 ug/L 03/03/2020 1359
Acceptance
Surrogate Q % Rec Limit
o - Terphenyl (aromatic) 63 40-140
2-Fluorobiphenyl (fractionation 1) 71 40-140
2-Bromonaphthalene (fractionation 2) 73 40-140
LOQ = Limit of Quantitation P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL + = RPD is out of criteria
LOD = Limit of Detection ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 35 of 46
MADEP EPH (aromatics) - LCS
Sample ID: VQ46030-002
Matrix: Aqueous
Batch:46030
Prep Method: MADEP-EPH-04
Analytical Method: MADEP-EPH-04
Prep Date: 02/25/2020 1325
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L) Q
Dil % Rec Limit Analysis Date
C11 - C22 Aromatics
850
550
1 65 40-140 03/03/2020 1429
Surrogate
Q % Rec
Acceptance
Limit
o - Terphenyl (aromatic) 69 40-140
2-Fluorobiphenyl (fractionation 1) 74 40-140
2-Bromonaphthalene (fractionation 2) 73 40-140
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 36 of 46
MADEP EPH (aromatics) - LCSD
Sample ID: VQ46030-003 Matrix: Aqueous
Batch:46030 Prep Method: MADEP-EPH-04
Analytical Method: MADEP-EPH-04 Prep Date: 02/25/2020 1325
Spike
Amount Result % Rec % RPD
Parameter (ug/L) (ug/L) Q Dil % Rec % RPD Limit Limit Analysis Date
C11 - C22 Aromatics 850 600 1 70 7.4 40-140 25 03/03/2020 1500
Acceptance
Surrogate Q % Rec Limit
o - Terphenyl (aromatic) 72 40-140
2-Fluorobiphenyl (fractionation 1) 76 40-140
2-Bromonaphthalene (fractionation 2) 68 40-140
LOQ = Limit of Quantitation P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL + = RPD is out of criteria
LOD = Limit of Detection ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 37 of 46
MADEP VPH (aromatics) - MB
Sample ID: VQ46411-001 Matrix: Aqueous
Batch:46411 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Parameter Result Q Dil LOQ DL Units Analysis Date
C9 - C10 Aromatics ND 1 25 5.0 ug/L 02/27/2020 1028
Surrogate
2,5-Dibromotoluene (PID)
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
Acceptance
Q % Rec Limit
103 70-130
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 38 of 46
MADEP VPH (aromatics) - LCS
Sample ID: VQ46411-002 Matrix: Aqueous
Batch:46411 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Spike
Amount Result % Rec
Parameter (ug/L) (ug/L) Q Dil % Rec Limit Analysis Date
C9 - C10 Aromatics 25 26 1 105 70-130 02/27/2020 0931
Surrogate
2,5-Dibromotoluene (PID)
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
Acceptance
Q % Rec Limit
108 70-130
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 39 of 46
MADEP VPH (aromatics) - LCSD
Sample ID: VQ46411-003 Matrix: Aqueous
Batch:46411 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Spike
Amount Result % Rec % RPD
Parameter (ug/L) (ug/L) Q Dil % Rec % RPD Limit Limit Analysis Date
C9 - C10 Aromatics 25 26 1 103 2.3 70-130 25 02/27/2020 1000
Surrogate
2,5-Dibromotoluene (PID)
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
Acceptance
Q % Rec Limit
105 70-130
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 40 of 46
MADEP VPH (aliphatics) - MB
Sample ID: VQ46412-001 Matrix: Aqueous
Batch:46412 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Parameter Result Q Dil LOQ DL Units Analysis Date
C5 - C8 Aliphatics ND 1 75 15 ug/L 02/27/2020 1028
C9 - C12 Aliphatics ND 1 75 15 ug/L 02/27/2020 1028
Surrogate
2,5-Dibromotoluene (FID)
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
Acceptance
Q % Rec Limit
103 70-130
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 41 of 46
MADEP VPH (aliphatics) - LCS
Sample ID: VQ46412-002 Matrix: Aqueous
Batch:46412 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L) Q Dil
% Rec Limit Analysis Date
C5 - C8 Aliphatics
150
140 1
95 70-130 02/27/2020 0931
C9 - C12 Aliphatics
180
170 1
98 70-130 02/27/2020 0931
Surrogate
2,5-Dibromotoluene (FID)
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
Acceptance
Q % Rec Limit
103 70-130
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 42 of 46
MADEP VPH (aliphatics) - LCSD
Sample ID: VQ46412-003 Matrix: Aqueous
Batch:46412 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Spike
Amount
Result
% Rec
% RPD
Parameter
(ug/L)
(ug/L) Q
Dil % Rec % RPD Limit
Limit Analysis Date
C5 - C8 Aliphatics
150
140
1 94 1.4 70-130
25 02/27/2020 1000
C9 - C12 Aliphatics
180
170
1 97 0.82 70-130
25 02/27/2020 1000
Surrogate
2,5-Dibromotoluene (FID)
LOQ = Limit of Quantitation
DL = Detection Limit
LOD = Limit of Detection
Acceptance
Q % Rec Limit
98 70-130
P = The RPD between two GC columns exceeds 40 % N = Recovery is out of criteria
J = Estimated result < LOQ and > DL + = RPD is out of criteria
ND = Not detected at or above the DL
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 43 of 46
Chain of Custody
and
Miscellaneous Documents
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 44 of 46
PACE ANALYTICAL SERVICES, LLC
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Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 45 of 46
PACE ANALYTICAL SERVICES, LLC
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 46 of 46
0
aceAnalytical
Report of Analysis
Apex Companies, LLC
10610 Metromont Parkway
Suite 206
Charlotte, NC 28269
Attention: Andrew Street
Project Name: CPC Kannapolis
Project Number: CPC 20107 Task 1
Lot Number:VH07111
Date Completed:08/26/2020
08/26/2020 3:42 PM
Approved and released by:
Project Manager II: Lucas Odom
pCC/►F�
24r�A
SOA
ANSI National Accreditation Board
A C C R E D I T E D
TESTING LABORATORY
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Page 1 of 49
PACE ANALYTICAL SERVICES, LLC
SC DHEC No: 32010001 NELAC No: E87653 NC DENR No: 329 NC Field Parameters No: 5639
Case Narrative
Apex Companies, LLC
Lot Number: VH07111
This Report of Analysis contains the analytical result(s) for the sample(s) listed on the Sample Summary
following this Case Narrative. The sample receiving date is documented in the header information
associated with each sample.
All results listed in this report relate only to the samples that are contained within this report.
Sample receipt, sample analysis, and data review have been performed in accordance with the most
current approved NELAC standards, the Pace Analytical Services, LLC ("Pace") Quality Assurance
Management Plan (QAMP), standard operating procedures (SOPS), and Pace policies. Any exceptions to
the NELAC standards, the QAMP, SOPS or policies are qualified on the results page or discussed below.
If you have any questions regarding this report please contact the Pace Project Manager listed on the
cover page.
EPH
Surrogate recovery for the following samples was outside control limits: VH07111-005, VH07111-006.
Evidence of matrix interference is present; therefore, re -extraction and/or re -analysis was not performed.
SVOCs by GUMS
The laboratory control sample (LCS) for analytical batch 63591 recovered marginally outside acceptance
criteria for 2-Chloronapthalene. The following samples are out of hold: VH07111-004, VH07111-005,
VH07111-006. The data has been reported.
The following sample was diluted due to the nature of the sample matrix: VH07111-006. The LOQ has
been elevated to reflect the dilution.
The initial calibration verification (ICV) associated with samples VH07111-004, VH07111-005, VH07111-
006 exceeded control criteria of 70-130 for analytes: Nitrobenzene, Isophorone. The data has been
reported.
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Page 2 of 49
PACE ANALYTICAL SERVICES, LLC
Sample Summary
Apex Companies, LLC
Lot Number: VH07111
Sample Number
Sample ID
Matrix
Date Sampled
Date Received
001
MW-13
Aqueous
08/06/20201330
08/07/2020
002
MW-8
Aqueous
08/06/20201305
08/07/2020
003
MW-6
Aqueous
08/06/20201240
08/07/2020
004
MW-25D
Aqueous
08/06/20201210
08/07/2020
005
MW-25
Aqueous
08/06/20201130
08/07/2020
006
MW-24
Aqueous
08/06/20201055
08/07/2020
007
MW-4
Aqueous
08/06/20201025
08/07/2020
008
DUP-1
Aqueous
08/06/2020
08/07/2020
009
EB-1
Aqueous
08/06/2020
08/07/2020
010
TRIP BLANK
Aqueous
08/06/2020
08/07/2020
(10 samples)
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 3 of 49
PACE ANALYTICAL SERVICES, LLC
Detection Summary
Apex Companies, LLC
Lot Number: VH07111
Sample Sample ID
Matrix
Parameter
Method
Result
Q
Units
Page
001
MW-13
Aqueous
Benzene
SM 6200B-
0.45
J
ug/L
5
001
MW-13
Aqueous
Methyl tertiary butyl ether
SM 6200B-
7.2
ug/L
5
004
MW-25D
Aqueous
Di-n-butyl phthalate
625.1
0.93
J
ug/L
9
005
MW-25
Aqueous
Di-n-butyl phthalate
625.1
0.86
J
ug/L
13
006
MW-24
Aqueous
Benzene
SM 6200B-
4.9
ug/L
16
006
MW-24
Aqueous
Ethylbenzene
SM 6200B-
2.0
ug/L
16
006
MW-24
Aqueous
Toluene
SM 6200B-
1.1
ug/L
16
006
MW-24
Aqueous
Xylenes (total)
SM 6200B-
2.7
ug/L
16
006
MW-24
Aqueous
Fluoranthene
625.1
5.2
J
ug/L
17
006
MW-24
Aqueous
1-Methylnaphthalene
625.1
2.6
J
ug/L
17
006
MW-24
Aqueous
Pyrene
625.1
4.7
J
ug/L
17
006
MW-24
Aqueous
C11 - C22 Aromatics
MADEP-EPH-
140
ug/L
18
006
MW-24
Aqueous
C5 - C8 Aliphatics
MADEP-VPH-
790
ug/L
18
006
MW-24
Aqueous
C9 - C12 Aliphatics
MADEP-VPH-
200
ug/L
18
006
MW-24
Aqueous
C9 - C10 Aromatics
MADEP-VPH-
220
ug/L
19
(15 detections)
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Page 4 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-001
Description: MW-13 Matrix: Aqueous
Date Sampled:08/06/2020 1330
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
2 SM 6200B- SM 620OB-2011 1 08/15/2020 0516 DJG 63623
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 620OB-2011
0.45 J
0.50
0.40
ug/L
2
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
2
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 620OB-2011
7.2
0.50
0.40
ug/L
2
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
2
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
2
Run 2 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
100 70-130
1,2-Dichloroethane-d4
104 70-130
Toluene-d8
96 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 5 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-002
Description: MW-8 Matrix: Aqueous
Date Sampled:08/06/2020 1305
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 08/12/2020 0129 JAN 63127
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
97 70-130
1,2-Dichloroethane-d4
81 70-130
Toluene-d8
93 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 6 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-003
Description: MW-6 Matrix: Aqueous
Date Sampled:08/06/2020 1240
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 08/12/2020 0154 JAN 63127
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
96 70-130
1,2-Dichloroethane-d4
80 70-130
Toluene-d8
92 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 7 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-004
Description: MW-25D Matrix: Aqueous
Date Sampled:08/06/2020 1210
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 SM 6200B-
SM 620OB-2011 1 08/12/2020 0219 JAN
63127
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Benzene
71-43-2 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
96 70-130
1,2-Dichloroethane-d4
82 70-130
Toluene-d8
91 70-130
Semivolatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 625.1
625.1 1 08/25/2020 1957 JCG
08/10/2020 1715 62956
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Acenaphthene
83-32-9 625.1
ND
1.6
0.80
ug/L
1
Acenaphthylene
208-96-8 625.1
ND
1.6
0.80
ug/L
1
Anthracene
120-12-7 625.1
ND
1.6
0.80
ug/L
1
Benzo(a)anthracene
56-55-3 625.1
ND
1.6
0.80
ug/L
1
Benzo(a)pyrene
50-32-8 625.1
ND
1.6
0.80
ug/L
1
Benzo(b)fluoranthene
205-99-2 625.1
ND
1.6
0.80
ug/L
1
Benzo(g,h,i)perylene
191-24-2 625.1
ND
1.6
0.80
ug/L
1
Benzo(k)fluoranthene
207-08-9 625.1
ND
1.6
0.80
ug/L
1
Benzyl alcohol
100-51-6 625.1
ND
3.2
2.0
ug/L
1
4-Bromophenyl phenyl ether
101-55-3 625.1
ND
1.6
0.80
ug/L
1
Butyl benzyl phthalate
85-68-7 625.1
ND
1.6
0.80
ug/L
1
bis (2-Chloro-1-methylethyl) ether
108-60-1 625.1
ND
1.6
0.80
ug/L
1
4-Chloro-3-methyl phenol
59-50-7 625.1
ND
1.6
0.80
ug/L
1
bis(2-Chloroethoxy)methane
111-91-1 625.1
ND
1.6
0.80
ug/L
1
bis(2-Chloroethyl)ether
111-44-4 625.1
ND
1.6
0.80
ug/L
1
2-Chloronaphthalene
91-58-7 625.1
ND
1.6
0.80
ug/L
1
2-Chlorophenol
95-57-8 625.1
ND
1.6
0.80
ug/L
1
4-Chlorophenyl phenyl ether
7005-72-3 625.1
ND
1.6
0.80
ug/L
1
Chrysene
218-01-9 625.1
ND
1.6
0.80
ug/L
1
Dibenzo(a,h)anthracene
53-70-3 625.1
ND
1.6
0.80
ug/L
1
Dibenzofuran
132-64-9 625.1
ND
1.6
1.0
ug/L
1
3,3'-Dichlorobenzidine
91-94-1 625.1
ND
8.0
0.80
ug/L
1
2,4-Dichlorophenol
120-83-2 625.1
ND
1.6
0.80
ug/L
1
Diethylphthalate
84-66-2 625.1
ND
1.6
0.80
ug/L
1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range DL =
Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result <
LOQ and > DL
H = Out of holding time W =
Reported on wet weight basis
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Page 8 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-004
Description: MW-25D Matrix: Aqueous
Date Sampled:08/06/2020 1210
Date Received:08/07/2020
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 625.1 625.1 1 08/25/2020 1957 JCG 08/10/2020 1715 62956
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Dimethyl phthalate
131-11-3
625.1
ND
1.6
0.80
ug/L
2,4-Dimethylphenol
105-67-9
625.1
ND
1.6
0.80
ug/L
Di-n-butyl phthalate
84-74-2
625.1
0.93 J
1.6
0.81
ug/L
4,6-Dinitro-2-methylphenol
534-52-1
625.1
ND
8.0
0.80
ug/L
2,4-Dinitrophenol
51-28-5
625.1
ND
8.0
0.80
ug/L
Di-n-octylphthalate
117-84-0
625.1
ND
1.6
0.80
ug/L
1,2-Diphenylhydrazine(as azobenzene)
103-33-3
625.1
ND
1.6
0.80
ug/L
bis(2-Ethylhexyl)phthalate
117-81-7
625.1
ND
8.0
4.0
ug/L
Fluoranthene
206-44-0
625.1
ND
1.6
0.80
ug/L
Fluorene
86-73-7
625.1
ND
1.6
0.80
ug/L
Hexachlorobenzene
118-74-1
625.1
ND
1.6
0.80
ug/L
Hexachlorobutadiene
87-68-3
625.1
ND
1.6
0.80
ug/L
Hexachlorocyclopentadiene
77-47-4
625.1
ND
8.0
4.0
ug/L
Hexachloroethane
67-72-1
625.1
ND
1.6
0.80
ug/L
Indeno(1,2,3-c,d)pyrene
193-39-5
625.1
ND
1.6
0.80
ug/L
Isophorone
78-59-1
625.1
ND
1.6
0.80
ug/L
1-Methylnaphthalene
90-12-0
625.1
ND
1.6
0.40
ug/L
2-Methylnaphthalene
91-57-6
625.1
ND
1.6
0.40
ug/L
2-Methylphenol
95-48-7
625.1
ND
1.6
0.67
ug/L
3+4-Methylphenol
106-44-5
625.1
ND
1.6
1.5
ug/L
Naphthalene
91-20-3
625.1
ND
1.6
0.80
ug/L
Nitrobenzene
98-95-3
625.1
ND
1.6
0.80
ug/L
2-Nitrophenol
88-75-5
625.1
ND
3.2
0.80
ug/L
4-Nitrophenol
100-02-7
625.1
ND
8.0
4.0
ug/L
N-Nitrosodi-n-propylamine
621-64-7
625.1
ND
1.6
0.80
ug/L
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
625.1
ND
1.6
0.80
ug/L
Pentachlorophenol
87-86-5
625.1
ND
8.0
4.0
ug/L
Phenanthrene
85-01-8
625.1
ND
1.6
0.80
ug/L
Phenol
108-95-2
625.1
ND
1.6
0.80
ug/L
Pyrene
129-00-0
625.1
ND
1.6
0.80
ug/L
1,2,4-Trichlorobenzene
120-82-1
625.1
ND
1.6
0.80
ug/L
2,4,6-Trichlorophenol
88-06-2
625.1
ND
1.6
0.80
ug/L
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 9 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-004
Description: MW-25D Matrix: Aqueous
Date Sampled:08/06/2020 1210
Date Received:08/07/2020
Run 1 Acceptance
Surrogate
Q % Recovery Limits
2-Fluorobiphenyl
81 37-129
2-Fluorophenol
52 24-127
Nitrobenzene-d5
71 38-127
Phenol-d5
64 28-128
Terphenyl-d14
50 10-148
2,4,6-Tribromophenol
105 41-144
MADEP EPH (aromatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 08/14/2020 2021 JJG 08/12/2020 1505 63243
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C11 - C22 Aromatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
o - Terphenyl (aromatic)
76 40-140
2-Fluorobiphenyl (fractionation 1)
80 40-140
2-Bromonaphthalene (fractionation
2) 82 40-140
MADEP EPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 08/14/2020 1718 JJG 08/12/2020 1505 63242
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C9 - C18 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
C19 - C36 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
1-Chloro-octadecane (aliphatic)
49 40-140
MADEP VPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
2 VPH
MADEP-VPH-18-2.1 1 08/13/2020 0126 STM
63321
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C5 - C8 Aliphatics
MADEP-VPH-18- ND
75
15 ug/L 2
C9 - C12 Aliphatics
MADEP-VPH-18- ND
75
15 ug/L 2
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range
DL = Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 %
J = Estimated result <
LOQ and > DL
H = Out of holding time W
= Reported on wet weight basis
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Page 10 of 49
Client:Apex Companies, LLC Laboratory ID: VH07111-004
Description: MW-25D Matrix: Aqueous
Date Sampled:08/06/2020 1210
Date Received:08/07/2020
Run 2 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (FID) 84 70-130
MADEP VPH (aromatics)
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
2 VPH MADEP-VPH-18-2.1 1 08/13/2020 0126 STM 63322
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
C9 - C10 Aromatics MADEP-VPH-18- ND 25 5.0 ug/L 2
Run 2 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (PID) 82 70-130
LOCI = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
ND = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 11 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-005
Description: MW-25 Matrix: Aqueous
Date Sampled:08/06/2020 1130
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 SM 6200B-
SM 620OB-2011 1 08/12/2020 0243 JAN
63127
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Benzene
71-43-2 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
96 70-130
1,2-Dichloroethane-d4
80 70-130
Toluene-d8
90 70-130
Semivolatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 625.1
625.1 1 08/25/2020 2023 JCG
08/10/2020 1715 62956
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Acenaphthene
83-32-9 625.1
ND
1.6
0.80
ug/L
1
Acenaphthylene
208-96-8 625.1
ND
1.6
0.80
ug/L
1
Anthracene
120-12-7 625.1
ND
1.6
0.80
ug/L
1
Benzo(a)anthracene
56-55-3 625.1
ND
1.6
0.80
ug/L
1
Benzo(a)pyrene
50-32-8 625.1
ND
1.6
0.80
ug/L
1
Benzo(b)fluoranthene
205-99-2 625.1
ND
1.6
0.80
ug/L
1
Benzo(g,h,i)perylene
191-24-2 625.1
ND
1.6
0.80
ug/L
1
Benzo(k)fluoranthene
207-08-9 625.1
ND
1.6
0.80
ug/L
1
Benzyl alcohol
100-51-6 625.1
ND
3.2
2.0
ug/L
1
4-Bromophenyl phenyl ether
101-55-3 625.1
ND
1.6
0.80
ug/L
1
Butyl benzyl phthalate
85-68-7 625.1
ND
1.6
0.80
ug/L
1
bis (2-Chloro-1-methylethyl) ether
108-60-1 625.1
ND
1.6
0.80
ug/L
1
4-Chloro-3-methyl phenol
59-50-7 625.1
ND
1.6
0.80
ug/L
1
bis(2-Chloroethoxy)methane
111-91-1 625.1
ND
1.6
0.80
ug/L
1
bis(2-Chloroethyl)ether
111-44-4 625.1
ND
1.6
0.80
ug/L
1
2-Chloronaphthalene
91-58-7 625.1
ND
1.6
0.80
ug/L
1
2-Chlorophenol
95-57-8 625.1
ND
1.6
0.80
ug/L
1
4-Chlorophenyl phenyl ether
7005-72-3 625.1
ND
1.6
0.80
ug/L
1
Chrysene
218-01-9 625.1
ND
1.6
0.80
ug/L
1
Dibenzo(a,h)anthracene
53-70-3 625.1
ND
1.6
0.80
ug/L
1
Dibenzofuran
132-64-9 625.1
ND
1.6
1.0
ug/L
1
3,3'-Dichlorobenzidine
91-94-1 625.1
ND
8.0
0.80
ug/L
1
2,4-Dichlorophenol
120-83-2 625.1
ND
1.6
0.80
ug/L
1
Diethylphthalate
84-66-2 625.1
ND
1.6
0.80
ug/L
1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range DL =
Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result <
LOQ and > DL
H = Out of holding time W =
Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 12 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-005
Description: MW-25 Matrix: Aqueous
Date Sampled:08/06/2020 1130
Date Received:08/07/2020
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 625.1 625.1 1 08/25/2020 2023 JCG 08/10/2020 1715 62956
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Dimethyl phthalate
131-11-3
625.1
ND
1.6
0.80
ug/L
2,4-Dimethylphenol
105-67-9
625.1
ND
1.6
0.80
ug/L
Di-n-butyl phthalate
84-74-2
625.1
0.86 J
1.6
0.81
ug/L
4,6-Dinitro-2-methylphenol
534-52-1
625.1
ND
8.0
0.80
ug/L
2,4-Dinitrophenol
51-28-5
625.1
ND
8.0
0.80
ug/L
Di-n-octylphthalate
117-84-0
625.1
ND
1.6
0.80
ug/L
1,2-Diphenylhydrazine(as azobenzene)
103-33-3
625.1
ND
1.6
0.80
ug/L
bis(2-Ethylhexyl)phthalate
117-81-7
625.1
ND
8.0
4.0
ug/L
Fluoranthene
206-44-0
625.1
ND
1.6
0.80
ug/L
Fluorene
86-73-7
625.1
ND
1.6
0.80
ug/L
Hexachlorobenzene
118-74-1
625.1
ND
1.6
0.80
ug/L
Hexachlorobutadiene
87-68-3
625.1
ND
1.6
0.80
ug/L
Hexachlorocyclopentadiene
77-47-4
625.1
ND
8.0
4.0
ug/L
Hexachloroethane
67-72-1
625.1
ND
1.6
0.80
ug/L
Indeno(1,2,3-c,d)pyrene
193-39-5
625.1
ND
1.6
0.80
ug/L
Isophorone
78-59-1
625.1
ND
1.6
0.80
ug/L
1-Methylnaphthalene
90-12-0
625.1
ND
1.6
0.40
ug/L
2-Methylnaphthalene
91-57-6
625.1
ND
1.6
0.40
ug/L
2-Methylphenol
95-48-7
625.1
ND
1.6
0.67
ug/L
3+4-Methylphenol
106-44-5
625.1
ND
1.6
1.5
ug/L
Naphthalene
91-20-3
625.1
ND
1.6
0.80
ug/L
Nitrobenzene
98-95-3
625.1
ND
1.6
0.80
ug/L
2-Nitrophenol
88-75-5
625.1
ND
3.2
0.80
ug/L
4-Nitrophenol
100-02-7
625.1
ND
8.0
4.0
ug/L
N-Nitrosodi-n-propylamine
621-64-7
625.1
ND
1.6
0.80
ug/L
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
625.1
ND
1.6
0.80
ug/L
Pentachlorophenol
87-86-5
625.1
ND
8.0
4.0
ug/L
Phenanthrene
85-01-8
625.1
ND
1.6
0.80
ug/L
Phenol
108-95-2
625.1
ND
1.6
0.80
ug/L
Pyrene
129-00-0
625.1
ND
1.6
0.80
ug/L
1,2,4-Trichlorobenzene
120-82-1
625.1
ND
1.6
0.80
ug/L
2,4,6-Trichlorophenol
88-06-2
625.1
ND
1.6
0.80
ug/L
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 13 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-005
Description: MW-25 Matrix: Aqueous
Date Sampled:08/06/2020 1130
Date Received:08/07/2020
Run 1 Acceptance
Surrogate
Q % Recovery Limits
2-Fluorobiphenyl
69 37-129
2-Fluorophenol
51 24-127
Nitrobenzene-d5
65 38-127
Phenol-d5
53 28-128
Terphenyl-d14
78 10-148
2,4,6-Tribromophenol
88 41-144
MADEP EPH (aromatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 08/14/2020 2052 JJG 08/12/2020 1505 63243
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C11 - C22 Aromatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
o - Terphenyl (aromatic)
67 40-140
2-Fluorobiphenyl (fractionation 1)
72 40-140
2-Bromonaphthalene (fractionation
2) 69 40-140
MADEP EPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 08/14/2020 1748 JJG 08/12/2020 1505 63242
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C9 - C18 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
C19 - C36 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
1-Chloro-octadecane (aliphatic)
N 27 40-140
MADEP VPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
2 VPH
MADEP-VPH-18-2.1 1 08/13/2020 0155 STM
63321
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C5 - C8 Aliphatics
MADEP-VPH-18- ND
75
15 ug/L 2
C9 - C12 Aliphatics
MADEP-VPH-18- ND
75
15 ug/L 2
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range
DL = Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 %
J = Estimated result <
LOQ and > DL
H = Out of holding time W
= Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 14 of 49
Client:Apex Companies, LLC Laboratory ID: VH07111-005
Description: MW-25 Matrix: Aqueous
Date Sampled:08/06/2020 1130
Date Received:08/07/2020
Run 2 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (FID) 90 70-130
MADEP VPH (aromatics)
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
2 VPH MADEP-VPH-18-2.1 1 08/13/2020 0155 STM 63322
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
C9 - C10 Aromatics MADEP-VPH-18- ND 25 5.0 ug/L 2
Run 2 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (PID) 86 70-130
LOCI = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
ND = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 15 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-006
Description: MW-24 Matrix: Aqueous
Date Sampled:08/06/2020 1055
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
2 SM 6200B-
SM 620OB-2011 1 08/15/2020 0538 DJG
63623
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Benzene
71-43-2 SM 620OB-2011
4.9
0.50
0.40
ug/L
2
Ethylbenzene
100-41-4 SM 620OB-2011
2.0
0.50
0.40
ug/L
2
Toluene
108-88-3 SM 620OB-2011
1.1
0.50
0.40
ug/L
2
Xylenes (total)
1330-20-7 SM 620OB-2011
2.7
0.50
0.40
ug/L
2
Run 2 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
105 70-130
1,2-Dichloroethane-d4
108 70-130
Toluene-d8
99 70-130
Semivolatile Organic Compounds by GC/MS
Run Prep Method
Analytical Method Dilution Analysis Date Analyst
Prep Date
Batch
1 625.1
625.1 5 08/25/2020 2048 JCG
08/10/2020 1715 62956
CAS Analytical
Parameter
Number Method
Result Q
LOQ
DL
Units
Run
Acenaphthene
83-32-9 625.1
ND
8.0
4.0
ug/L
1
Acenaphthylene
208-96-8 625.1
ND
8.0
4.0
ug/L
1
Anthracene
120-12-7 625.1
ND
8.0
4.0
ug/L
1
Benzo(a)anthracene
56-55-3 625.1
ND
8.0
4.0
ug/L
1
Benzo(a)pyrene
50-32-8 625.1
ND
8.0
4.0
ug/L
1
Benzo(b)fluoranthene
205-99-2 625.1
ND
8.0
4.0
ug/L
1
Benzo(g,h,i)perylene
191-24-2 625.1
ND
8.0
4.0
ug/L
1
Benzo(k)fluoranthene
207-08-9 625.1
ND
8.0
4.0
ug/L
1
Benzyl alcohol
100-51-6 625.1
ND
16
10
ug/L
1
4-Bromophenyl phenyl ether
101-55-3 625.1
ND
8.0
4.0
ug/L
1
Butyl benzyl phthalate
85-68-7 625.1
ND
8.0
4.0
ug/L
1
bis (2-Chloro-1-methylethyl) ether
108-60-1 625.1
ND
8.0
4.0
ug/L
1
4-Chloro-3-methyl phenol
59-50-7 625.1
ND
8.0
4.0
ug/L
1
bis(2-Chloroethoxy)methane
111-91-1 625.1
ND
8.0
4.0
ug/L
1
bis(2-Chloroethyl)ether
111-44-4 625.1
ND
8.0
4.0
ug/L
1
2-Chloronaphthalene
91-58-7 625.1
ND
8.0
4.0
ug/L
1
2-Chlorophenol
95-57-8 625.1
ND
8.0
4.0
ug/L
1
4-Chlorophenyl phenyl ether
7005-72-3 625.1
ND
8.0
4.0
ug/L
1
Chrysene
218-01-9 625.1
ND
8.0
4.0
ug/L
1
Dibenzo(a,h)anthracene
53-70-3 625.1
ND
8.0
4.0
ug/L
1
Dibenzofuran
132-64-9 625.1
ND
8.0
5.0
ug/L
1
3,3'-Dichlorobenzidine
91-94-1 625.1
ND
40
4.0
ug/L
1
2,4-Dichlorophenol
120-83-2 625.1
ND
8.0
4.0
ug/L
1
Diethylphthalate
84-66-2 625.1
ND
8.0
4.0
ug/L
1
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range DL =
Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result <
LOQ and > DL
H = Out of holding time W =
Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 16 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-006
Description: MW-24 Matrix: Aqueous
Date Sampled:08/06/2020 1055
Date Received:08/07/2020
Semivolatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 625.1 625.1 5 08/25/2020 2048 JCG 08/10/2020 1715 62956
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Dimethyl phthalate
131-11-3
625.1
ND
8.0
4.0
ug/L
2,4-Dimethylphenol
105-67-9
625.1
ND
8.0
4.0
ug/L
Di-n-butyl phthalate
84-74-2
625.1
ND
8.0
4.1
ug/L
4,6-Dinitro-2-methylphenol
534-52-1
625.1
ND
40
4.0
ug/L
2,4-Dinitrophenol
51-28-5
625.1
ND
40
4.0
ug/L
Di-n-octylphthalate
117-84-0
625.1
ND
8.0
4.0
ug/L
1,2-Diphenylhydrazine(as azobenzene)
103-33-3
625.1
ND
8.0
4.0
ug/L
bis(2-Ethylhexyl)phthalate
117-81-7
625.1
ND
40
20
ug/L
Fluoranthene
206-44-0
625.1
5.2 J
8.0
4.0
ug/L
Fluorene
86-73-7
625.1
ND
8.0
4.0
ug/L
Hexachlorobenzene
118-74-1
625.1
ND
8.0
4.0
ug/L
Hexachlorobutadiene
87-68-3
625.1
ND
8.0
4.0
ug/L
Hexachlorocyclopentadiene
77-47-4
625.1
ND
40
20
ug/L
Hexachloroethane
67-72-1
625.1
ND
8.0
4.0
ug/L
Indeno(1,2,3-c,d)pyrene
193-39-5
625.1
ND
8.0
4.0
ug/L
Isophorone
78-59-1
625.1
ND
8.0
4.0
ug/L
1-Methylnaphthalene
90-12-0
625.1
2.6 J
8.0
2.0
ug/L
2-Methylnaphthalene
91-57-6
625.1
ND
8.0
2.0
ug/L
2-Methylphenol
95-48-7
625.1
ND
8.0
3.4
ug/L
3+4-Methylphenol
106-44-5
625.1
ND
8.0
7.5
ug/L
Naphthalene
91-20-3
625.1
ND
8.0
4.0
ug/L
Nitrobenzene
98-95-3
625.1
ND
8.0
4.0
ug/L
2-Nitrophenol
88-75-5
625.1
ND
16
4.0
ug/L
4-Nitrophenol
100-02-7
625.1
ND
40
20
ug/L
N-Nitrosodi-n-propylamine
621-64-7
625.1
ND
8.0
4.0
ug/L
N-Nitrosodiphenylamine (Diphenylamine)
86-30-6
625.1
ND
8.0
4.0
ug/L
Pentachlorophenol
87-86-5
625.1
ND
40
20
ug/L
Phenanthrene
85-01-8
625.1
ND
8.0
4.0
ug/L
Phenol
108-95-2
625.1
ND
8.0
4.0
ug/L
Pyrene
129-00-0
625.1
4.7 J
8.0
4.0
ug/L
1,2,4-Trichlorobenzene
120-82-1
625.1
ND
8.0
4.0
ug/L
2,4,6-Trichlorophenol
88-06-2
625.1
ND
8.0
4.0
ug/L
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 17 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-006
Description: MW-24 Matrix: Aqueous
Date Sampled:08/06/2020 1055
Date Received:08/07/2020
Run 1 Acceptance
Surrogate
Q % Recovery Limits
2-Fluorobiphenyl
68 37-129
2-Fluorophenol
48 24-127
Nitrobenzene-d5
68 38-127
Phenol-d5
52 28-128
Terphenyl-d14
46 10-148
2,4,6-Tribromophenol
86 41-144
MADEP EPH (aromatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 08/14/2020 2123 JJG 08/12/2020 1505 63243
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C11 - C22 Aromatics
MADEP-EPH-04 140
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
o - Terphenyl (aromatic)
75 40-140
2-Fluorobiphenyl (fractionation 1)
86 40-140
2-Bromonaphthalene (fractionation
2) 88 40-140
MADEP EPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
1 MADEP-EPH-
MADEP-EPH-04 1 08/14/2020 1819 JJG 08/12/2020 1505 63242
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C9 - C18 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
C19 - C36 Aliphatics
MADEP-EPH-04 ND
100
100 ug/L 1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
1-Chloro-octadecane (aliphatic)
N 39 40-140
MADEP VPH (aliphatics)
Run Prep Method
Analytical Method Dilution Analysis Date Analyst Prep Date
Batch
2 VPH
MADEP-VPH-18-2.1 1 08/13/2020 0224 STM
63321
CAS Analytical
Parameter
Number Method Result Q
LOQ
DL Units Run
C5 - C8 Aliphatics
MADEP-VPH-18- 790
75
15 ug/L 2
C9 - C12 Aliphatics
MADEP-VPH-18- 200
75
15 ug/L 2
LOQ = Limit of Quantitation B =
Detected in the method blank E = Quantitation of compound exceeded the calibration range
DL = Detection Limit
NO = Not detected at or above the DL N =
Recovery is out of criteria P = The RPD between two GC columns exceeds 40 %
J = Estimated result <
LOQ and > DL
H = Out of holding time W
= Reported on wet weight basis
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Page 18 of 49
Client:Apex Companies, LLC Laboratory ID: VH07111-006
Description: MW-24 Matrix: Aqueous
Date Sampled:08/06/2020 1055
Date Received:08/07/2020
Run 2 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (FID) 70 70-130
MADEP VPH (aromatics)
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
2 VPH MADEP-VPH-18-2.1 1 08/13/2020 0224 STM 63322
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
C9 - C10 Aromatics MADEP-VPH-18- 220 25 5.0 ug/L 2
Run 2 Acceptance
Surrogate Q % Recovery Limits
2,5-Dibromotoluene (PID) 73 70-130
LOCI = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
ND = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 19 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-007
Description: MW-4 Matrix: Aqueous
Date Sampled:08/06/2020 1025
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 08/12/2020 0308 JAN 63127
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
97 70-130
1,2-Dichloroethane-d4
81 70-130
Toluene-d8
93 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 20 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-008
Description: DUP-1 Matrix: Aqueous
Date Sampled:08/06/2020
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 08/12/2020 0333 JAN 63127
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
97 70-130
1,2-Dichloroethane-d4
81 70-130
Toluene-d8
90 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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Page 21 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-009
Description: EB-1 Matrix: Aqueous
Date Sampled:08/06/2020
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 6200B- SM 620OB-2011 1 08/12/2020 0039 JAN 63127
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
96 70-130
1,2-Dichloroethane-d4
79 70-130
Toluene-d8
92 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 22 of 49
Client:Apex Companies, LLC Laboratory ID:VH07111-010
Description: TRIP BLANK Matrix: Aqueous
Date Sampled:08/06/2020
Date Received:08/07/2020
Volatile Organic Compounds by GC/MS
Run Prep Method Analytical Method Dilution Analysis Date Analyst Prep Date Batch
1 SM 620013- SM 620OB-2011 1 08/12/2020 0104 JAN 63127
CAS Analytical
Parameter Number Method Result Q LOQ DL Units Run
Benzene
71-43-2 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Ethylbenzene
100-41-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Methyl tertiary butyl ether (MTBE)
1634-04-4 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Toluene
108-88-3 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Xylenes (total)
1330-20-7 SM 620OB-2011
ND
0.50
0.40
ug/L
1
Run 1 Acceptance
Surrogate
Q % Recovery Limits
Bromofluorobenzene
95 70-130
1,2-Dichloroethane-d4
80 70-130
Toluene-d8
93 70-130
LOQ = Limit of Quantitation B = Detected in the method blank E = Quantitation of compound exceeded the calibration range DL = Detection Limit
NO = Not detected at or above the DL N = Recovery is out of criteria P = The RPD between two GC columns exceeds 40 % J = Estimated result < LOQ and > DL
H = Out of holding time W = Reported on wet weight basis
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 23 of 49
QC Summary
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Page 24 of 49
Volatile Organic Compounds by GC/MS - MB
Sample ID: VQ63127-001 Matrix: Aqueous
Batch: 63127 Prep Method: SM 620OB-2011
Analytical Method: SM 620OB-2011
Parameter
Result
Q Dil
LOQ
DL
Units
Analysis Date
Benzene
ND
1
0.50
0.40
ug/L
08/11/2020 2320
Ethylbenzene
ND
1
0.50
0.40
ug/L
08/11/2020 2320
Methyl tertiary butyl ether (MTBE)
ND
1
0.50
0.40
ug/L
08/11/2020 2320
Toluene
ND
1
0.50
0.40
ug/L
08/11/2020 2320
Xylenes (total)
ND
1
0.50
0.40
ug/L
08/11/2020 2320
Acceptance
Surrogate
Q % Rec
Limit
Bromofluorobenzene 98 70-130
1,2-Dichloroethane-d4 80 70-130
Toluene-d8 93 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 25 of 49
Volatile Organic Compounds by GC/MS - LCS
Sample ID: VQ63127-002
Matrix:
Aqueous
Batch: 63127
Prep Method:
SM 620OB-2011
Analytical Method: SM 620OB-2011
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L) Q
Dil
% Rec
Limit
Analysis Date
Benzene
50
48
1
95
70-130
08/11/2020 2212
Ethylbenzene
50
53
1
105
70-130
08/11/2020 2212
Methyl tertiary butyl ether (MTBE)
50
42
1
83
70-130
08/11/2020 2212
Toluene
50
51
1
102
70-130
08/11/2020 2212
Xylenes (total)
100
100
1
102
70-130
08/11/2020 2212
Surrogate
Q % Rec
Acceptance
Limit
Bromofluorobenzene 93 70-130
1,2-Dichloroethane-d4 78 70-130
Toluene-d8 99 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 26 of 49
Volatile Organic Compounds by GC/MS - MS
Sample ID: VH071 11 -001 MS
Matrix:
Aqueous
Batch: 63127
Prep Method:
SM 620OB-2011
Analytical Method: SM 620OB-2011
Sample
Spike
Amount
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L)
(ug/L) Q
Dil
% Rec
Limit
Analysis Date
Benzene
ND
250
260
5
102
70-130
08/12/2020 0448
Ethylbenzene
ND
250
280
5
112
70-130
08/12/2020 0448
Methyl tertiary butyl ether (MTBE)
5.5
250
210
5
83
70-130
08/12/2020 0448
Toluene
ND
250
270
5
107
70-130
08/12/2020 0448
Xylenes (total)
ND
500
540
5
107
70-130
08/12/2020 0448
Surrogate
Q % Rec
Acceptance
Limit
Bromofluorobenzene 99 70-130
1,2-Dichloroethane-d4 82 70-130
Toluene-d8 103 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 27 of 49
Volatile Organic Compounds by GC/MS - MSD
Sample ID: VH071 11 -001 MID
Matrix:
Aqueous
Batch: 63127
Prep Method:
SM 620OB-2011
Analytical Method: SM 620OB-2011
Sample
Spike
Amount
Amount
Result
% Rec
% RPD
Parameter
(ug/L)
(ug/L)
(ug/L)
Q Dil
% Rec % RPD
Limit
Limit
Analysis Date
Benzene
ND
250
260
5
102
0.13
70-130
20
08/12/2020 0513
Ethylbenzene
ND
250
280
5
113
0.82
70-130
20
08/12/2020 0513
Methyl tertiary butyl ether (MTBE)
5.5
250
230
5
88
5.7
70-130
20
08/12/2020 0513
Toluene
ND
250
270
5
110
2.1
70-130
20
08/12/2020 0513
Xylenes (total)
ND
500
550
5
109
1.7
70-130
20
08/12/2020 0513
Acceptance
Surrogate
Q % Rec
Limit
Bromofluorobenzene 97 70-130
1,2-Dichloroethane-d4 81 70-130
Toluene-d8 104 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 28 of 49
Volatile Organic Compounds by GC/MS - MB
Sample ID: VQ63623-001 Matrix: Aqueous
Batch: 63623 Prep Method: SM 620OB-2011
Analytical Method: SM 620OB-2011
Parameter
Result
Q Dil
LOQ
DL
Units
Analysis Date
Benzene
ND
1
0.50
0.40
ug/L
08/14/2020 2216
Ethylbenzene
ND
1
0.50
0.40
ug/L
08/14/2020 2216
Methyl tertiary butyl ether (MTBE)
ND
1
0.50
0.40
ug/L
08/14/2020 2216
Toluene
ND
1
0.50
0.40
ug/L
08/14/2020 2216
Xylenes (total)
ND
1
0.50
0.40
ug/L
08/14/2020 2216
Acceptance
Surrogate
Q % Rec
Limit
Bromofluorobenzene 109 70-130
1,2-Dichloroethane-d4 107 70-130
Toluene-d8 101 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 29 of 49
Volatile Organic Compounds by GC/MS - LCS
Sample ID: VQ63623-002
Matrix:
Aqueous
Batch: 63623
Prep Method:
SM 620OB-2011
Analytical Method: SM 620OB-2011
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L) Q
Dil
% Rec
Limit
Analysis Date
Benzene
50
49
1
97
70-130
08/14/2020 2052
Ethylbenzene
50
49
1
98
70-130
08/14/2020 2052
Methyl tertiary butyl ether (MTBE)
50
52
1
104
70-130
08/14/2020 2052
Toluene
50
49
1
98
70-130
08/14/2020 2052
Xylenes (total)
100
100
1
100
70-130
08/14/2020 2052
Surrogate
Q % Rec
Acceptance
Limit
Bromofluorobenzene 103 70-130
1,2-Dichloroethane-d4 106 70-130
Toluene-d8 102 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 30 of 49
Semivolatile Organic Compounds by GC/MS - MB
Sample ID: VQ62956-001 Matrix: Aqueous
Batch: 62956 Prep Method: 625.1
Analytical Method: 625.1 Prep Date: 08/10/2020 1715
Parameter
Result Q
Dil
LOQ
DL
Units
Analysis Date
Acenaphthene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Acenaphthylene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Anthracene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Benzo(a)anthracene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Benzo(a)pyrene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Benzo(b)fluoranthene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Benzo(g,h,i)perylene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Benzo(k)fluoranthene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Benzyl alcohol
ND
1
3.2
2.0
ug/L
08/14/2020 1505
4-Bromophenyl phenyl ether
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Butyl benzyl phthalate
ND
1
1.6
0.80
ug/L
08/14/2020 1505
bis (2-Chloro-1-methylethyl) ether
ND
1
1.6
0.80
ug/L
08/14/2020 1505
4-Chloro-3-methyl phenol
ND
1
1.6
0.80
ug/L
08/14/2020 1505
bis(2-Chloroethoxy)methane
ND
1
1.6
0.80
ug/L
08/14/2020 1505
bis(2-Chloroethyl)ether
ND
1
1.6
0.80
ug/L
08/14/2020 1505
2-Chloronaphthalene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
2-Chlorophenol
ND
1
1.6
0.80
ug/L
08/14/2020 1505
4-Chlorophenyl phenyl ether
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Chrysene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Dibenzo(a,h)anth race ne
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Dibenzofuran
ND
1
1.6
1.0
ug/L
08/14/2020 1505
3,3'-Dichlorobenzidine
ND
1
8.0
0.80
ug/L
08/14/2020 1505
2,4-Dichlorophenol
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Diethylphthalate
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Dimethyl phthalate
ND
1
1.6
0.80
ug/L
08/14/2020 1505
2,4-Dimethylphenol
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Di-n-butyl phthalate
ND
1
1.6
0.81
ug/L
08/14/2020 1505
4,6-Dinitro-2-methyl phenol
ND
1
8.0
0.80
ug/L
08/14/2020 1505
2,4-Dinitrophenol
ND
1
8.0
0.80
ug/L
08/14/2020 1505
Di-n-octylphthalate
ND
1
1.6
0.80
ug/L
08/14/2020 1505
1,2-Diphenylhydrazine(as azobenzene)
ND
1
1.6
0.80
ug/L
08/14/2020 1505
bis(2-Ethylhexyl)phthalate
ND
1
8.0
4.0
ug/L
08/14/2020 1505
Fluoranthene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Fluorene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Hexachlorobenzene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Hexachlorobutadiene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Hexachlorocyclopentadiene
ND
1
8.0
4.0
ug/L
08/14/2020 1505
Hexachloroethane
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Indeno(1,2,3-c,d)pyrene
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Isophorone
ND
1
1.6
0.80
ug/L
08/14/2020 1505
1-Methyl naphthalene
ND
1
1.6
0.40
ug/L
08/14/2020 1505
2-Methyl naphthalene
ND
1
1.6
0.40
ug/L
08/14/2020 1505
2-Methylphenol
ND
1
1.6
0.67
ug/L
08/14/2020 1505
3+4-Methylphenol
ND
1
1.6
1.5
ug/L
08/14/2020 1505
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
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Page 31 of 49
Semivolatile Organic Compounds by GC/MS - MB
Sample ID: VQ62956-001 Matrix: Aqueous
Batch: 62956 Prep Method: 625.1
Analytical Method: 625.1 Prep Date: 08/10/2020 1715
Parameter
Result Q
Dil
LOQ
DL
Units
Analysis Date
Naphthalene
ND
1
1.6
0.80
ug/L
08/14/20201505
Nitrobenzene
ND
1
1.6
0.80
ug/L
08/14/20201505
2-Nitrophenol
ND
1
3.2
0.80
ug/L
08/14/20201505
4-Nitrophenol
ND
1
8.0
4.0
ug/L
08/14/20201505
N-Nitrosodi-n-propylamine
ND
1
1.6
0.80
ug/L
08/14/20201505
N-Nitrosodiphenylamine (Diphenylamine)
ND
1
1.6
0.80
ug/L
08/14/2020 1505
Pentachlorophenol
ND
1
8.0
4.0
ug/L
08/14/20201505
Phenanthrene
ND
1
1.6
0.80
ug/L
08/14/20201505
Phenol
ND
1
1.6
0.80
ug/L
08/14/20201505
Pyrene
ND
1
1.6
0.80
ug/L
08/14/20201505
1,2,4-Trichlorobenzene
ND
1
1.6
0.80
ug/L
08/14/20201505
2,4,6-Trichlorophenol
ND
1
1.6
0.80
ug/L
08/14/20201505
Surrogate Q /o Rec Acceptance
0
Limit
2-Fluorobiphenyl
61
37-129
2-Fluorophenol
36
24-127
Nitrobenzene-d5
71
38-127
Phenol-d5
60
28-128
Terphenyl-d 14
69
10-148
2,4,6-Tribromophenol
62
41-144
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 32 of 49
Semivolatile Organic Compounds by GC/MS - LCS
Sample ID: VQ62956-002
Matrix:
Aqueous
Batch: 62956
Prep Method:
625.1
Analytical Method: 625.1
Prep Date:
08/10/2020 1715
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L)
Q Dil
% Rec
Limit
Analysis Date
Acenaphthene
20
12
1
59
47-145
08/14/2020 1417
Acenaphthylene
20
12
1
58
33-145
08/14/2020 1417
Anthracene
20
12
1
58
27-133
08/14/2020 1417
Benzo(a)anthracene
20
12
1
62
33-143
08/14/2020 1417
Benzo(a)pyrene
20
11
1
56
17-163
08/14/2020 1417
Benzo(b)fluoranthene
20
12
1
62
24-159
08/14/2020 1417
Benzo(g,h,i)perylene
20
13
1
65
1-219
08/14/2020 1417
Benzo(k)fluoranthene
20
12
1
61
11-162
08/14/2020 1417
Benzyl alcohol
20
7.7
1
39
30-130
08/14/2020 1417
4-Bromophenyl phenyl ether
20
12
1
62
53-127
08/14/2020 1417
Butyl benzyl phthalate
20
12
1
62
1-152
08/14/2020 1417
bis (2-Chloro-1-methylethyl) ether
20
11
1
57
36-166
08/14/2020 1417
4-Chloro-3-methyl phenol
20
13
1
64
22-147
08/14/2020 1417
bis(2-Chloroethoxy)methane
20
12
1
58
33-184
08/14/2020 1417
bis(2-Chloroethyl)ether
20
14
1
68
12-158
08/14/2020 1417
2-Chloronaphthalene
20
12
N 1
58
60-120
08/14/2020 1417
2-Chlorophenol
20
11
1
57
23-134
08/14/2020 1417
4-Chlorophenyl phenyl ether
20
13
1
66
25-158
08/14/2020 1417
Chrysene
20
13
1
63
17-168
08/14/2020 1417
Dibenzo(a,h)anth race ne
20
14
1
68
1-227
08/14/2020 1417
Dibenzofuran
20
12
1
61
48-118
08/14/2020 1417
3,3'-Dichlorobenzidine
20
1.1
1
5.6
1-262
08/14/2020 1417
2,4-Dichlorophenol
20
12
1
61
39-135
08/14/2020 1417
Diethylphthalate
20
14
1
68
1-120
08/14/2020 1417
Dimethyl phthalate
20
12
1
62
1-120
08/14/2020 1417
2,4-Dimethylphenol
20
18
1
90
32-120
08/14/2020 1417
Di-n-butyl phthalate
20
12
1
60
1-120
08/14/2020 1417
4,6-Dinitro-2-methyl phenol
20
14
1
71
1-181
08/14/2020 1417
2,4-Dinitrophenol
40
32
1
80
1-191
08/14/2020 1417
Di-n-octylphthalate
20
12
1
62
4-146
08/14/2020 1417
1,2-Diphenylhydrazine(as azobenzene)
20
12
1
58
1-150
08/14/2020 1417
bis(2-Ethylhexyl)phthalate
20
12
1
62
8-158
08/14/2020 1417
Fluoranthene
20
11
1
55
26-137
08/14/2020 1417
Fluorene
20
12
1
61
59-121
08/14/2020 1417
Hexachlorobenzene
20
12
1
61
1-152
08/14/2020 1417
Hexachlorobutadiene
20
12
1
62
24-120
08/14/2020 1417
Hexachlorocyclopentadiene
100
41
1
41
1-150
08/14/2020 1417
Hexachloroethane
20
12
1
62
40-120
08/14/2020 1417
Indeno(1,2,3-c,d)pyrene
20
12
1
59
1-171
08/14/2020 1417
Isophorone
20
15
1
74
21-196
08/14/2020 1417
1-Methyl naphthalene
20
12
1
62
42-126
08/14/2020 1417
2-Methyl naphthalene
20
12
1
60
40-132
08/14/2020 1417
2-Methylphenol
20
14
1
72
30-130
08/14/2020 1417
3+4-Methylphenol
20
15
1
74
30-130
08/14/2020 1417
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 33 of 49
Semivolatile Organic Compounds by GC/MS - LCS
Sample ID: VQ62956-002
Matrix:
Aqueous
Batch: 62956
Prep Method:
625.1
Analytical Method: 625.1
Prep Date:
08/10/2020 1715
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L) Q
Dil
% Rec
Limit
Analysis Date
Naphthalene
20
11
1
56
21-133
08/14/20201417
Nitrobenzene
20
15
1
76
35-180
08/14/20201417
2-Nitrophenol
20
14
1
69
29-182
08/14/20201417
4-Nitrophenol
40
31
1
78
1-132
08/14/20201417
N-Nitrosodi-n-propylamine
20
16
1
80
1-230
08/14/20201417
N-Nitrosodiphenylamine (Diphenylamine) 20
6.8
1
34
1-150
08/14/2020 1417
Pentachlorophenol
40
25
1
61
14-176
08/14/20201417
Phenanthrene
20
11
1
57
54-120
08/14/20201417
Phenol
20
11
1
55
5-120
08/14/20201417
Pyrene
20
12
1
60
52-120
08/14/20201417
1,2,4-Trichlorobenzene
20
11
1
56
44-142
08/14/20201417
2,4,6-Trichlorophenol
20
13
1
66
37-144
08/14/20201417
Acceptance
Surrogate
0
Q /o Rec
Limit
2-Fluorobiphenyl
59
37-129
2-Fluorophenol
36
24-127
Nitrobenzene-d5
71
38-127
Phenol-d5
57
28-128
Terphenyl-d 14
60
10-148
2,4,6-Tribromophenol
68
41-144
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 34 of 49
MADEP EPH (aliphatics) - MB
Sample ID: VQ63242-001 Matrix: Aqueous
Batch: 63242 Prep Method: MADEP-EPH-04
Analytical Method: MADEP-EPH-04 Prep Date: 08/12/2020 1505
Parameter Result Q Dil LOQ DL Units Analysis Date
C9 - C18 Aliphatics ND 1 100 100 ug/L 08/14/2020 1546
C19 - C36 Aliphatics ND 1 100 100 ug/L 08/14/2020 1546
Acceptance
Surrogate Q % Rec Limit
1-Chloro-octadecane (aliphatic) 45 40-140
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 35 of 49
MADEP EPH (aliphatics) - LCS
Sample ID: VQ63242-002
Matrix:
Aqueous
Batch: 63242
Prep Method:
MADEP-EPH-04
Analytical Method: MADEP-EPH-04
Prep Date:
08/12/2020 1505
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L)
Q Dil
% Rec
Limit Analysis Date
C9 - C18 Aliphatics
300
150
1
50
40-140 08/14/2020 1616
C19 - C36 Aliphatics
400
290
1
74
40-140 08/14/2020 1616
Acceptance
Surrogate Q % Rec Limit
1-Chloro-octadecane (aliphatic) 54 40-140
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 36 of 49
MADEP EPH (aliphatics) - LCSD
Sample ID: VQ63242-003
Matrix:
Aqueous
Batch: 63242
Prep Method:
MADEP-EPH-04
Analytical Method: MADEP-EPH-04
Prep Date:
08/12/2020 1505
Spike
Amount
Result
% Rec
% RPD
Parameter
(ug/L)
(ug/L) Q
Dil % Rec
% RPD Limit
Limit Analysis Date
C9 - C18 Aliphatics
300
140
1 47
6.7 40-140
25 08/14/2020 1647
C19 - C36 Aliphatics
400
290
1 71
2.9 40-140
25 08/14/2020 1647
Acceptance
Surrogate Q % Rec Limit
1-Chloro-octadecane (aliphatic) 42 40-140
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 37 of 49
MADEP EPH (aromatics) - MB
Sample ID: VQ63243-001 Matrix: Aqueous
Batch: 63243 Prep Method: MADEP-EPH-04
Analytical Method: MADEP-EPH-04 Prep Date: 08/12/2020 1505
Parameter Result Q Dil LOQ DL Units Analysis Date
C11 - C22 Aromatics ND 1 100 100 ug/L 08/14/2020 1849
Acceptance
Surrogate Q % Rec Limit
o - Terphenyl (aromatic) 67 40-140
2-Fluorobiphenyl (fractionation 1) 72 40-140
2-Bromonaphthalene (fractionation 2) 74 40-140
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 38 of 49
MADEP EPH (aromatics) - LCS
Sample ID: VQ63243-002
Matrix:
Aqueous
Batch: 63243
Prep Method:
MADEP-EPH-04
Analytical Method: MADEP-EPH-04
Prep Date:
08/12/2020 1505
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L) Q
Dil
% Rec Limit Analysis Date
C11 - C22 Aromatics
850
500
1
59 40-140 08/14/2020 1920
Surrogate
Q % Rec
Acceptance
Limit
o - Terphenyl (aromatic) 73 40-140
2-Fluorobiphenyl (fractionation 1) 77 40-140
2-Bromonaphthalene (fractionation 2) 80 40-140
LOQ = Limit of Quantitation
DL = Detection Limit
ND = Not detected at or above the DL N = Recovery is out of criteria
J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 39 of 49
MADEP EPH (aromatics) - LCSD
Sample ID: VQ63243-003
Matrix:
Aqueous
Batch: 63243
Prep Method:
MADEP-EPH-04
Analytical Method: MADEP-EPH-04
Prep Date:
08/12/2020 1505
Spike
Amount
Result
% Rec % RPD
Parameter
(ug/L)
(ug/L) Q Dil % Rec
% RPD Limit Limit Analysis Date
C11 - C22 Aromatics
850
570 1 66
11 40-140 25 08/14/2020 1950
Acceptance
Surrogate Q % Rec Limit
o - Terphenyl (aromatic) 79 40-140
2-Fluorobiphenyl (fractionation 1) 87 40-140
2-Bromonaphthalene (fractionation 2) 89 40-140
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 40 of 49
MADEP VPH (aliphatics) - MB
Sample ID: VQ63321-001 Matrix: Aqueous
Batch: 63321 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Parameter Result Q Dil LOQ DL Units Analysis Date
C5 - C8 Aliphatics ND 1 75 15 ug/L 08/12/2020 2229
C9 - C12 Aliphatics ND 1 75 15 ug/L 08/12/2020 2229
Acceptance
Surrogate Q % Rec Limit
2,5-Dibromotoluene (FID) 80 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 41 of 49
MADEP VPH (aliphatics) - LCS
Sample ID: VQ63321-002
Matrix: Aqueous
Batch: 63321
Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Spike
Amount
Result
% Rec
Parameter
(ug/L)
(ug/L)
Q Dil % Rec
Limit Analysis Date
C5 - C8 Aliphatics
150
130
1 88
70-130 08/12/2020 2103
C9 - C12 Aliphatics
180
140
1 83
70-130 08/12/2020 2103
Acceptance
Surrogate Q % Rec Limit
2,5-Dibromotoluene (FID) 94 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 42 of 49
MADEP VPH (aliphatics) - LCSD
Sample ID: VQ63321-003
Matrix: Aqueous
Batch: 63321
Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Spike
Amount
Result
% Rec
% RPD
Parameter
(ug/L)
(ug/L) Q
Dil % Rec % RPD
Limit
Limit Analysis Date
C5 - C8 Aliphatics
150
130
1 86 2.3
70-130
25 08/12/2020 2200
C9 - C12 Aliphatics
180
150
1 85 2.4
70-130
25 08/12/2020 2200
Acceptance
Surrogate Q % Rec Limit
2,5-Dibromotoluene (FID) 90 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 43 of 49
MADEP VPH (aromatics) - MB
Sample ID: VQ63322-001 Matrix: Aqueous
Batch: 63322 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Parameter Result Q Dil LOQ DL Units Analysis Date
C9 - C10 Aromatics ND 1 25 5.0 ug/L 08/12/2020 2229
Acceptance
Surrogate Q % Rec Limit
2,5-Dibromotoluene (PID) 79 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 44 of 49
MADEP VPH (aromatics) - LCS
Sample ID: VQ63322-002 Matrix: Aqueous
Batch: 63322 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Spike
Amount Result % Rec
Parameter (ug/L) (ug/L) Q Dil % Rec Limit Analysis Date
C9 - C10 Aromatics 25 23 1 90 70-130 08/12/2020 2103
Acceptance
Surrogate Q % Rec Limit
2,5-Dibromotoluene (PID) 94 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 45 of 49
MADEP VPH (aromatics) - LCSD
Sample ID: VQ63322-003 Matrix: Aqueous
Batch: 63322 Prep Method: VPH
Analytical Method: MADEP-VPH-18-2.1
Spike
Amount Result % Rec % RPD
Parameter (ug/L) (ug/L) Q Dil % Rec % RPD Limit Limit Analysis Date
C9 - C10 Aromatics 25 22 1 88 2.2 70-130 25 08/12/2020 2200
Acceptance
Surrogate Q % Rec Limit
2,5-Dibromotoluene (PID) 89 70-130
LOQ = Limit of Quantitation ND = Not detected at or above the DL N = Recovery is out of criteria
DL = Detection Limit J = Estimated result < LOQ and > DL P = The RPD between two GC columns exceeds 40 %
+ = RPD is out of criteria
Note: Calculations are performed before rounding to avoid round -off errors in calculated results
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 46 of 49
Chain of Custody
and
Miscellaneous Documents
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 47 of 49
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kiethod of cool
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tu-e upon reeeilst f T>ifived Gol't'ccted) teMperMture upon ro6drt Ngolid Snap -Cup ID- 21�-1342
NA f MA OC NA' INA mC NA _{l']A ,C
peramurc 13lank ❑Against Boltlex IR Gua fD: 5 ° IR Curl Con-exlirsn Facmr 0 °C
nt:71 Vez ice ❑Ice Packs ❑ y ke ❑ for e '
ND
O NA
3, ]f lt't11p,^,rfJ4ur�oFratycaalcrcx�.c:.d:.d 6.4'C;- �w'a.� 1'rojeat i�`anager Notili:c'' '
PM was NiAifre{l by: phone? ::mslil l r;Lcr..tn.fa , (CirCl on ). 1
❑ `des
❑ N
1Z HA
4. is Cht C4i �'n �i3i; cottricr's packing slip attached to this Corn,?
0 Yes
El N5,
proper cLlx'rr�y �,nooCrfures {rc+l�ing4ished ieoeived} falEawad7 j
LEY e
N7
71�erc
6. WeFes'aniplEII� 118kd LIIL t1L� Co C
O Yes
❑ M
7, Were sample IDs ]isbad 4ai rill s& nplC Coartainecs°
❑ Ycs
❑ M
, Was Coll.=1011 date & time Iit;LNI On ahtC CSC:?'
0 Yes
❑ N
9, War, colloctia5n date k tire} llsh--d un all ."wo I.aontnurers?
® Yes
❑ N
3
10. Mel. all eontainer ;ahol intnrinalion (ID, date, tbo) agee with Me WC?
vjyesl
❑ M
11, Wary trots to be Led lisieL: un LEre COC:71
❑ Yes
Yes
ON)
❑ N
I?- Did 0i mmplu t=ivv in the pml:er container€ .far each tee t wkdAor in goo.1 condition
(unbroker� 1-ds axe elc.) %
13, Was adQquzw sample Yalturno pvttilelr Ee
Yes
N
1 114.
W'ctr alisampies received within `li tha holdirgtime. or 49 hrnlrs_ whic&everminer, first?
15, Wm-e my salnples coirnirers misfinVexcesc (circle tole) sumplm Not lwcd on
Yts.
0 M
1
❑ Ycsl
ONj
U NA
16. For VIA and RSK-17r} 5 arrlplrs, w um bubbl present > )Pea size' ('W ce 6Fnm in diameter)
in any afthe VOA vials?
❑ Yes i
7
NA
17. Wm- all DF Ohnetalenwriera =tiplms rrtxiv'L=4 A N PH of c 27
❑ Yes;'
❑ N
0 NA
1 S- VY ai- all cyanide samplrs T=civcd at a pH '> I and sullhid a sarn les raceivad at a plA > 9?
0 Iti
O NA
19- weire all applicable NJ4/1`KN Ic}�ni ee p ono r: ,- u.5t ) sainp es tree of residual
chlogino°
❑Yes
❑ T-
}I
20. WCM. trli¢ut rornarkSiraauassts (i-e. reyursterl di�uLionS, M.SMSD d(niglalions, 0i;...)
correctly tYyruscribed fray r e CGO i_sto the LXr»m�riC m"iwi is LIMS?
❑ Ye
T
a
2], 1°va the. saute riumbe 1is1W rm the znnta,ini4T1abc17If yw, Qucu4 NA
sample PFC5P7
:it10Il [RQnst bB C071}lEt�� lil' �.tt1r Saril}�le(s} iLFL'Uf:�i.'i,l}' pr4s�rv+cd raF with heucl�aave.�
Sample(s) NA
'n sample r,mei
Time of pMery
were ivM incorrectly pseseived and were s4MIM ucC rai'q'y
lug ,mith NA ral, E% `nimle or:e+ M21; 34, RN103, HC1, Na013 ii-lug SR ? NA
ricn NA - If more tkao 070 preservative is needed, Please hate in die cot .rnent5 below.
SaMplc(S) NA
were
-leiym with lAbble€ >6lnm in dia,neteI-.
ITftC
Samples(s) MA
adjusted accord
I y'crc >e iv4d witl;ith
if wTh souiwn thicsulfaw (Na#8t )
> 0.5 ir1gL ([! I {) is Ro j arid .r cr L:
She�1y II}. v
,pin sa,ilple receiv�ii
Sl�l+a.rcode lab
lrly
Is applied}': h�11,H7
I}air;: SJ��7,7
Pace Analytical Services, LLC (formerly Shealy Environmental Services, Inc.)
106 Vantage Point Drive West Columbia, SC 29172 (803) 791-9700 Fax (803) 791-9111 www.pacelabs.com
Page 49 of 49
Way poi nt .
ANALYTICAL
Colonial Pipeline Company
John Culbreath
PO Box 87
Charlotte, NC 28130
NC Certification No. 402
NC Drinking Water Cert No. 37735
SC Certification No. 99012
Project: Kannapolis
Project No.: October DW 2020
Lab Submittal Date: 10/16/2020
Work Order: 0100228
Case Narrative
10/21/20 15:12
This data package contains the analytical results for the project identified above and includes a Case Narrative, Sample
Results and Chain of Custody. Unless otherwise noted, all samples were received in acceptable condition and processed
according to the referenced methods.
Data qualifiers are flagged individually on each sample. A key reference for the data qualifiers appears at the end of this case
narrative.
Please call if you have any questions relating to this analytical report.
Respectfully,
WAYPOINT ANALYTICAL
Terri W. Cole
Project Manager
Data Qualifiers Key Reference:
BRL Below Reporting Limit
MDL Method Detection Limit
RPD Relative Percent Difference
* Results reported to the reporting limit. All other results are reported to the MDL with values between MDL and
reporting limit indicated with a J.
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, NC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409 Page 1 of 12
0
Waypoi nt..
ANALYTICAL
Sample Receipt Summary
10/21 /2020
Work Order: 0100228
Client Sample ID
Lab Sample ID
Matrix
Date/Time Sampled
Date/Time Received
DW-Smith 10/16/20 Lab
0100228-01
Water
10/16/20
10:50
10/16/20
14:34
DW-Cook-Influent 10/16/20 Lab
0100228-02
Water
10/16/20
11:05
10/16/20
14:34
DW-Coren-Influent 10/16/20 Lab
0100228-03
Water
10/16/20
11:00
10/16/20
14:34
DW-Goodnight-New-influent_10/16/20_Lab
0100228-04
Water
10/16/20
12:15
10/16/20
14:34
DW-Maurer-Influent 10/16/20 Lab
0100228-05
Water
10/16/20
12:55
10/16/20
14:34
DW-Kann-Station 10/16/20 Lab
0100228-06
Water
10/16/20
10:30
10/16/20
14:34
DW-Watts-New-Influent 10/16/20 Lab
0100228-07
Water
10/16/20
12:30
10/16/20
14:34
Samples were received in good condition at 4.4 degrees C unless otherwise noted.
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, NC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 2 of 12
0
Way po� nt .
ANALYTICAL
Colonial Pipeline Company
Attn: John Culbreath
PO Box 87
Charlotte, NC 28130
Project: Kannapolis
Project No.: October DW 2020
Sample Matrix: Water
Laboratory Report
10/21/2020
Client Sample ID: DW-Smith_10/16/20_Lab
Sample ID: 0100228-01
Work Order: 0100228
Time Collected: 10/16/20 10:50
Time Submitted: 10/16/20 14:34
Parameter Result Units Report MDL Dilution Method Analysis Analyst Batch
Limit Factor Date/Time ID
Volatile Organic Compounds by GC/MS
Benzene
BRL
ug/L
0.50
0.048
1
*8260D
10/19/20 15:51
JLB
POJ0349
Ethylbenzene
BRL
ug/L
0.50
0.061
1
*8260D
10/19/20 15:51
JLB
POJ0349
m,p-Xylenes
BRL
ug/L
1.0
0.12
1
*8260D
10/19/20 15:51
JLB
POJ0349
Methyl-tert-Butyl Ether
BRL
ug/L
5.0
0.042
1
*8260D
10/19/20 15:51
JLB
POJ0349
Naphthalene
BRL
ug/L
1.0
0.30
1
*8260D
10/19/20 15:51
JLB
POJ0349
o-Xylene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 15:51
JLB
POJ0349
Toluene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 15:51
JLB
POJ0349
Xylenes, total
BRL
ug/L
3.0
0.15
1
*8260D
10/19/20 15:51
JLB
POJ0349
Surrogate
Recovery Control Limits
4-Bromofluorobenzene 96 % 80-124
Dibromofluoromethane 100 % 75-129
Toluene-d8 101 % 77-123
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, INC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 3 of 12
0
Way poi nt.
ANALYTICAL
Colonial Pipeline Company
Attn: John Culbreath
PO Box 87
Charlotte, NC 28130
Project: Kannapolis
Project No.: October DW 2020
Sample Matrix: Water
Laboratory Report
10/21/2020
Client Sample ID: DW-cook-Influent_10/16/2o_Lab
Sample ID: 0100228-02
Work Order: 0100228
Time Collected: 10/16/20 11:05
Time Submitted: 10/16/20 14:34
Parameter Result Units Report MDL Dilution Method Analysis Analyst Batch
Limit Factor Date/Time ID
Volatile Organic Compounds by GUMS
Benzene
BRL
ug/L
0.50
0.048
1
*8260D
10/19/20 16:18
JLB
POJ0349
Ethylbenzene
BRL
ug/L
0.50
0.061
1
*8260D
10/19/20 16:18
JLB
POJ0349
m,p-Xylenes
BRL
ug/L
1.0
0.12
1
*8260D
10/19/20 16:18
JLB
POJ0349
Methyl-tert-Butyl Ether
BRL
ug/L
5.0
0.042
1
*8260D
10/19/20 16:18
JLB
POJ0349
Naphthalene
BRL
ug/L
1.0
0.30
1
*8260D
10/19/20 16:18
JLB
POJ0349
o-Xylene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 16:18
JLB
POJ0349
Toluene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 16:18
JLB
POJ0349
Xylenes, total
BRL
ug/L
3.0
0.15
1
*8260D
10/19/20 16:18
JLB
POJ0349
Surrogate
Recovery Control Limits
4-Bromofluorobenzene 97 % 80-124
Dibromofluoromethane 99 % 75-129
Toluene-d8 100 % 77-123
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, INC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 4 of 12
0
Way poi nt.
ANALYTICAL
Colonial Pipeline Company
Attn: John Culbreath
PO Box 87
Charlotte, NC 28130
Project: Kannapolis
Project No.: October DW 2020
Sample Matrix: Water
Laboratory Report
10/21/2020
Client Sample ID: DW-Coren-Influent_10/16/20_Lab
Sample ID: 0100228-03
Work Order: 0100228
Time Collected: 10/16/20 11:00
Time Submitted: 10/16/20 14:34
Parameter Result Units Report MDL Dilution Method Analysis Analyst Batch
Limit Factor Date/Time ID
Volatile Organic Compounds by GUMS
Benzene
BRL
ug/L
0.50
0.048
1
*8260D
10/19/20 16:46
JLB
POJ0349
Ethylbenzene
BRL
ug/L
0.50
0.061
1
*8260D
10/19/20 16:46
JLB
POJ0349
m,p-Xylenes
BRL
ug/L
1.0
0.12
1
*8260D
10/19/20 16:46
JLB
POJ0349
Methyl-tert-Butyl Ether
BRL
ug/L
5.0
0.042
1
*8260D
10/19/20 16:46
JLB
POJ0349
Naphthalene
BRL
ug/L
1.0
0.30
1
*8260D
10/19/20 16:46
JLB
POJ0349
o-Xylene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 16:46
JLB
POJ0349
Toluene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 16:46
JLB
POJ0349
Xylenes, total
BRL
ug/L
3.0
0.15
1
*8260D
10/19/20 16:46
JLB
POJ0349
Surrogate
Recovery Control Limits
4-Bromofluorobenzene 97 % 80-124
Dibromofluoromethane 98 % 75-129
Toluene-d8 101 % 77-123
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, INC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 5 of 12
0
Way poi nt.
ANALYTICAL
Colonial Pipeline Company
Attn: John Culbreath
PO Box 87
Charlotte, NC 28130
Project: Kannapolis
Project No.: October DW 2020
Sample Matrix: Water
Laboratory Report
10/21/2020
Client Sample ID: DW-Goodnight-New-Influent_10/1
Sample ID: 0100228-04
Work Order: 0100228
Time Collected: 10/16/20 12:15
Time Submitted: 10/16/20 14:34
Parameter Result Units Report MDL Dilution Method Analysis Analyst Batch
Limit Factor Date/Time ID
Volatile Organic Compounds by GUMS
Benzene
BRL
ug/L
0.50
0.048
1
*8260D
10/19/20 17:14
JLB
POJ0349
Ethylbenzene
BRL
ug/L
0.50
0.061
1
*8260D
10/19/20 17:14
JLB
POJ0349
m,p-Xylenes
BRL
ug/L
1.0
0.12
1
*8260D
10/19/20 17:14
JLB
POJ0349
Methyl-tert-Butyl Ether
BRL
ug/L
5.0
0.042
1
*8260D
10/19/20 17:14
JLB
POJ0349
Naphthalene
BRL
ug/L
1.0
0.30
1
*8260D
10/19/20 17:14
JLB
POJ0349
o-Xylene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 17:14
JLB
POJ0349
Toluene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 17:14
JLB
POJ0349
Xylenes, total
BRL
ug/L
3.0
0.15
1
*8260D
10/19/20 17:14
JLB
POJ0349
Surrogate
Recovery Control Limits
4-Bromofluorobenzene 96 % 80-124
Dibromofluoromethane 100 % 75-129
Toluene-d8 101 % 77-123
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, INC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 6 of 12
0
Way poi nt.
ANALYTICAL
Colonial Pipeline Company
Attn: John Culbreath
PO Box 87
Charlotte, NC 28130
Project: Kannapolis
Project No.: October DW 2020
Sample Matrix: Water
Laboratory Report
10/21/2020
Client Sample ID: DW-Maurer-Influent_10/16/20_La
Sample ID: 0100228-05
Work Order: 0100228
Time Collected: 10/16/20 12:55
Time Submitted: 10/16/20 14:34
Parameter Result Units Report MDL Dilution Method Analysis Analyst Batch
Limit Factor Date/Time ID
Volatile Organic Compounds by GUMS
Benzene
BRL
ug/L
0.50
0.048
1
*8260D
10/19/20 17:42
JLB
POJ0349
Ethylbenzene
BRL
ug/L
0.50
0.061
1
*8260D
10/19/20 17:42
JLB
POJ0349
m,p-Xylenes
BRL
ug/L
1.0
0.12
1
*8260D
10/19/20 17:42
JLB
POJ0349
Methyl-tert-Butyl Ether
BRL
ug/L
5.0
0.042
1
*8260D
10/19/20 17:42
JLB
POJ0349
Naphthalene
BRL
ug/L
1.0
0.30
1
*8260D
10/19/20 17:42
JLB
POJ0349
o-Xylene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 17:42
JLB
POJ0349
Toluene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 17:42
JLB
POJ0349
Xylenes, total
BRL
ug/L
3.0
0.15
1
*8260D
10/19/20 17:42
JLB
POJ0349
Surrogate
Recovery Control Limits
4-Bromofluorobenzene 94 % 80-124
Dibromofluoromethane 98 % 75-129
Toluene-d8 101 % 77-123
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, INC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 7 of 12
0
Way poi nt.
ANALYTICAL
Colonial Pipeline Company
Attn: John Culbreath
PO Box 87
Charlotte, NC 28130
Project: Kannapolis
Project No.: October DW 2020
Sample Matrix: Water
Laboratory Report
10/21/2020
Client Sample ID: DW-Kann-Station_10/16/20_Lab
Sample ID: 0100228-06
Work Order: 0100228
Time Collected: 10/16/20 10:30
Time Submitted: 10/16/20 14:34
Parameter Result Units Report MDL Dilution Method Analysis Analyst Batch
Limit Factor Date/Time ID
Volatile Organic Compounds by GUMS
Benzene
BRL
ug/L
0.50
0.048
1
*8260D
10/19/20 18:10
JLB
POJ0349
Ethylbenzene
BRL
ug/L
0.50
0.061
1
*8260D
10/19/20 18:10
JLB
POJ0349
m,p-Xylenes
BRL
ug/L
1.0
0.12
1
*8260D
10/19/20 18:10
JLB
POJ0349
Methyl-tert-Butyl Ether
BRL
ug/L
5.0
0.042
1
*8260D
10/19/20 18:10
JLB
POJ0349
Naphthalene
BRL
ug/L
1.0
0.30
1
*8260D
10/19/20 18:10
JLB
POJ0349
o-Xylene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 18:10
JLB
POJ0349
Toluene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 18:10
JLB
POJ0349
Xylenes, total
BRL
ug/L
3.0
0.15
1
*8260D
10/19/20 18:10
JLB
POJ0349
Surrogate
Recovery Control Limits
4-Bromofluorobenzene 96 % 80-124
Dibromofluoromethane 99 % 75-129
Toluene-d8 102 % 77-123
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, INC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 8 of 12
0
Way poi nt.
ANALYTICAL
Colonial Pipeline Company
Attn: John Culbreath
PO Box 87
Charlotte, NC 28130
Project: Kannapolis
Project No.: October DW 2020
Sample Matrix: Water
Laboratory Report
10/21/2020
Client Sample ID: DW-Watts-New-Influent_10/16/20
Sample ID: 0100228-07
Work Order: 0100228
Time Collected: 10/16/20 12:30
Time Submitted: 10/16/20 14:34
Parameter Result Units Report MDL Dilution Method Analysis Analyst Batch
Limit Factor Date/Time ID
Volatile Organic Compounds by GUMS
Benzene
BRL
ug/L
0.50
0.048
1
*8260D
10/19/20 18:37
JLB
POJ0349
Ethylbenzene
BRL
ug/L
0.50
0.061
1
*8260D
10/19/20 18:37
JLB
POJ0349
m,p-Xylenes
BRL
ug/L
1.0
0.12
1
*8260D
10/19/20 18:37
JLB
POJ0349
Methyl-tert-Butyl Ether
BRL
ug/L
5.0
0.042
1
*8260D
10/19/20 18:37
JLB
POJ0349
Naphthalene
BRL
ug/L
1.0
0.30
1
*8260D
10/19/20 18:37
JLB
POJ0349
o-Xylene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 18:37
JLB
POJ0349
Toluene
BRL
ug/L
0.50
0.044
1
*8260D
10/19/20 18:37
JLB
POJ0349
Xylenes, total
BRL
ug/L
3.0
0.15
1
*8260D
10/19/20 18:37
JLB
POJ0349
Surrogate
Recovery Control Limits
4-Bromofluorobenzene 97 % 80-124
Dibromofluoromethane 98 % 75-129
Toluene-d8 102 % 77-123
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, INC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 9 of 12
(2)
Way po Int
ANALYTICAL
Colonial Pipeline Company Project: Kannapolis
Attn: John Culbreath
PO Box 87 Project No: October DW 2020
Charlotte, NC 28130
Volatile Organic Compounds by GC/MS - Quality Control
Level II QC Report
10/21/20
Work Order: 0100228
Time Submitted: 10/16/2020 2:34:OOPM
Reporting Spike Source %REC RPD
Analyte Result Limit Units Level Result %REC Limits RPD Limit Notes
Batch POJ0349 - 5030B
Blank (POJ0349-BLK1)
Prepared & Analyzed: 10/19/20
Benzene
BRL
0.50
ug/L
Ethylbenzene
BRL
0.50
ug/L
m,p-Xylenes
BRL
1.0
ug/L
Methyl-tert-Butyl Ether
BRL
5.0
ug/L
Naphthalene
BRL
1.0
ug/L
o-Xylene
BRL
0.50
ug/L
Toluene
BRL
0.50
ug/L
Xylenes, total
BRL
3.0
ug/L
Heptane
0.00
ug/L
Surrogate:4-Bromofluorobenzene
48.5
ug/L
50.00
97
80-124
Surrogate: Dibromofluoromethane
50.0
ug/L
50.00
100
75-129
Surrogate: Toluene-d8
50.8
ug/L
50.00
102
77-123
LCS (POJ0349-BS1)
Prepared &Analyzed: 10/19/20
Benzene
20.6
0.50
ug/L
20.00
103
77-128
Ethylbenzene
20.7
0.50
ug/L
20.00
103
80-127
m,p-Xylenes
44.0
1.0
ug/L
40.00
110
77-133
Methyl-tert-Butyl Ether
21.0
5.0
ug/L
20.00
105
68-135
Naphthalene
20.0
1.0
ug/L
20.00
100
64-136
o-Xylene
20.9
0.50
ug/L
20.00
105
78-128
Toluene
20.7
0.50
ug/L
20.00
103
76-131
Xylenes, total
65.0
3.0
ug/L
60.00
108
77-133
Surrogate:4-Bromofluorobenzene
48.1
ug/L
50.00
96
80-124
Surrogate: Dibromofluoromethane
49.3
ug/L
50.00
99
75-129
Surrogate: Toluene-d8
50.6
ug/L
50.00
101
77-123
Matrix Spike (POJ0349-MS1)
Source: 0100228-01
Prepared & Analyzed: 10/19/20
Benzene
202
5.0
ug/L
200.0 BRL
101
73-131
Ethylbenzene
202
5.0
ug/L
200.0 BRL
101
78-130
m,p-Xylenes
432
10
ug/L
400.0 BRL
108
66-144
Methyl-tert-Butyl Ether
206
50
ug/L
200.0 BRL
103
71-133
Naphthalene
169
10
ug/L
200.0 BRL
84
63-134
o-Xylene
200
5.0
ug/L
200.0 BRL
100
75-131
Toluene
204
5.0
ug/L
200.0 BRL
102
72-135
Xylenes, total
632
30
ug/L
600.0 BRL
105
66-144
Surrogate:4-Bromofluorobenzene
48.2
ug/L
50.00
96
80-124
Surrogate: Dibromofluoromethane
49.6
ug/L
50.00
99
75-129
Surrogate: Toluene-d8
50.1
ug/L
50.00
100
77-123
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, NC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 10 of 12
1 0
Waypoint.
ANALYTICAL
Colonial Pipeline Company Project: Kannapolis
Attn: John Culbreath
PO Box 87 Project No: October DW 2020
Charlotte, NC 28130
Volatile Organic Compounds by GC/MS - Quality Control
Level II QC Report
10/21 /20
Work Order: 0100228
Time Submitted: 10/16/2020 2:34:OOPM
Reporting Spike Source %REC RPD
Analyte Result Limit Units Level Result %REC Limits RPD Limit Notes
Batch POJ0349 - 5030B
Matrix Spike Dup (POJ0349-MSD1)
Source: 0100228-01
Prepared & Analyzed: 10/19/20
Benzene
200
5.0
ug/L
200.0
BRL
100
73-131
1
17
Ethylbenzene
199
5.0
ug/L
200.0
BRL
100
78-130
1
18
m,p-Xylenes
420
10
ug/L
400.0
BRL
105
66-144
3
19
Methyl-tert-Butyl Ether
205
50
ug/L
200.0
BRL
102
71-133
0.5
19
Naphthalene
183
10
ug/L
200.0
BRL
91
63-134
8
32
o-Xylene
201
5.0
ug/L
200.0
BRL
100
75-131
0.3
20
Toluene
200
5.0
ug/L
200.0
BRL
100
72-135
2
18
Xylenes, total
621
30
ug/L
600.0
BRL
103
66-144
2
20
Surrogate:4-Bromofluorobenzene
48.2
ug/L
50.00
96
80-124
Surrogate: Dibromofluoromethane
49.5
ug/L
50.00
99
75-129
Surrogate: Toluene-d8
50.2
ug/L
50.00
100
77-123
Sample Extraction Data
Prep Method: 5030B
Lab Number Batch Initial Final Daterrime
0100228-01
POJ0349
10
mL
10
mL
10/19/20
10:00
0100228-02
POJ0349
10
mL
10
mL
10/19/20
10:00
0100228-03
POJ0349
10
mL
10
mL
10/19/20
10:00
0100228-04
POJ0349
10
mL
10
mL
10/19/20
10:00
0100228-05
POJ0349
10
mL
10
mL
10/19/20
10:00
0100228-06
POJ0349
10
mL
10
mL
10/19/20
10:00
0100228-07
POJ0349
10
mL
10
mL
10/19/20
10:00
This report should not be reproduced, except in its entirety, without the written consent of Waypoint Analytical.
449 Springbrook Road - P.O. Box 240543 - Charlotte, NC 28224-0543
Phone: 704/529-6364 - Toll Free Number: 1-800/529-6364 - Fax: 704/525-0409
Page 11 of 12
Chain Of Custody #: KAN-J-176 Laboratory Account#:
Consultant Contact:: '
Site Location:
Kannapolis
Consulting Firm:.
Project, Name:-
October DW 2020
Address:
Facility/Site.113M
0820
City, State, Zip: ,
Colonial• Pipeline PM:
John.Culbreath #1533
Phone:
Cost Center/AFE#:
561.8
Faz: .
Re ques#ed: Analysis ;Method .
Lab Billing Control #:'
:' - : '
Pros.
Soil
ample Collection
-
- -
Depth -
Date and. Time .
Test/
. .. -
9y :
Meth
Method
O
^:
.Samle .
Field Sample ID:. _ Comment'.. .
Type:
Date:...'
Time:...
Matrix:.
DW-Smith:10/16/20_Lab . _ -
3 ..
Lab
0 ..
0 .
10/16/2020
..10:50 AM
Groundwater:
R
Method00�
DW-Cook-Influent 10/16/20_La
'.
3-
Lab
0 .
:0 :.
10/16/2020.
.
11:05 AM
Groundwater
..
DW-Coren-Influent :10/16/20- L
-
-
3.
'Lab
0:
0
10/11i/2020
11:00 AM
Groundwater
V
-
DW=Goodnight-New-Influent-10
- =
3.
Lab
0
0 .
10/16/2020
.12:15PMGroundwater
DO
DW-Maurer-Influent 10/16/20_
3.
Lab
0
0
10/16/2020
12:55 PM
Groundwater
0�
DW-Kann-Station_10/16/20 La.
3-
Lab .':'0
0
10/16/2020
- .10:30 AM
Groundwater
DW-Watts-New-Influent_10/16/.
:.
3
-Lab .
0
0
10/16/2020
- •. 1:3O
Groundwater -
um Around Time: Special Instructions:
Special Detection Limits:
A Standard TAT
ush'TAT.(Fax due.Close•of Business CST �•
ue Date: %� �2/. ?�2C.. ; • .
Relinquished by: Date: Time: Received : :Date:. ' Time:
Custod
Sampler.'.- John Culbreath
Record :.. , ...
Laboratory:
Page 12 of 2
in 1
ti_u
APPENDIX C
CONCENTRATION TIME TREND SERIES GRAPH - MW-13
�1
APEX
200
180
160
140
120
i
N
L
a 100
E
m
L
p
U
80
C
Ci
0
60
L
r
U
C
40
a,
c
a,
N
C
m 20
u
MW-13 Benzene Concentration Fluctuations with Time
I� 00 W M M O O " M N N M M 0 0 W W 0 a " n M M M Q1 O O �--� �--� N M M LI1 Lf1 Lf1 lD lD I� n 00 00 Ql Ql O O
O O O O O O O O O �--I � � r-I � � � � � � � � � � r-I � � � � � N N
Ql Ol \ Ql Ql O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O O
N N N N N fV N N N N N N N N N N fV fV N N N N N N N N N fV fV N N N N N N N N N fV A
O NO I� Ql n l0 M LD I, 00 M 00 Ol M M I� N lD O " Lf1 00 rl O N l!'1 00 M Ol Ol Lf1 M 00 lD Ql r Lli rl lD Lfi 00 00 lD
N N �--I r-I r-I r-I N .--I N N i--I r-I r-I r-I N �--I N .--I N y N N i--I N \ �--I r-I \ .--I \ N i--I N N A \ 11 1 \ \ i--I \
00 \ 00
O N 0 N 00 N 00 N 00 N 00 N 00 N 00 N 00 N 00 N 00 N 00 N 00 00 N N 00 N 00 N 00 rl N 00 00 00 N N
c-I
Time Benzene
Beverly, Trudy
From: Michael Bator <mbator@vertexeng.com>
Sent: Tuesday, December 1, 2020 7:32 AM
To: Beverly, Trudy
Subject: RE: [External] Annual Groundwater Monitoring Report, Kannapolis Booster Station
f1911NMOMernal email. Do not click links or open attachments unless you verify. Send all suspicious email as an attachment to
ort.spam@nc.&ov
Thanks!
Michael Bator, PG
SENIOR PROJECT MANAGER
O: 919.238.4370 1 C: 201.519.4085 1 VERTEXENG.COM
THE VERTEX COMPANIES, INC.
2500 GATEWAY CENTRE BLVD., STE 300
MORRISVILLE, NC 27560
From: Beverly, Trudy <trudy.beverly@ncdenr.gov>
Sent: Tuesday, December 1, 2020 6:41 AM
To: Michael Bator <mbator@vertexeng.com>
Subject: FW: [External] Annual Groundwater Monitoring Report, Kannapolis Booster Station
Good Morning Michael,
The report was submitted yesterday (see attached).
Have a great day,
Trudy
Trudy Beverly, L.G.
Hydrogeologist, Division of Waste Management
North Carolina Department of Environmental Quality
D�.
UST Section, Mooresville Regional Office
704.235.2182 (Office)
Trudv.Beverlvaa.ncdenr. cov
Email correspondence to and from this address is subject to the
North Carolina Public Records Law and may be disclosed to third parties.
Office Mailing Address:
610 East Center Avenue, Suite 301
Mooresville, NC 28115
Branch's Underground Storage Tanks Website Address: https://deg.nc.gov/about/divisions/waste-management/ust
Branch's Above Ground Storage Tanks Website Address: https://deg.nc.gov/about/divisions/waste-management/ust/ast-proeram
INTERACTIVE MAPS WITH DWM SITES AND PERMITTED FACILITIES:
httos://dea.nc. eov/about/divisions/waste-management/waste-management-rules-data/waste-management-eis-mans
File Review Procedures:
https://deq.nc. gov/about/divisions/waste-management/ust/file-review-procedures#mooresville-regional-office
ONLINE ACCESS TO UST SECTION DOCUMENTS (Laserfiche):
httos: //dea.nc. eov/about/divisions/waste-mana2ement/laserfiche
Document Submittal & UST File Names for Laserfiche Policies:
httys:Hfiles.nc.aov/nedeci/Waste%2OMana2ement/DWM/UST/WhatsNew/Final-Electronic-Document-Submittal-Policy.odf
htips:Hfiles.nc.gov/ncdeg/Waste%2OManagement/D WM/UST/Corrective%2OAction/UST%20file%20names%20for%2OLaserfiche.docx
From: Tom Naumann [mailto:Tom.Naumann@apexcos.com]
Sent: Monday, November 30, 2020 4:31 PM
To: Beverly, Trudy <trudy.beverly@ncdenr.gov>
Cc: Andrew Street <Andrew.Street@apexcos.com>; Morrison, Jeff <jmorrison@colpipe.com>
Subject: [External] Annual Groundwater Monitoring Report, Kannapolis Booster Station
External email. Do not click links or open attachments unless you verify. Send all suspicious email as an attachment to
report.spam@nc.gov
Ms. Trudy,
Please find the attached Annual Groundwater Monitoring Report for the Colonial Pipeline Company's Kannapolis
Booster Station, Incident Number 14414 & 91340.
Thank you.
Sincerely,
Tom Naumann
Tom Naumann
Scientist 2
Apex Companies, LLC
1071 Pemberton Hill Rd, Ste 203
Apex, NC 27502
0)919-646-1473 M)404-483-3093
Add me to your contact list!
ENR Top 30 All -Environmental Firm
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