AS-3241_28414_CA_MRP_20190807

An Equal Opportunity Employer

August 7, 2019

Certified Mail
Return Receipt Requested

Mr. Dan Murphy
North Carolina Department of Environmental Quality
Division of Waste Management, UST Section
Asheville Regional Office
2090 U.S. Highway 70
Swannanoa, North Carolina 28778

Subject: GROUNDWATER MONITORING REPORT
SPEEDWAY 7972 (FORMER WILCOHESS 353)
502 WILKESBORO BLVD. SE
LENOIR, CALDWELL COUNTY, NORTH CAROLINA
DWM INCIDENT NO. 28414
MID-ATLANTIC JOB NO. 000R1760.18

Dear Mr. Murphy:

Speedway LLC is pleased to present this report of environmental services for the Speedway 7972
(formerly WilcoHess 353) facility located at 502 Wilkesboro Boulevard SE in Lenoir, North
Carolina. This report documents the results of the groundwater monitoring and surface water
sampling activities conducted at the site in March 2019. If you have any questions, please feel
free to contact me at [phone] or Patrick Kelly with Mid-Atlantic Associates, Inc. at (980)
585-1271.

Sincerely,

SPEEDWAY LLC

Charles A. Chiara
Environmental Representative

Speedway LLC

Speedway Office
P.O. Box 1500
Springfield, OH 45501
Telephone [phone]

GROUNDWATER MONITORING REPORT
SPEEDWAY 7972 (FORMER WILCOHESS 353)
FACILITY I.D. NO.: 0-033119
502 WILKESBORO BOULEVARD SE
LENOIR, CALDWELL COUNTY, NORTH CAROLINA
INCIDENT NO. 28414

Risk Classification: Intermediate
Ranking (RRA): I-184-D

Prepared For:

Speedway LLC
500 Speedway Drive
Enon, Ohio 45323
937) 591-1283

Prepared By:

Mid-Atlantic Associates, Inc.
409 Rogers View Court
Raleigh, North Carolina 27610
[phone]

August 7, 2019

TABLE OF CONTENTS

LIST OF ACRONYMS ..................................................................................................... i

1.0 INTRODUCTION ..................................................................................................... 1

2.0 POTENTIAL RECEPTORS ..................................................................................... 1

3.0 FIELD ACTIVITIES ................................................................................................. 2
3.1 Water Level Measurements ............................................................................ 2
3.2 Monitoring Well Sample Collection .................................................................. 2
3.3 Surface Water Sample Collection ................................................................... 2

4.0 DISCUSSION OF SAMPLING RESULTS .............................................................. 2
4.1 Summary of Laboratory Analytical Results...................................................... 2
4.2 Description of Current Plume Size and Location ............................................. 3
4.3 Additional Monitoring Information .................................................................... 3
4.4 Spill Bucket Sampling Discussion ................................................................... 4

5.0 FUTURE SITE REMEDIATION ............................................................................... 4

6.0 SUMMARY, CONCLUSIONS AND RECOMMENDATIONS .................................. 5

DRAWINGS

Drawing 1.1 Topographic Site Map
Drawing 1.2 Site and Monitoring Well Location Map
Drawing 4.1 Estimated Isoconcentration Map - Benzene in Shallow Groundwater
March 25, 2019
Drawing 4.2 Estimated Isoconcentration Map – Toluene in Shallow Groundwater
March 25, 2019
Drawing 4.3 Estimated Water Table Contour Map
March 25, 2019

TABLES

Table 3.1 Monitoring Well Construction Information
Table 3.2 Historical Liquid Level Measurements
Table 4.1 Summary of Historical Groundwater Monitoring Results for Selected
Compounds
Table 4.2 Summary of Surface Water Sampling Results for Selected Compounds
Table 4.3 Elevation Comparison of the Water Table to Drainage Ditch

TABLE OF CONTENTS (CONTINUED)

APPENDICES

Appendix A Selected Historical Site Assessment Data
Appendix B Mid-Atlantic Field Procedures
Appendix C Laboratory Analytical Report and Chain-of-Custody Report

i
LIST OF ACRONYMS

2012 Guidelines Underground Storage Tank Section Guidelines for
Assessment and Corrective Action For UST
Releases, DENR, Division of Waste Management
UST Section, July 15, 2008 Version, Change 2,
Effective October 1, 2012
AFVR Aggressive Fluid-Vapor Recovery
AS Air Sparge
AST Aboveground Storage Tank

BQL Below (Laboratory Practical) Quantitation Limit
BLS Below Land Surface
BTEX Benzene, Toluene, Ethylbenzene, Xylenes

CAP Corrective Action Plan
cm Centimeter
COC Constituents of Concern
CSA Comprehensive Site Assessment

DIPE Diisopropyl Ether (also IPE: Isopropyl Ether)
DNAPL Dense Non-Aqueous Phase Liquids
DO Dissolved Oxygen
DPE Dual-Phase Extraction
DPT Direct Push Technology
DRO Diesel Range Organics
DSCA North Carolina Dry-Cleaning Solvent Act
DTW Depth to Water
DWM Division of Waste Management
DWQ Division of Water Quality

EDB Ethylene di-bromide
EPA Environmental Protection Agency
EPH Extractable Petroleum Hydrocarbons

FID Flame Ionization Detector
FT Feet

GCL Gross Contamination Level
GIS Geographic Information System
GPM Gallons Per Minute
GPS Global Positioning System
GRO Gasoline Range Organics

ID Identification
IDW Investigation Derived Waste
IGQS Interim Groundwater Quality Standards

LSA Limited Site Assessment
LUST Leaking Underground Storage Tank

m Meter
MADEP Massachusetts Department of Environmental
Protection
Mid-Atlantic Mid-Atlantic Associates, Inc.
MDL Method Detection Limit
mg/Kg Milligrams per Kilogram
mg/L Milligrams per Liter
MMP Minimum Management Practices
MMPE Mobile Multi-Phase Extraction
MNA Monitored Natural Attenuation
MSCC Maximum Soil Contaminant Concentration
MSL Mean Sea Level
MTBE Methyl tertiary butyl ether
g/Kg Micrograms per Kilogram g/L Micrograms per Liter

NA Not Analyzed
N/A Not Applicable
NC North Carolina
NCAC North Carolina Administrative Code
NCDEQ North Carolina Department of Environmental Quality
NCDOT North Carolina Department of
Transportation
NCGQS North Carolina Groundwater Quality
Standards
NCSWQS North Carolina Surface Water Quality
Standards
ND Not Detected
NM Not Measured
NORR Notice of Regulatory Requirements
NOV Notice of Violation
NS Not Sampled

ORP Oxidation-Reduction Potential
OVA Organic Vapor Analyzer

PA Prioritization Assessment
PAA Prioritization Assessment Agreement
PAH Polynuclear Aromatic Hydrocarbons
Pb Lead
PCBs Polychlorinated Biphenyls
PCE Perchloroethylene (also tetrachloroethene)
PPB Parts Per Billion
PPM Parts Per Million
PID Photo Ionization Detector
POTW Publicly Owned Treatment Works
PQL Practical Quantitation Limit
PRF Prioritization Ranking Form
PVC Polyvinyl chloride

RBCA Risk-Based Corrective Action
RCRA Resource Conservation and Recovery Act
ROI Radius of Influence

s Seconds
SAR Soil Assessment Report
SOW Scope of Work
STG Soil-to-Groundwater
SVE Soil Vapor Extraction
SVOC Semi-Volatile Organic Compound

TDHF Toxicologically Defined Hydrocarbon
Fractions
TCLP Toxicity Characteristic Leaching Procedure
TIC Tentatively Identified Compound
TOC Top of Casing
TPH Total Petroleum Hydrocarbons

UFA Ultraviolet Fluorescence Detector
US United States
USCS Unified Soil Classification System
USGS United States Geological Survey
UST Underground Storage Tank
UT Unnamed Tributary
VOC Volatile Organic Compounds
VPH Volatile Petroleum Hydrocarbons
yr Year

1.0 INTRODUCTION

The subject site is the Speedway 7972 (former WilcoHess 353) located at 502 Wilkesboro
Boulevard SE in Lenoir, North Carolina (Drawing 1.1). On October 1, 2014, Speedway LLC
acquired the site from Hess Corporation, who had previously acquired the site from
WilcoHess LLC. The site is currently in use as a convenience store and retail petroleum
dispensing facility. The facility operates three 12,000-gallon gasoline USTs, one 12,000-
gallon diesel UST, and one 10,000-gallon kerosene UST. The layout of the facility is shown
on Drawing 1.2.

Gasoline free product was historically present on the water table in monitoring wells MW-1
and MW-8, but has not been detected at the site since September 2012. The site is
currently classified as intermediate risk due to the presence of a downgradient surface
water body (UT to Lower Creek) located within 500 feet of the source area of the release.
The UT to Lower Creek is located approximately 125 feet south and hydraulically
downgradient of the source area of the release, and petroleum-related constituents have
historically been detected in surface water samples collected from this drainage feature at
concentrations exceeding the NCSWQS. The approximate surface water sampling
locations are identified on Drawing 1.2. Selected historical site assessment data is included
in Appendix A.

This report documents the results of the groundwater monitoring and surface water sampling
activities conducted at the site in March 2019. The opinions included herein are based on
our experience and information obtained during the study. This report is based on limited
observations made on the dates noted using procedures described herein. If additional
information becomes available, we request the opportunity to review the information,
reassess the potential environmental concerns, and modify our conclusions, if
appropriate.

2.0 POTENTIAL RECEPTORS

Receptor information for the site was previously documented in Mid-Atlantic’s Phase I
Limited Site Assessment Report dated November 13, 2006. A receptor survey update
was not conducted during this monitoring event. Please refer to previous reports for
detailed receptor information. As indicated, the site is currently classified as “intermediate”
risk due to the presence of a surface water body (UT to Lower Creek) located
approximately 125 feet south and hydraulically downgradient of the release area
(Drawing 1.2).

According to Classifications and Water Quality Standards Assigned to the Waters of the
Yadkin-Pee Dee River Basin, Lower Creek is classified as a Class C Water. A Class C
Water is defined as freshwaters that must be protected for secondary recreation, fishing,
aquatic life including propagation and survival, and wildlife.

Groundwater Monitoring Report August 7, 2019
Speedway 7972 (former WilcoHess 353) Page 2
Lenoir, North Carolina

3.0 FIELD ACTIVITIES

3.1 Water Level Measurements

Mid-Atlantic personnel collected groundwater level measurements from selected site
monitoring wells MW-1, MW-3, MW-8, MW-11, MW-15 and MW-16 on March 25, 2019
using an electronic water level indicator. Monitoring well construction details are provided
in Table 3.1. Groundwater level measurements were collected using the procedures
outlined in Appendix B. The results of these activities, along with historical
measurements, are summarized in Table 3.2.

3.2 Monitoring Well Sample Collection

Mid-Atlantic personnel collected groundwater samples from six selected site monitoring
wells (MW-1, MW-3, MW-8, MW-11, MW-15, and MW-16) on March 25, 2019. The sampling
event was conducted to monitor plume concentrations in the vicinity of the source area of
the release (MW-1, MW-3 and MW-8) and immediately upgradient of the receiving UT to
lower Creek (MW-11, MW-15 and MW-16). Groundwater samples were collected using the
procedures outlined in Appendix B. Samples were shipped to Pace Analytical in Mt. Juliet,
Tennessee and analyzed by the methods shown on the chain-of-custody record provided in
Appendix C.

3.3 Surface Water Sample Collection

On March 25, 2019, Mid-Atlantic personnel collected three surface water samples from
the UT to Lower Creek, located to the south and downgradient of the source area of the
release. The approximate sample locations (Stream #1, Stream #2, and Stream #3) are
shown on Drawing 1.2. Surface water samples were collected using the procedures
outlined in Appendix B. Samples were shipped to Pace Analytical in Mt. Juliet, Tennessee
and analyzed by the methods shown on the chain-of-custody record in Appendix C.

4.0 DISCUSSION OF SAMPLING RESULTS

4.1 Summary of Laboratory Analytical Results

Groundwater

The laboratory analytical report and chain-of-custody record for groundwater samples
collected in March 2019 are provided in Appendix C and summarized in Table 4.1, which
also includes a summary of historical groundwater sampling data for selected target
compounds. As summarized, the groundwater sample collected from source area
monitoring well MW-8 exhibited toluene and naphthalene concentrations in excess of ten
times the NCSWQS but below the GCLs. No other samples collected during the monitoring
event exceeded ten times the NCSWQS, including the wells located immediately upgradient
of the UT to Lower Creek (MW-11, MW-15 and MW-16).
Groundwater Monitoring Report August 7, 2019
Speedway 7972 (former WilcoHess 353) Page 3
Lenoir, North Carolina

Surface Water

The laboratory analytical report and chain-of-custody record for surface water samples
collected in March 2019 are provided in Appendix C and summarized in Table 4.2, which
also includes a summary of historical surface water sampling data for selected target
compounds. As summarized, target compounds were detected in surface water samples
Stream #1 and Stream #2 at concentrations below the NCSWQS for the March 2019
sampling event.

4.2 Description of Current Plume Size and Location

Free product has not been detected at the site since September 2012 and dissolved-
phase groundwater contaminants appear to have migrated hydraulically downgradient of
the source area of the release, in the direction of the UT to Lower Creek. The dissolved-
phase groundwater contaminant plume appears to be defined by the current monitoring well
network to the extent of ten times the NCSWQS as concentrations did not exceed ten times
the NCSWQS for samples collected from monitoring wells MW-11, MW-15 or MW-16,
located immediately up gradient of the UT to Lower Creek.

Benzene and toluene isoconcentration maps for the March 2019 sampling event are
provided as Drawings 4.1 and 4.2, respectively. When compared with the results of
previous sampling events, the overall groundwater contaminant concentrations appear to
be generally consistent with previous sampling events. An increase in benzene
concentrations was observed in the groundwater samples collected from wells MW-1
(note the lab indicated results for this sample were biased on the high side), MW-8 and
MW-15; however, the additional target compound concentrations detected in the samples
collected from these wells remained relatively consistent with previous sampling events.

Target compound concentrations for surface water samples collected from the UT to
Lower Creek have not been detected in excess of the NCSWQS since February 2013.
Based on the current available data, additional monitoring events appear to be warranted
to continue to evaluate contaminant trends associated with wells MW-1, MW-3, MW-8,
MW-11, MW-15 and MW-16 and the downgradient UT to Lower Creek.

4.3 Additional Monitoring Information

 Elevation Comparison of the Water Table to the UT to Lower Creek

The elevations of the shallow water table for three monitoring wells (MW-2, MW-11,
and MW-12) in the vicinity of the UT to Lower Creek were previously compared to
the elevations of two surveyed points in the drainage feature. These activities were
documented in Mid-Atlantic’s Groundwater Monitoring and Free Product Recovery
Report dated June 15, 2012 and the results of water elevation comparisons since
that time are summarized in Table 4.3. As indicated, it appears the bottom of the
ditch is lower in elevation than the water table, suggesting that groundwater is
discharging into the drainage feature.
Groundwater Monitoring Report August 7, 2019
Speedway 7972 (former WilcoHess 353) Page 4
Lenoir, North Carolina

 Proximity of Plume to Nearest Receptor:

The nearest surface water body is the UT to Lower Creek, located approximately
125 feet to the south and hydraulically downgradient of the source area of release.
Based on relative elevations of the water table in this area to the bottom of the UT,
groundwater appears to be discharging to this drainage feature (Table 4.3).
Monitoring wells MW-11, MW-15 and MW-16 are located immediately upgradient
of the UT to Lower Creek and thus provide the best data for use in groundwater to
surface water comparisons. Therefore, based on the results of the current and
historical sampling events, the dissolved-phase groundwater contaminant plume
appears to be migrating off-site and discharging to the UT to Lower Creek.

 Estimated Groundwater Flow Direction:

Groundwater flow direction in the surficial aquifer was determined by development
of a water table contour map (Drawing 4.3) based upon water table elevation data
obtained from select site monitoring wells in March 2019. Interpretation of the
water level data for the current sampling event suggests that the groundwater flow
direction is primarily towards the southwest, with a hydraulic gradient (measured
from MW-8 toward MW-15) of approximately 0.070 ft/ft. The hydraulic gradient was
calculated using the procedure discussed in Appendix B.

4.4 Spill Bucket Discussion

Non-passing hydrostatic tests were conducted on the spill buckets for the regular
unleaded USTs in November 2017 and November 2018. In response, NCDEQ concurred
that in lieu of a site check, the sampling results from source area wells MW-1 and MW-8
in March 2019 should be compared to the results of previous sampling events (Table 4.1).
As indicated, benzene concentrations detected in the samples collected during the
March 2019 sampling event increased when compared to the results of previous (note
that the benzene results for the sample collected from MW-1 were biased on the high
side, as indicated in the laboratory report in Appendix C). However, please also note that
additional target compound concentrations detected in these samples appeared to be
generally consistent with the results of prior events. Therefore, in the event a release(s)
did occur from the spill buckets, the release(s) would not affect the current remedial
approach. As such, Mid-Atlantic recommends no further action for the spill bucket issue.

5.0 FUTURE SITE REMEDIATION

The site is currently ranked intermediate risk due to the presence of surface water within
500 feet of the source area of release. The UT to Lower Creek is located approximately 125
feet south and hydraulically downgradient of the release, and petroleum-related constituents
have historically been detected in the surface water samples collected from this drainage
feature (note that these constituents have not been reported above the NCSWQS since
February 2013). As such, the proposed remedial approach for the site at this time includes
Groundwater Monitoring Report August 7, 2019
Speedway 7972 (former WilcoHess 353) Page 5
Lenoir, North Carolina

a combination of active source zone treatment and enhanced natural attenuation along the
outer extent of the plume, particularly between the source area of the release and the
downgradient receptor (UT to Lower Creek).

Based on the recent data and current groundwater trends, the proposed remedial approach
will utilize chemical oxidation technologies to reduce contaminant concentrations within the
source area of the release (i.e. the immediate vicinity of wells MW-1 and MW-8) and mitigate
the discharge of petroleum-related constituents to the receiving surface waters. Under this
approach, monitoring wells MW-11, MW-15, and MW-16 will be used to support the
application of ORC (or similar) and formation of an “oxygen barrier” between the source area
of the release and the UT to Lower Creek. However, additional monitoring events may be
warranted prior to the use of chemical oxidation technologies.

6.0 SUMMARY, CONCLUSIONS AND RECOMMENDATIONS

The March 2019 groundwater/surface water monitoring activities are summarized as
follows:

 Groundwater samples were collected from six selected site monitoring wells on
March 25, 2019 to monitor plume concentrations in the vicinity of the source area
of the release (MW-1, MW-3 and MW-8) and immediately upgradient of the
receiving UT to lower Creek (MW-11, MW-15 and MW-16); and

 Three surface water samples were collected from the downgradient UT to Lower
Creek, located approximately 125 feet south of the source area of the release.

Based on the results of the sampling event, Mid-Atlantic concludes the following:

 Free product was not detected at the site during the March 2019 groundwater
monitoring event and has not been detected at the site since September 2012;

 The groundwater sample collected from source area monitoring well MW-8 exhibited
toluene and naphthalene concentrations in excess of ten times the NCSWQS but
below the GCLs. No other samples collected during the monitoring event exceeded
ten times the NCSWQS, including the wells located immediately upgradient of the
UT to Lower Creek (MW-11, MW-15 and MW-16);

 Surface water samples collected from the UT to Lower Creek did not exhibit target
compound concentrations in excess of the NCSWQS for the current monitoring
event. Additionally, target compounds for surface water samples collected from the
UT to Lower Creek have not been detected at concentrations exceeding the
NCSWQS since February 2013;

Groundwater Monitoring Report August 7, 2019
Speedway 7972 (former WilcoHess 353) Page 6
Lenoir, North Carolina

 When compared with the results of previous sampling events, the overall
groundwater contaminant concentrations appear to be generally consistent with
previous sampling events. An increase in benzene concentrations was observed
in the groundwater samples collected from wells MW-1 (note the lab indicated
results for this sample were biased on the high side), MW-8 and MW-15; however,
the additional target compound concentrations detected in the samples collected
from these wells remained relatively consistent with previous sampling events; and

 The dissolved-phase groundwater contaminant plume is currently defined by the
existing monitoring well network to the extent of ten times the NCSWQS.

Based on these conclusions, Mid-Atlantic recommends the following:

 In the event a release(s) did occur from the spill buckets, the release(s) would not
affect the current remedial approach. As such, Mid-Atlantic recommends no further
action for the spill bucket issue;

 Additional groundwater/surface water monitoring prior to the use of chemical
oxidation technologies; and

 Submittal of this report to the NCDEQ, Asheville Regional Office, UST Section.

DRAWINGS
´
TOPOGRAPHIC SITE MAP SPEEDWAY 7972LENOIR, NORTH CAROLINA
DRAWN BY: RDC DATE:
ENG. CHECK:
JOB NO:
APPROVAL:
DRAFTCHECK:GIS NO:
DWG NO:
REFERENCES:SCALE:
North Carolina
CALDWELL
BURKE
AVERY
CATAWBA
WILKESAREA SHOWNWITHIN CALDWELL COUNTY
AUGUST 2018
000R1760.17
06G-00R1760.17-11.1
1. LENOIR, NC DIGITAL RASTER GRAPHIC, USGS. SCANNED FROM 1:24,000-SCALE USGS TOPOGRAPHIC MAP: LENOIR, NC, 1994.2. INSET MAP DIGITAL DATA FROM 2002 NATIONAL TRANSPORTATION ATLAS, BUREAU OF TRANSPORTATION STATISTICS, WASHINGTON, D.C.
CONTOUR INTERVAL = 40 FEET
0 1,000 2,000Feet
SITE
´
1:12,000

TABLES
MW-1 2 9/20/2006 20 5 - 20
MW-2 2 5/31/2011 15 5 - 15
MW-3 2 6/1/2011 18 8 - 18
MW-4 2 5/31/2011 16.5 6.5 - 16.5
MW-5 2 5/31/2011 17 7 - 17
MW-6 2 5/31/2011 18 8 - 18
MW-7 2 6/1/2011 17 7 - 17
MW-8 2 6/1/2011 16 6 - 16
MW-9D 2 6/2/2011 80 40 - 80
MW-10 2 8/30/2011 21 11 - 21
MW-11 2 8/29/2011 16 6 - 16
MW-12 2 8/29/2011 17 7 - 17
MW-13 2 8/30/2011 16 6 - 16
MW-14 2 8/30/2011 16 6 - 16
MW-15 2 8/3/2016 17 7 - 17
MW-16 2 8/3/2016 16 6 - 16
NOTES:
BLS - Below land surface
WELL NUMBER DIAMETER
(INCHES)
CONSTRUCTION
DATE
CASING DEPTH
(FEET BLS)
SCREENED
INTERVAL (FEET
BLS)
DWM INCIDENT NO.: 28414
TABLE 3.1
MONITORING WELL CONSTRUCTION INFORMATION
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC JOB NO. 000R1760.18
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP
THICKNESS (ft)DTW (ft), BTOC CORRECTED
DTW (ft)SWLE (ft)
MW-1 09/21/06 102.18 ----11.05 --91.13
MW-1 06/02/11 102.18 ----11.01 --91.17
MW-1 08/29/11 102.18 11.54 0.56 12.10 11.69 90.49
MW-1 04/27/12 102.18 ----10.74 --91.44
MW-1 08/16/12 102.18 ----11.34 --90.84
MW-1 02/13/13 102.18 ----10.81 --91.37
MW-1 09/05/13 102.18 ----10.79 --91.39
MW-1 05/01/14 102.18 ----10.46 --91.72
MW-1 09/23/14 102.18 ----11.30 --90.88
MW-1 10/28/15 102.18 ----10.70 --91.48
MW-1 08/03/16 102.18 ----11.38 --90.80
MW-1 12/21/17 102.18 ----11.10 --91.08
MW-1 06/27/18 102.18 NM NM NM NM NM
MW-1 03/25/19 102.18 ----10.49 --91.69
MW-2
MW-2 06/02/11 98.52 ----7.90 --90.62
MW-2 08/29/11 98.52 ----8.45 --90.07
MW-2 04/27/12 98.52 ----7.27 --91.25
MW-2 08/16/12 98.52 ----8.39 --90.13
MW-2 02/13/13 98.52 ----8.09 --90.43
MW-2 09/05/13 98.52 ----8.32 --90.20
MW-2 05/01/14 98.52 ----8.14 --90.38
MW-2 09/23/14 98.52 ----8.51 --90.01
MW-2 10/28/15 98.52 ----8.06 --90.46
MW-2 08/03/16 98.52 NM NM NM NM NM
MW-2 12/21/17 98.52 NM NM NM NM NM
MW-2 06/27/18 98.52 NM NM NM NM NM
MW-2 03/25/19 98.52 NM NM NM NM NM
MW-3
MW-3 06/02/11 102.71 ----12.87 --89.84
MW-3 08/29/11 102.71 ----13.50 --89.21
MW-3 04/27/12 102.71 ----12.23 --90.48
MW-3 08/16/12 102.71 ----12.30 --90.41
MW-3 02/13/13 102.71 ----12.09 --90.62
MW-3 09/05/13 102.71 ----12.91 --89.80
MW-3 05/01/14 102.71 ----12.28 --90.43
MW-3 09/23/14 102.71 ----13.19 --89.52
MW-3 10/28/15 102.71 ----11.26 --91.45
MW-3 08/03/16 102.71 ----12.85 --89.86
MW-3 12/21/17 102.71 ----11.86 --90.85
MW-3 06/27/18 102.71 NM NM NM NM NM
MW-3 03/25/19 102.71 ----12.70 --90.01
MW-4
MW-4 06/02/11 103.37 ----11.76 --91.61
MW-4 08/29/11 103.37 ----12.47 --90.90
MW-4 04/27/12 103.37 ----11.41 --91.96
MW-4 08/16/12 103.37 ----12.28 --91.09
MW-4 02/13/13 103.37 ----11.37 --92.00
MW-4 09/05/13 103.37 ----11.60 --91.77
MW-4 05/01/14 103.37 ----11.22 --92.15
MW-4 09/23/14 103.37 ----12.06 --91.31
MW-4 10/28/15 103.37 ----11.92 --91.45
MW-4 08/03/16 103.37 NM NM NM NM NM
Well did not exist
Well did not exist
Well did not exist
TABLE 3.2
HISTORICAL LIQUID LEVEL MEASUREMENTS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC JOB NO. 000R1760.18
DWM INCIDENT NO.: 28414
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP
THICKNESS (ft)DTW (ft), BTOC CORRECTED
DTW (ft)SWLE (ft)
TABLE 3.2
HISTORICAL LIQUID LEVEL MEASUREMENTS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC JOB NO. 000R1760.18
DWM INCIDENT NO.: 28414
MW-4 12/21/17 103.37 NM NM NM NM NM
MW-4 06/27/18 103.37 NM NM NM NM NM
MW-4 03/25/19 103.37 NM NM NM NM NM
MW-5
MW-5 06/02/11 103.23 ----10.23 --93.00
MW-5 08/29/11 103.23 ----10.80 --92.43
MW-5 04/27/12 103.23 ----10.14 --93.09
MW-5 08/16/12 103.23 ----10.69 --92.54
MW-5 02/13/13 103.23 ----10.12 --93.11
MW-5 09/05/13 103.23 ----10.09 --93.14
MW-5 05/01/14 103.23 ----10.01 --93.22
MW-5 09/23/14 103.23 ----10.43 --92.80
MW-5 10/28/15 103.23 ----10.53 --92.70
MW-5 08/03/16 103.23 NM NM NM NM NM
MW-5 12/21/17 103.23 NM NM NM NM NM
MW-5 06/27/18 103.23 NM NM NM NM NM
MW-5 03/25/19 103.23 NM NM NM NM NM
MW-6
MW-6 06/02/11 103.85 ----10.74 --93.11
MW-6 08/29/11 103.85 ----11.34 --92.51
MW-6 04/27/12 103.85 ----10.69 --93.16
MW-6 08/16/12 103.85 ----11.19 --92.66
MW-6 02/13/13 103.85 ----10.66 --93.19
MW-6 09/05/13 103.85 ----10.59 --93.26
MW-6 05/01/14 103.85 ----10.48 --93.37
MW-6 09/23/14 103.85 ----10.96 --92.89
MW-6 10/28/15 103.85 ----11.04 --92.81
MW-6 08/03/16 103.85 NM NM NM NM NM
MW-6 12/21/17 103.85 NM NM NM NM NM
MW-6 06/27/18 103.85 NM NM NM NM NM
MW-6 03/25/19 103.85 NM NM NM NM NM
MW-7
MW-7 06/02/11 101.70 ----9.24 --92.46
MW-7 08/29/11 101.70 ----9.64 --92.06
MW-7 04/27/12 101.70 ----9.18 --92.52
MW-7 08/16/12 101.70 ----9.46 --92.24
MW-7 02/13/13 101.70 ----9.13 --92.57
MW-7 09/05/13 101.70 ----9.02 --92.68
MW-7 05/01/14 101.70 ----8.98 --92.72
MW-7 09/23/14 101.70 ----9.39 --92.31
MW-7 10/28/15 101.70 ----9.18 --92.52
MW-7 08/03/16 101.70 NM NM NM NM NM
MW-7 12/21/17 101.70 NM NM NM NM NM
MW-7 06/27/18 101.70 NM NM NM NM NM
MW-7 03/25/19 101.70 NM NM NM NM NM
MW-8
MW-8 06/02/11 102.29 ----10.92 --91.37
MW-8 08/29/11 102.29 11.74 0.26 12.00 11.81 90.48
MW-8 04/27/12 102.29 ----11.14 --91.15
MW-8 08/16/12 102.29 11.51 0.04 11.55 11.52 90.74
MW-8 02/13/13 102.29 ----11.10 --91.19
MW-8 09/05/13 102.29 ----11.26 --91.03
Well did not exist
Well did not exist
Well did not exist
Well did not exist
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP
THICKNESS (ft)DTW (ft), BTOC CORRECTED
DTW (ft)SWLE (ft)
TABLE 3.2
HISTORICAL LIQUID LEVEL MEASUREMENTSSPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC JOB NO. 000R1760.18
DWM INCIDENT NO.: 28414
MW-8 05/01/14 102.29 ----10.09 --92.20
MW-8 09/23/14 102.29 ----11.59 --90.70
MW-8 10/28/15 102.29 ----10.89 --91.40
MW-8 08/03/16 102.29 ----11.61 --90.68
MW-8 12/21/17 102.29 ----11.29 --91.00
MW-8 06/27/18 102.29 NM NM NM NM NM
MW-8 03/25/19 102.29 ----11.16 --91.13
MW-9D
MW-9D 06/02/11 102.64 ----78.29 --24.35
MW-9D 08/29/11 102.64 ----14.40 --88.24
MW-9D 04/27/12 102.64 ----10.75 --91.89
MW-9D 08/16/12 102.64 ----11.03 --91.61
MW-9D 02/14/13 102.64 ----10.32 --92.32
MW-9D 09/05/13 102.64 ----9.96 --92.68
MW-9D 05/01/14 102.64 ----10.26 --92.38
MW-9D 09/23/14 102.64 ----11.16 --91.48
MW-9D 10/28/15 102.64 ----10.80 --91.84
MW-9D 08/03/16 102.64 NM NM NM NM NM
MW-9D 12/21/17 102.64 NM NM NM NM NM
MW-9D 06/27/18 102.64 NM NM NM NM NM
MW-9D 03/25/19 102.64 NM NM NM NM NM
MW-10
MW-10 08/29/11 98.02 ----15.53 --82.49
MW-10 04/27/12 98.02 ----13.25 --84.77
MW-10 08/16/12 98.02 ----13.77 --84.25
MW-10 02/13/13 98.02 ----13.38 --84.64
MW-10 09/05/13 98.02 ----13.90 --84.12
MW-10 05/01/14 98.02 ----13.11 --84.91
MW-10 09/23/14 98.02 ----14.46 --83.56
MW-10 10/28/15 98.02 ----11.83 --86.19
MW-10 08/03/16 98.02 NM NM NM NM NM
MW-10 12/21/17 98.02 NM NM NM NM NM
MW-10 06/27/18 98.02 NM NM NM NM NM
MW-10 03/25/19 98.02 NM NM NM NM NM
MW-11
MW-11 08/29/11 93.21 ----9.84 --83.37
MW-11 04/27/12 93.21 ----9.29 --83.92
MW-11 08/16/12 93.21 ----9.52 --83.69
MW-11 02/13/13 93.21 ----9.39 --83.82
MW-11 09/05/13 93.21 ----9.62 --83.59
MW-11 05/01/14 93.21 ----9.42 --83.79
MW-11 09/23/14 93.21 ----9.72 --83.49
MW-11 10/28/15 93.21 ----8.95 --84.26
MW-11 08/03/16 93.21 ----9.62 --83.59
MW-11 12/21/17 93.21 ----9.20 --84.01
MW-11 06/27/18 93.21 ----9.20 --84.01
MW-11 03/25/19 93.21 ----9.43 --83.78
MW-12
MW-12 08/29/11 94.31 ----10.17 --84.14
MW-12 04/27/12 94.31 ----9.74 --84.57
MW-12 08/16/12 94.31 ----10.12 --84.19
MW-12 02/13/13 94.31 ----9.88 --84.43
Well did not exist
Well did not exist
Well did not exist
Well did not exist
WELL NUMBER DATE TOC (ft)DTP (ft)APPARENT FP
THICKNESS (ft)DTW (ft), BTOC CORRECTED
DTW (ft)SWLE (ft)
TABLE 3.2HISTORICAL LIQUID LEVEL MEASUREMENTS
SPEEDWAY 7972 (FORMER WILCOHESS 353)LENOIR, NORTH CAROLINA
MID-ATLANTIC JOB NO. 000R1760.18DWM INCIDENT NO.: 28414
MW-12 09/05/13 94.31 ----10.14 --84.17
MW-12 05/01/14 94.31 ----9.94 --84.37
MW-12 09/23/14 94.31 ----10.28 --84.03
MW-12 10/28/15 94.31 ----9.69 --84.62
MW-12 08/03/16 94.31 NM NM NM NM NM
MW-12 12/21/17 94.31 NM NM NM NM NM
MW-12 06/27/18 94.31 NM NM NM NM NM
MW-12 03/25/19 94.31 NM NM NM NM NM
MW-13
MW-13 08/29/11 95.18 ----9.88 --85.30
MW-13 04/27/12 95.18 ----10.02 --85.16
MW-13 08/16/12 95.18 ----10.08 --85.10
MW-13 02/14/13 95.18 ----10.04 --85.14
MW-13 09/05/13 95.18 ----10.68 --84.50
MW-13 05/01/14 95.18 ----10.58 --84.60
MW-13 09/23/14 95.18 ----10.69 --84.49
MW-13 10/28/15 95.18 ----10.69 --84.49
MW-13 08/03/16 95.18 NM NM NM NM NM
MW-13 12/21/17 95.18 NM NM NM NM NM
MW-13 06/27/18 95.18 NM NM NM NM NM
MW-13 03/25/19 95.18 NM NM NM NM NM
MW-14
MW-14 08/29/11 95.92 ----8.90 --87.02
MW-14 04/27/12 95.92 ----8.46 --87.46
MW-14 08/16/12 95.92 ----8.83 --87.09
MW-14 02/14/13 95.92 ----8.29 --87.63
MW-14 09/05/13 95.92 ----8.38 --87.54
MW-14 05/01/14 95.92 ----8.18 --87.74
MW-14 09/23/14 95.92 ----8.41 --87.51
MW-14 10/28/15 95.92 ----8.33 --87.59
MW-14 08/03/16 95.92 NM NM NM NM NM
MW-14 12/21/17 95.92 NM NM NM NM NM
MW-14 06/27/18 95.92 NM NM NM NM NM
MW-14 03/25/19 95.92 NM NM NM NM NM
MW-15
MW-15 08/03/16 92.12 ----8.35 --83.77
MW-15 12/21/17 92.12 ----8.04 --84.08
MW-15 06/27/18 92.12 ----8.02 --84.10
MW-15 03/25/19 92.12 ----8.15 --83.97
MW-16 08/03/16 92.02 ----7.64 --84.38
MW-16 12/21/17 92.02 ----8.01 --84.01
MW-16 06/27/18 92.02 ----7.99 --84.03
MW-16 03/25/19 92.02 ----8.17 --83.85
Notes:
Shaded cells indicate that the water level has been corrected for the presence of free product
BTOC - Below Top of Casing (TOC)
DTP - Depth to Free Product (in feet)
DTW - Depth to Water (in feet)
SWLE - Static Water Elevation (in feet)
NM - Not Measured
Well did not exist
Well did not exist
Well did not exist
5,000 84,500 260,000 85,500 70,000 20,000 6,000 NE NE NE 15,000
510 970 110 4,500 NE 15,000 120 14,000 NE NE 250
1 600 600 500 70 20 6 400 700 200 15
MW-1 09/21/06 10,100 910 12,800 4,860 NA 2,070 NA 35,000 8,700 2,000 NA
MW-1 06/02/11 1,540 2,480 9,710 11,610 ND NDa 676 26,000 33,300 11,800 0.8 J
MW-1 08/29/11 FP FP FP FP FP FP FP FP FP FP FP
MW-1 04/27/12 794 1,900 7,300 10,700 ND NDa NA NA NA NA NA
MW-1 08/16/12 536 1,510 2,580 5,550 133 NDa NA NA NA NA NA
MW-1 02/13/13 400 2,400 2,700 9,600 ND 74 J 650 NA NA NA NA
MW-1 09/05/13 110 1,100 750 4,100 ND ND 480 J NA NA NA NA
MW-1 05/02/14 110 1,100 590 3,700 ND ND NA NA NA NA NA
MW-1 09/23/14 46 880 310 2,750 ND ND 270 NA NA NA NA
MW-1 10/28/15 22.2 670 107 2,043 ND ND 329 NA NA NA NA
MW-1 08/03/16 51.4 633 107 1,877 7.07 J ND 252 NA NA NA NA
MW-1 12/21/17 54.8 592 47.5 J 1,670 ND ND 204 J NA NA NA NA
MW-1 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-1 03/25/19 182 V3 503 ND ND 40.7 V3 23.9 V3 114 NA NA NA NA
MW-2 06/02/11 3,200 1,150 6,080 3,960 ND NDa 240 17,200 12,400 NDa 0.7 J
MW-2 08/29/11 1,450 822 820 1,006 74 J 125 J NA NA NA NA NA
MW-2 04/27/12 1,400 1,730 1,340 3,322 ND NDa NA NA NA NA NA
MW-2 08/16/12 131 141 ND ND ND 22.8 NA NA NA NA NA
MW-2 02/13/13 78 37 3.0 2.2 J 0.46 J 14 12 NA NA NA NA
MW-2 09/05/13 3.9 1.0 ND ND ND 4.5J ND NA NA NA NA
MW-2 05/02/14 2.0 4.9 ND ND ND 12 NA NA NA NA NA
MW-2 09/23/14 0.16 J 0.37 J ND ND ND 6.4 ND NA NA NA NA
MW-2 10/28/15 ND 1.15 ND 4.48 J ND 3.62 ND NA NA NA NA
MW-2 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-2 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-2 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-2 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-3 06/02/11 50.9 25.9 103 122.5 ND ND 8.34 154 ND 191 1.3 J
MW-3 08/29/11 155 68.6 129 376.2 23.4 ND NA NA NA NA NA
MW-3 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-3 08/16/12 2.56 ND 0.840 J 3.92 J ND ND NA NA NA NA NA
MW-3 02/13/13 ND ND ND ND ND ND ND NA NA NA NA
MW-3 09/05/13 1.1 1.2 1.8 2.5 J ND ND ND NA NA NA NA
MW-3 05/01/14 ND ND ND ND ND ND NA NA NA NA NA
MW-3 09/23/14 4.4 5.4 2.6 9.8 ND ND 1.4 NA NA NA NA
TABLE 4.1
SUMMARY OF HISTORICAL GROUNDWATER MONITORING RESULTS FOR SELECTED COMPOUNDS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC PROJECT NO. 000R1760.18
GCL (ug/l)
DWM INCIDENT NO.: 28414
10X SWQS or NWQC (ug/l)
Toluene
(ug/l)
Total
Xylenes
(ug/l)
Well Number Sample Date
NCGQS (ug/l)
C9-C12
Aliphatics
(ug/l)
Benzene
(ug/l)
Ethylbenzene
(ug/l)
C9-C10
Aromatics
(ug/l)
Lead (ug/l)Diisopropyl
ether (DIPE)
(ug/l)
MTBE (ug/l)Naphthalene
(ug/l)
C5-C8
Aliphatics
(ug/l)
Page 1 of 6
5,000 84,500 260,000 85,500 70,000 20,000 6,000 NE NE NE 15,000
510 970 110 4,500 NE 15,000 120 14,000 NE NE 250
1 600 600 500 70 20 6 400 700 200 15
TABLE 4.1
SUMMARY OF HISTORICAL GROUNDWATER MONITORING RESULTS FOR SELECTED COMPOUNDS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC PROJECT NO. 000R1760.18
GCL (ug/l)
DWM INCIDENT NO.: 28414
10X SWQS or NWQC (ug/l)
Toluene
(ug/l)
Total
Xylenes
(ug/l)
Well Number Sample Date
NCGQS (ug/l)
C9-C12
Aliphatics
(ug/l)
Benzene
(ug/l)
Ethylbenzene
(ug/l)
C9-C10
Aromatics
(ug/l)
Lead (ug/l)Diisopropyl
ether (DIPE)
(ug/l)
MTBE (ug/l)Naphthalene
(ug/l)
C5-C8
Aliphatics
(ug/l)
MW-3 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-3 08/03/16 9.12 8.50 4.37 J 21.5 ND ND 7.42 NA NA NA NA
MW-3 12/21/17 ND ND ND ND ND ND ND NA NA NA NA
MW-3 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-3 03/25/19 ND ND ND ND ND ND 1.76 J NA NA NA NA
MW-4 06/02/11 ND ND ND ND 0.41 6.95 ND ND ND ND 0.8J
MW-4 08/29/11 ND ND ND ND ND 3.11 NA NA NA NA NA
MW-4 04/27/12 ND ND ND ND ND 1.56 J NA NA NA NA NA
MW-4 08/16/12 ND ND ND ND ND 2.54 NA NA NA NA NA
MW-4 02/13/13 ND ND ND ND ND 1.1 J ND NA NA NA NA
MW-4 09/05/13 ND ND ND ND ND 3.6 J ND NA NA NA NA
MW-4 05/01/14 ND ND ND ND ND 1.5*NA NA NA NA NA
MW-4 09/23/14 ND ND ND ND 0.26 J 1.8 NA NA NA NA NA
MW-4 10/28/15 ND ND ND ND ND 0.927 J ND NA NA NA NA
MW-4 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-4 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-4 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-4 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-5 06/02/11 ND ND ND ND ND 1.62 ND ND ND ND 0.7 J
MW-5 08/29/11 ND ND ND ND ND 1.48 J NA NA NA NA NA
MW-5 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-5 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-5 02/13/13 ND ND ND ND ND 0.77 J ND NA NA NA NA
MW-5 09/05/13 ND ND ND ND ND 0.76 J ND NA NA NA NA
MW-5 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-5 09/23/14 ND ND ND ND ND 1.0 NA NA NA NA NA
MW-5 10/28/15 ND ND ND ND ND 0.659 J ND NA NA NA NA
MW-5 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-5 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-5 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-5 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-6 06/02/11 ND ND ND ND ND 3.76 ND ND ND ND 1.2 J
MW-6 08/29/11 ND ND ND ND ND 2.58 NA NA NA NA NA
MW-6 04/27/12 ND ND ND ND ND 2.00 NA NA NA NA NA
Page 2 of 6
5,000 84,500 260,000 85,500 70,000 20,000 6,000 NE NE NE 15,000
510 970 110 4,500 NE 15,000 120 14,000 NE NE 250
1 600 600 500 70 20 6 400 700 200 15
TABLE 4.1
SUMMARY OF HISTORICAL GROUNDWATER MONITORING RESULTS FOR SELECTED COMPOUNDS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC PROJECT NO. 000R1760.18
GCL (ug/l)
DWM INCIDENT NO.: 28414
10X SWQS or NWQC (ug/l)
Toluene
(ug/l)
Total
Xylenes
(ug/l)
Well Number Sample Date
NCGQS (ug/l)
C9-C12
Aliphatics
(ug/l)
Benzene
(ug/l)
Ethylbenzene
(ug/l)
C9-C10
Aromatics
(ug/l)
Lead (ug/l)Diisopropyl
ether (DIPE)
(ug/l)
MTBE (ug/l)Naphthalene
(ug/l)
C5-C8
Aliphatics
(ug/l)
MW-6 08/16/12 ND ND ND ND ND 2.68 NA NA NA NA NA
MW-6 02/13/13 ND ND ND ND ND 3.2 J ND NA NA NA NA
MW-6 09/05/13 ND ND ND ND ND 3.3 J ND NA NA NA NA
MW-6 05/01/14 ND ND ND ND 0.49 J 6.1*NA NA NA NA NA
MW-6 09/23/14 ND ND ND ND 0.52 4.2 NA NA NA NA NA
MW-6 10/28/15 ND ND ND ND 0.640 J 3.41 ND NA NA NA NA
MW-6 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-6 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-6 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-6 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-7 06/02/11 ND ND ND ND ND 0.9 ND ND ND ND 24.1
MW-7 08/29/11 ND ND ND ND ND ND NA NA NA NA NA
MW-7 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-7 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-7 02/13/13 ND ND ND ND ND 0.81 J ND NA NA NA NA
MW-7 09/05/13 ND ND ND ND ND 0.55 J ND NA NA NA NA
MW-7 05/01/14 ND ND ND ND ND ND NA NA NA NA NA
MW-7 09/23/14 ND ND ND ND ND 0.80 NA NA NA NA NA
MW-7 10/28/15 ND ND ND ND ND 0.980 J ND NA NA NA NA
MW-7 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-7 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-7 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-7 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-8 06/02/11 2,300 1,600 12,500 11,220 NDa NDa 600 22,600 27,900 NDa 1.1 J
MW-8 08/29/11 FP FP FP FP FP FP FP FP FP FP FP
MW-8 04/27/12 805 1,340 5,280 10,240 ND NDa NA NA NA NA NA
MW-8 08/16/12 FP FP FP FP FP FP FP FP FP FP FP
MW-8 02/13/13 700 1,800 3,500 12,000 ND ND 880 NA NA NA NA
MW-8 09/05/13 730 1,300 6,900 11,000 ND ND 900 NA NA NA NA
MW-8 05/02/14 480 1,100 3,800 8,800 ND ND NA NA NA NA NA
MW-8 09/23/14 300 1,400 3,800 7,600 ND ND 710 NA NA NA NA
MW-8 10/28/15 140 1,740 3,580 8,970 ND ND 875 NA NA NA NA
MW-8 08/03/16 655 942 2,300 4,920 39.1 J ND 670 NA NA NA NA
MW-8 12/21/17 180 1,100 2,000 5,480 ND ND 556 NA NA NA NA
MW-8 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
Page 3 of 6
5,000 84,500 260,000 85,500 70,000 20,000 6,000 NE NE NE 15,000
510 970 110 4,500 NE 15,000 120 14,000 NE NE 250
1 600 600 500 70 20 6 400 700 200 15
TABLE 4.1
SUMMARY OF HISTORICAL GROUNDWATER MONITORING RESULTS FOR SELECTED COMPOUNDS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC PROJECT NO. 000R1760.18
GCL (ug/l)
DWM INCIDENT NO.: 28414
10X SWQS or NWQC (ug/l)
Toluene
(ug/l)
Total
Xylenes
(ug/l)
Well Number Sample Date
NCGQS (ug/l)
C9-C12
Aliphatics
(ug/l)
Benzene
(ug/l)
Ethylbenzene
(ug/l)
C9-C10
Aromatics
(ug/l)
Lead (ug/l)Diisopropyl
ether (DIPE)
(ug/l)
MTBE (ug/l)Naphthalene
(ug/l)
C5-C8
Aliphatics
(ug/l)
MW-8 03/25/19 418 668 1,090 2,487 46.9 7.75 386 NA NA NA NA
MW-9d 06/02/11 ND ND 0.64 ND ND ND ND ND ND ND 7.6
MW-9d 08/29/11 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 02/14/13 ND ND ND ND ND ND ND NA NA NA NA
MW-9d 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-9d 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-9d 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-9d 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-9d 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-10
MW-10 08/30/11 ND ND ND ND ND ND ND ND ND ND 17.2
MW-10 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-10 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-10 02/13/13 ND ND ND ND ND ND ND NA NA NA NA
MW-10 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-10 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-10 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-10 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-10 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-10 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-10 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-10 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-11
MW-11 08/30/11 303 ND ND ND ND 335 ND 853 ND ND 4.0 J
MW-11 04/27/12 ND ND ND ND 6.27 17.2 NA NA NA NA NA
MW-11 08/16/12 71.7 ND ND ND 7.70 75.6 NA NA NA NA NA
MW-11 02/13/13 ND ND ND ND 10 8.9 ND NA NA NA NA
MW-11 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-11 05/02/14 ND ND ND ND 1.3 ND NA NA NA NA NA
Well did not exist
Well did not exist
Page 4 of 6
5,000 84,500 260,000 85,500 70,000 20,000 6,000 NE NE NE 15,000
510 970 110 4,500 NE 15,000 120 14,000 NE NE 250
1 600 600 500 70 20 6 400 700 200 15
TABLE 4.1
SUMMARY OF HISTORICAL GROUNDWATER MONITORING RESULTS FOR SELECTED COMPOUNDS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC PROJECT NO. 000R1760.18
GCL (ug/l)
DWM INCIDENT NO.: 28414
10X SWQS or NWQC (ug/l)
Toluene
(ug/l)
Total
Xylenes
(ug/l)
Well Number Sample Date
NCGQS (ug/l)
C9-C12
Aliphatics
(ug/l)
Benzene
(ug/l)
Ethylbenzene
(ug/l)
C9-C10
Aromatics
(ug/l)
Lead (ug/l)Diisopropyl
ether (DIPE)
(ug/l)
MTBE (ug/l)Naphthalene
(ug/l)
C5-C8
Aliphatics
(ug/l)
MW-11 09/23/14 ND ND ND ND 0.61 0.97 NA NA NA NA NA
MW-11 10/28/15 20.3 ND ND ND 0.719 J 4.27 ND NA NA NA NA
MW-11 08/03/16 ND ND ND ND 0.398 J 0.486 J ND NA NA NA NA
MW-11 12/21/17 ND ND ND ND 3.34 0.824 J ND NA NA NA NA
MW-11 06/27/18 ND ND ND ND 0.511 J ND ND NA NA NA NA
MW-11 03/25/19 ND ND ND ND ND ND ND NA NA NA NA
MW-12
MW-12 08/30/11 ND ND ND ND ND ND ND ND ND ND 0.9J
MW-12 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-12 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-12 02/13/13 ND ND ND ND ND ND ND NA NA NA NA
MW-12 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-12 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-12 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-12 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-12 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-12 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-12 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-12 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-13
MW-13 08/30/11 ND ND ND ND ND ND ND ND ND ND 8.5
MW-13 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-13 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-13 02/14/13 ND ND ND ND ND ND ND NA NA NA NA
MW-13 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-13 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-13 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-13 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-13 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-13 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-13 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-13 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-14
MW-14 08/30/11 ND ND ND ND ND ND ND ND ND ND 9.1
Well did not exist
Well did not exist
Well did not exist
Page 5 of 6
5,000 84,500 260,000 85,500 70,000 20,000 6,000 NE NE NE 15,000
510 970 110 4,500 NE 15,000 120 14,000 NE NE 250
1 600 600 500 70 20 6 400 700 200 15
TABLE 4.1
SUMMARY OF HISTORICAL GROUNDWATER MONITORING RESULTS FOR SELECTED COMPOUNDS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
MID-ATLANTIC PROJECT NO. 000R1760.18
GCL (ug/l)
DWM INCIDENT NO.: 28414
10X SWQS or NWQC (ug/l)
Toluene
(ug/l)
Total
Xylenes
(ug/l)
Well Number Sample Date
NCGQS (ug/l)
C9-C12
Aliphatics
(ug/l)
Benzene
(ug/l)
Ethylbenzene
(ug/l)
C9-C10
Aromatics
(ug/l)
Lead (ug/l)Diisopropyl
ether (DIPE)
(ug/l)
MTBE (ug/l)Naphthalene
(ug/l)
C5-C8
Aliphatics
(ug/l)
MW-14 04/27/12 ND ND ND ND ND ND NA NA NA NA NA
MW-14 08/16/12 ND ND ND ND ND ND NA NA NA NA NA
MW-14 02/14/13 ND ND ND ND ND ND ND NA NA NA NA
MW-14 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
MW-14 05/02/14 ND ND ND ND ND ND NA NA NA NA NA
MW-14 09/23/14 ND ND ND ND ND ND NA NA NA NA NA
MW-14 10/28/15 ND ND ND ND ND ND ND NA NA NA NA
MW-14 08/03/16 NS NS NS NS NS NS NS NS NS NS NS
MW-14 12/21/17 NS NS NS NS NS NS NS NS NS NS NS
MW-14 06/27/18 NS NS NS NS NS NS NS NS NS NS NS
MW-14 03/25/19 NS NS NS NS NS NS NS NS NS NS NS
MW-15
MW-15 08/04/16 2.05 14.7 5.09 37.4 2.75 113 4.96 J 636 492 241 8.72 B
MW-15 12/21/17 0.985 J 7.20 0.809 J 5.691 J 2.05 45.2 1.64 J NA NA NA NA
MW-15 06/27/18 3.64 3.70 ND 4.88 2.10 40.9 1.30 J NA NA NA NA
MW-15 03/25/19 128 20.0 6.67 12.29 1.55 23.8 3.48 J NA NA NA NA
MW-16
MW-16 08/04/16 218 368 80.4 1,772 1.45 24.6 181 1,380 4,980 1,720 3.50 B J
MW-16 12/21/17 73.6 198 22.2 983 1.55 19.7 77.2 NA NA NA NA
MW-16 06/27/18 13.4 J 268 ND 1,432 ND ND 154.0 NA NA NA NA
MW-16 03/25/19 2.05 98.2 0.643 J 438 ND ND 79.1 NA NA NA NA
Notes:
ND - Not detected at or above laboratory's practical quantitation limit MTBE - Methyl tertiary-butyl ether V3 - Analytical results biased high due to sample matrix interference.
NDa - detection limit exceeds NCGQS DIPE - diisopropyl ether EPA NWQC - EPA National Water Quality Criteria
NA - Not Analyzed for this parameter GCL - Gross Contamination Level * C9-C12 Aliphatics (VPH) only. See laboratory report.
NS - Not Sampled NCGQS - North Carolina Groundwater Quality Standard ** C9-C10 Aromatics (VPH) only. See laboratory report.
NE - Standard not established Shaded values exceed 10X 2B NCSWQS, 10X EPA NWQC and/or GCL All concentrations reported in ug/L - micrograms per liter
NCSWQS - North Carolina Surface Water Quality Standards J- Estimated Value
Bold values exceed NCGQS B - Same analyte is found in associated blank
Note: the following NCGQS changes effective 1/13/10: Ethylbenzene 550 ug/L to 600 ug/L, Toluene 1000 ug/L to 600 ug/L, Total Xylenes 550 ug/L to 500 ug/L,
MTBE 200 ug/L to 20 ug/L, naphthalene 21 ug/L to 6 ug/L
Note: the following NCSWQS and/or EPA NWQC changes effective 5/5/13: Ethylbenzene NE to 97 ug/L, Total Xylenes NE to 450 ug/L, MTBE NE to 1,500 ug/L, Napththalene NE to 12 ug/L,
C5-C8 Aliphatics NE to 1,400 ug/L
Well did not exist
Well did not exist
Page 6 of 6
51 97 11 450 NE 1,500 12 1,400 NE NE 25
Stream #1Stream #1 04/13/12 13.5 4.99 15.6 15.86 ND ND 1.38 ND ND ND NAStream #1 08/16/12 10.5 2.06 2.44 7.46 ND 1.24 0.870 NA NA NA NAStream #1 02/14/13 15 5.2 16 6.5 ND 1.4 1.500 NA NA NA NA
Stream #1 09/05/13 0.71 2.3 1.1 7.2 ND ND 0.79J NA NA NA NAStream #1 05/02/14 6.6 5.0 10 16 ND ND ND NA NA NA NAStream #1 09/23/14 0.21 J 0.57 0.50 1.8 J ND ND ND NA NA NA NA
Stream #1 12/01/15 4.38 5.86 7.86 16.6 ND 1.11 1.45 J NA NA NA NAStream #1 08/03/16 ND ND ND ND ND ND ND NA NA NA NAStream #1 12/21/17 0.350 J 2.31 2.02 5.53 ND ND 1.60 J NA NA NA NAStream #1 06/27/18 0.464 J 2.38 1.61 7.64 ND ND 1.17 J NA NA NA NAStream #1 03/25/19 0.662 J 3.00 2.25 9.12 ND ND 2.67 J NA NA NA NA
Stream #2Stream #2 04/13/12 7.23 3.05 7.83 10.9 ND ND 0.970 ND ND ND NAStream #2 08/16/12 5.67 1.15 1.28 4.13 0.190J 1.55 0.530 NA NA NA NAStream #2 02/14/13 7.6 3.4 9.8 5.2 ND 1.2 0.99J NA NA NA NAStream #2 09/05/13 ND 1.1 0.53 3.4 ND ND ND NA NA NA NA
Stream #2 05/02/14 2.2 1.9 3.5 6.6 ND ND ND NA NA NA NAStream #2 09/23/14 1.4 1.6 13 11.3 ND ND 0.59 NA NA NA NAStream #2 12/01/15 1.66 1.76 2.74 J 5.96 ND 0.721 J ND NA NA NA NA
Stream #2 08/03/16 ND ND ND ND ND ND ND NA NA NA NAStream #2 12/21/17 ND 0.852 J 0.931 J 1.959 J ND ND ND NA NA NA NAStream #2 06/27/18 ND 1.32 0.906 J 3.923 J ND ND ND NA NA NA NAStream #2 03/25/19 ND 0.850 J 0.839 J 2.743 J ND ND ND NA NA NA NA
Stream #3
Stream #3 04/13/12 NS NS NS NS NS NS NS NS NS NS NS
Stream #3 08/16/12 ND ND ND ND ND ND ND NA NA NA NA
Stream #3 02/14/13 ND ND ND ND ND ND ND NA NA NA NA
Stream #3 09/05/13 ND ND ND ND ND ND ND NA NA NA NA
Stream #3 05/02/14 ND 0.15 J ND ND ND ND ND NA NA NA NA
Stream #3 09/23/14 ND ND 0.10 J ND ND ND ND NA NA NA NA
Stream #3 12/01/15 ND ND ND ND ND ND ND NA NA NA NA
Stream #3 08/03/16 ND ND ND ND ND ND ND NA NA NA NA
Stream #3 12/21/17 ND ND ND ND ND ND ND NA NA NA NA
Stream #3 06/27/18 ND ND ND ND ND ND ND NA NA NA NA
Stream #3 03/25/19 ND ND ND ND ND ND ND NA NA NA NA
NA - Not analyzed for this parameter DIPE - diisopropyl ether
NE - Standard not established * C9-C12 Aliphatics (VPH) only. See laboratory report.
NS - Not sampled ** C9-C10 Aromatics (VPH) only. See laboratory report.
All concentrations reported in ug/L - micrograms per liter J- Estimated Value
Bold values exceed NC Surface Water Quality Standards (NCSWQS) and EPA National Water Quality Criteria (NWQC)
Note: This table summarizes results for selected compounds. Additional compounds may have been detected. Refer to laboratory reports for additional information
MID-ATLANTIC PROJECT NO. 000R1760.18
2B NCSWQS or EPA NWQC
Diisopropyl
ether (DIPE)MTBE
TABLE 4.2
SUMMARY OF SURFACE WATER SAMPLING RESULTS FOR SELECTED COMPOUNDS
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
Total Xylenes C9-C12
Aliphatics
Sample
Location Sample Date Benzene Naphthalene
DWM INCIDENT NO.: 28414
Not sampled on prior dates
Not sampled on prior dates
Ethylbenzene Toluene C5-C8
Aliphatics
C9-C10
Aromatics
Lead
Not sampled on prior dates
LOCATION DATE TOC (ft)DTW (ft),
BTOC SWLE (ft)
ELEVATION
OF DITCH
BOTTOM (ft)
ELEVATION
DIFFERENCE*
(ft)MW-2 06/02/11 98.52 7.90 90.62 ---8.25
MW-2 08/29/11 98.52 8.45 90.07 ---7.70
MW-2 04/27/12 98.52 7.27 91.25 ---8.88
MW-2 08/16/12 98.52 8.39 90.13 ---7.76
MW-2 02/13/13 98.52 8.09 90.43 ---8.06
MW-2 09/05/13 98.52 8.32 90.20 ---7.83
MW-2 05/01/14 98.52 8.14 90.38 ---8.01
MW-2 09/23/14 98.52 8.51 90.01 ---7.64
MW-2 10/28/15 98.52 8.06 90.46 ---8.09
MW-11 08/29/11 93.21 9.84 83.37 ---1.00
MW-11 04/27/12 93.21 9.29 83.92 ---1.55
MW-11 08/16/12 93.21 9.52 83.69 ---1.32
MW-11 02/13/13 93.21 9.39 83.82 ---1.45
MW-11 09/05/13 93.21 9.62 83.59 ---1.22
MW-11 05/01/14 93.21 9.42 83.79 ---1.42
MW-11 09/23/14 93.21 9.72 83.49 ---1.12
MW-11 10/28/15 93.21 8.95 84.26 ---1.89
MW-11 08/03/16 93.21 9.62 83.59 ---1.22
MW-11 12/21/17 93.21 9.20 84.01 ---1.64
MW-11 06/27/18 93.21 9.20 84.01 ---1.64
MW-11 03/25/19 93.21 9.43 83.78 -1.41
MW-12 08/29/11 94.31 10.17 84.14 ---1.77
MW-12 04/27/12 94.31 9.74 84.57 ---2.20
MW-12 08/16/12 94.31 10.12 84.19 ---1.82
MW-12 02/13/13 94.31 9.88 84.43 ---2.06
MW-12 09/05/13 94.31 10.14 84.17 ---1.80
MW-12 05/01/14 94.31 9.94 84.37 ---2.00
MW-12 09/23/14 94.31 10.28 84.03 ---1.66
Stream #1 04/13/12 82.37
75 ft. south of
Stream #1 04/13/12 81.72
Notes:
BTOC - Below Top of Casing (TOC)
DTW - Depth to Water (in feet)
SWLE - Static Water Table Elevation (in feet)
*Elevation difference between the SWLE and the elevation of the drainage ditch bottom at STREAM #1 location
MID-ATLANTIC JOB NO. 000R1760.18
TABLE 4.3
ELEVATION COMPARISON OF THE WATER TABLE TO DRAINAGE DITCH
SPEEDWAY 7972 (FORMER WILCOHESS 353)
LENOIR, NORTH CAROLINA
DWM INCIDENT NO.: 28414

APPENDIX A

SELECTED HISTORICAL SITE ASSESSMENT DATA

APPENDIX B

MID-ATLANTIC FIELD PROCEDURES
Groundwater Sampling Procedures

I. Sample Collection

A. Monitoring Wells

Prior to sample collection, each well is purged of three to five standing well volumes or to
dryness to remove stagnant water from the well and well bore in an effort to collect
samples that are representative of the water quality in the formation surrounding each
well. Purging is performed either with a new, polyethylene bailer dedicated to each well, or
with a decontaminated pump. Samples are retrieved from the monitoring well using the
dedicated bailer. New nylon string is used on each dedicated bailer, and new nitrile
sampling gloves are donned prior to purging and sampling of each well.

B. Geoprobe “Screen Point Sampler”

The screen point sampler is a “grab” sampling device that is driven into the saturated zone
and a surrounding metal sheath is retracted, exposing a screen. Groundwater entering the
screen is then drawn to land surface through disposable tubing that is placed through the
hollow push rods. The sample is collected from the tubing into the appropriate sampling
glassware.

C. Water-Supply Wells

Water samples are typically collected from the available spigot that is nearest to the well.
The water is allowed to run at a high flow from the spigot for approximately 10 to 15
minutes to allow the water in the delivery lines to be purged. The sample flow is then
reduced and the samples are collected directly into pre-labeled containers as described
below. New nitrile sampling gloves are donned prior to sampling of each well.

D. Treatment System Influent/Effluent

Samples are typically collected from the influent or effluent of pump-and-treat groundwater
remediation systems using designated sampling ports in the influent and effluent water
transport lines. The water is typically allowed to run for several seconds to clear potential
debris in the sampling port. The sample is then collected directly into sampling containers
as described below. New nitrile sampling gloves are donned prior to sample collection.

II. Preparation for Laboratory Analysis

Groundwater samples are decanted directly into laboratory-prepared, pre-labeled, sampling
containers, packed in ice, and shipped to a certified laboratory under chain-of-custody control.
Laboratory analyses performed on the samples are specified on the chain-of-custody.

Groundwater Flow Direction Determination Procedure

I. Well Casing Rim Elevation Determination

After well completion, a measuring point is marked on the rim of each well casing by field
personnel. A survey level and stadia rod is used to determine the vertical elevation of the
measuring point relative to a designated site benchmark. The elevations are determined to the
nearest 0.01 foot.

II. Depth-to-Groundwater Measurements

Prior to collecting depth-to-water measurements, the field technician opens the locking well
plugs and allows the water table to “stabilize” within the well. The technician then uses an
electronic water level indicator (or oil/water interface probe, if free product is present) to
measure the depth-to-water from the measuring point on the casing rim to the nearest 0.01
foot. The measured depths-to-water are then subtracted from the casing elevations to
determine water level elevations relative to the benchmark.

III. Horizontal Flow Direction Determination

Horizontal groundwater flow direction in the surficial aquifer is determined by development of a
water table contour map based upon water table elevation data obtained from site monitoring
wells. The water levels measured in deep, Type III monitoring wells are not used in
constructing the water table map. Mid-Atlantic uses Golden Software’s “Surfer” version 7.0 to
generate the contours using the Kriging method. Alternatively, the water-table contour map
may be hand drawn by Mid-Atlantic staff and then digitized by AutoCAD software.
Groundwater flow direction is determined by interpreting the contours. Groundwater will flow in
the direction from higher elevation to lower elevation (perpendicular to the generated
contours).

IV. Vertical Flow Direction Determination

Groundwater exhibits both horizontal and vertical components of flow through an aquifer. The
hydraulic gradient is the difference in hydraulic head divided by the distance along the flow
path. The vertical gradient may be either up or down within the aquifer.

The vertical gradient is calculated using measurements obtained from a “paired” shallow
monitoring well and a deep, Type III monitoring well. The gradient is calculated by first
determining the difference in the static water level elevations at the well pair. Second, the
relative elevation of the middle of the screened interval is determined for each well pair.
Finally, the difference in the static water level elevations at each well pair is divided by the
difference in the mid-screen elevations for the well pair. This value is arbitrarily assigned a
positive value if the groundwater is moving vertically downward (recharge area) and a negative
value if the groundwater is moving vertically upward (discharge area). Groundwater will flow in
the direction from higher elevation to lower elevation.
Hydraulic Gradient Determination Procedure

The hydraulic gradient, which is a measure of the “steepness” of the water table, is
determined by dividing the change in the elevation (in feet) of the water table over the
change in horizontal distance (in feet) between two measuring points. Typically, the
gradient is determined after the Water Table Elevation Contour Map is prepared. Two
wells are typically selected that, when a line is drawn between the wells, the orientation of
this line approximates the direction of groundwater flow. The greater the horizontal
distance between the lines, the more representative the hydraulic gradient value will be for
the site. If two wells are not arranged in line with groundwater flow, the hydraulic gradient
can be estimated by performing the same calculation using the contours generated for the
groundwater flow direction map. The units for the hydraulic gradient are feet/feet.

The hydraulic gradient (measured from MW-8 to MW-15) for the subject site was
determined as follows:

Gradient = dh/dl = (91.13 – 83.97) / 102 = 0.070 ft/ft

where:

dh = change in head (more specifically, water table elevation) in feet
dl = horizontal distance (in feet) between monitoring wells or other head measurement
points.

APPENDIX C

LABORATORY ANALYTICAL REPORT AND
CHAIN-OF-CUSTODY RECORD

ANALYTICAL REPORT
April 02, 2019
Mid-Atlantic - Speedway NC
Sample Delivery Group:L1082504
Samples Received:03/26/2019
Project Number:R1760.18A
Description:Speedway #7972
Site:7972
Report To:Mr. Patrick Kelly
409 Rogers View Court
Raleigh, NC 27610
Entire Report Reviewed By:
April 02, 2019
[Preliminary Report]
T. Alan Harvill
Project Manager
Results relate only to the items tested or calibrated and are reported as rounded values. This test report shall not be
reproduced, except in full, without written approval of the laboratory. Where applicable, sampling conducted by Pace National
is performed per guidance provided in laboratory standard operating procedures: 060302, 060303, and 060304.
12065 Lebanon Rd Mount Juliet, TN 37122 615-758-5858 800-767-5859 www.pacenational.com
April 02, 2019
T. Alan Harvill
Project Manager
ONE LAB. NATIONWIDE.TABLE OF CONTENTS
Cp: Cover Page 1
Tc: Table of Contents 2
Ss: Sample Summary 3
Cn: Case Narrative 5
Sr: Sample Results 6
TRIP BLANK L1082504-01 6
EQUIPMENT RINSE BLANK L1082504-02 8
MW-01 L1082504-03 10
MW-03 L1082504-04 12
MW-08 L1082504-05 14
MW-11 L1082504-06 16
MW-15 L1082504-07 18
MW-16 L1082504-08 20
STREAM #1 L1082504-09 22
STREAM #2 L1082504-10 24
STREAM #3 L1082504-11 26
Qc: Quality Control Summary 28
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 28
Gl: Glossary of Terms 36
Al: Accreditations & Locations 37
Sc: Sample Chain of Custody 38
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 2 of 42
ONE LAB. NATIONWIDE.SAMPLE SUMMARY
Collected by Collected date/time Received date/time
TRIP BLANK L1082504-01 GW Gary A. Fischer 03/25/19 00:00 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 15:40 03/30/19 15:40 ACG Mt. Juliet, TN
Collected by Collected date/time Received date/time
EQUIPMENT RINSE BLANK L1082504-02 GW Gary A. Fischer 03/25/19 00:00 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 15:59 03/30/19 15:59 ACG Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-01 L1082504-03 GW Gary A. Fischer 03/25/19 11:50 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258489 10 03/31/19 15:29 03/31/19 15:29 CAH Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-03 L1082504-04 GW Gary A. Fischer 03/25/19 08:50 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 17:37 03/30/19 17:37 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258489 1 03/31/19 13:00 03/31/19 13:00 CAH Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-08 L1082504-05 GW Gary A. Fischer 03/25/19 11:15 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 17:57 03/30/19 17:57 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258489 50 03/31/19 15:51 03/31/19 15:51 CAH Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-11 L1082504-06 GW Gary A. Fischer 03/25/19 09:15 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 18:16 03/30/19 18:16 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258489 1 03/31/19 13:21 03/31/19 13:21 CAH Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-15 L1082504-07 GW Gary A. Fischer 03/25/19 10:20 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 18:36 03/30/19 18:36 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258489 1 03/31/19 13:42 03/31/19 13:42 CAH Mt. Juliet, TN
Collected by Collected date/time Received date/time
MW-16 L1082504-08 GW Gary A. Fischer 03/25/19 09:45 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 18:56 03/30/19 18:56 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258489 20 03/31/19 16:12 03/31/19 16:12 CAH Mt. Juliet, TN
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
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ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 3 of 42
ONE LAB. NATIONWIDE.SAMPLE SUMMARY
Collected by Collected date/time Received date/time
STREAM #1 L1082504-09 GW Gary A. Fischer 03/25/19 08:00 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 19:16 03/30/19 19:16 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258489 1 03/31/19 14:04 03/31/19 14:04 CAH Mt. Juliet, TN
Collected by Collected date/time Received date/time
STREAM #2 L1082504-10 GW Gary A. Fischer 03/25/19 10:50 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 19:36 03/30/19 19:36 ACG Mt. Juliet, TN
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258489 1 03/31/19 14:25 03/31/19 14:25 CAH Mt. Juliet, TN
Collected by Collected date/time Received date/time
STREAM #3 L1082504-11 GW Gary A. Fischer 03/25/19 08:15 03/26/19 08:45
Method Batch Dilution Preparation Analysis Analyst Location
date/time date/time
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 WG1258292 1 03/30/19 19:55 03/30/19 19:55 ACG Mt. Juliet, TN
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 4 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 4 of 42
ONE LAB. NATIONWIDE.CASE NARRATIVE
All sample aliquots were received at the correct temperature, in the proper containers, with the
appropriate preservatives, and within method specified holding times, unless qualified or notated within
the report. Where applicable, all MDL (LOD) and RDL (LOQ) values reported for environmental samples
have been corrected for the dilution factor used in the analysis. All Method and Batch Quality Control
are within established criteria except where addressed in this case narrative, a non-conformance form
or properly qualified within the sample results. By my digital signature below, I affirm to the best of my
knowledge, all problems/anomalies observed by the laboratory as having the potential to affect the
quality of the data have been identified by the laboratory, and no information or data have been
knowingly withheld that would affect the quality of the data.
[Preliminary Report]
T. Alan Harvill
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 5 of 42
T. Alan Harvill
Project Manager
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 5 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 01
L1082504
TRIP BLANK
Collected date/time: 03/25/19 00:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 15:40 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 15:40 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 15:40 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 15:40 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 15:40 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 15:40 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 15:40 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 15:40 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 15:40 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 15:40 WG1258292
1,2,4-Trimethylbenzene U 0.373 1.00 1 03/30/2019 15:40 WG1258292
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 15:40 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 15:40 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 15:40 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 15:40 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 15:40 WG1258292
1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2019 15:40 WG1258292
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 15:40 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 15:40 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 15:40 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 15:40 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 15:40 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 15:40 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 15:40 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 15:40 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 15:40 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 15:40 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 15:40 WG1258292
Benzene U 0.331 1.00 1 03/30/2019 15:40 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 15:40 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 15:40 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 15:40 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 15:40 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 15:40 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 15:40 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 15:40 WG1258292
Chloroform U 0.324 5.00 1 03/30/2019 15:40 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 15:40 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 15:40 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 15:40 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 15:40 WG1258292
Di-isopropyl ether U 0.320 1.00 1 03/30/2019 15:40 WG1258292
Ethylbenzene U 0.384 1.00 1 03/30/2019 15:40 WG1258292
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 15:40 WG1258292
Isopropylbenzene U 0.326 1.00 1 03/30/2019 15:40 WG1258292
Methyl tert-butyl ether U 0.367 1.00 1 03/30/2019 15:40 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 15:40 WG1258292
Naphthalene U 1.00 5.00 1 03/30/2019 15:40 WG1258292
Styrene U 0.307 1.00 1 03/30/2019 15:40 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 15:40 WG1258292
Toluene U 0.412 1.00 1 03/30/2019 15:40 WG1258292
Trichloroethene U 0.398 1.00 1 03/30/2019 15:40 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 15:40 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 15:40 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 15:40 WG1258292
m&p-Xylenes U 0.719 2.00 1 03/30/2019 15:40 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 6 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 6 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 01
L1082504
TRIP BLANK
Collected date/time: 03/25/19 00:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U 0.361 1.00 1 03/30/2019 15:40 WG1258292
n-Propylbenzene U 0.349 1.00 1 03/30/2019 15:40 WG1258292
o-Xylene U 0.341 1.00 1 03/30/2019 15:40 WG1258292
p-Isopropyltoluene U 0.350 1.00 1 03/30/2019 15:40 WG1258292
sec-Butylbenzene U 0.365 1.00 1 03/30/2019 15:40 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 15:40 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 15:40 WG1258292
(S) Toluene-d8 101 80.0-120 03/30/2019 15:40 WG1258292
(S) a,a,a-Trifluorotoluene 96.3 80.0-120 03/30/2019 15:40 WG1258292
(S) 4-Bromofluorobenzene 94.3 77.0-126 03/30/2019 15:40 WG1258292
(S) 1,2-Dichloroethane-d4 108 70.0-130 03/30/2019 15:40 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 7 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 7 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 02
L1082504
EQUIPMENT RINSE BLANK
Collected date/time: 03/25/19 00:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 15:59 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 15:59 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 15:59 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 15:59 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 15:59 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 15:59 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 15:59 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 15:59 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 15:59 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 15:59 WG1258292
1,2,4-Trimethylbenzene U 0.373 1.00 1 03/30/2019 15:59 WG1258292
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 15:59 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 15:59 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 15:59 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 15:59 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 15:59 WG1258292
1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2019 15:59 WG1258292
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 15:59 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 15:59 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 15:59 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 15:59 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 15:59 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 15:59 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 15:59 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 15:59 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 15:59 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 15:59 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 15:59 WG1258292
Benzene U 0.331 1.00 1 03/30/2019 15:59 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 15:59 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 15:59 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 15:59 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 15:59 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 15:59 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 15:59 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 15:59 WG1258292
Chloroform U 0.324 5.00 1 03/30/2019 15:59 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 15:59 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 15:59 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 15:59 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 15:59 WG1258292
Di-isopropyl ether U 0.320 1.00 1 03/30/2019 15:59 WG1258292
Ethylbenzene U 0.384 1.00 1 03/30/2019 15:59 WG1258292
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 15:59 WG1258292
Isopropylbenzene U 0.326 1.00 1 03/30/2019 15:59 WG1258292
Methyl tert-butyl ether U 0.367 1.00 1 03/30/2019 15:59 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 15:59 WG1258292
Naphthalene U 1.00 5.00 1 03/30/2019 15:59 WG1258292
Styrene U 0.307 1.00 1 03/30/2019 15:59 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 15:59 WG1258292
Toluene U 0.412 1.00 1 03/30/2019 15:59 WG1258292
Trichloroethene U 0.398 1.00 1 03/30/2019 15:59 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 15:59 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 15:59 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 15:59 WG1258292
m&p-Xylenes U 0.719 2.00 1 03/30/2019 15:59 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 8 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 8 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 02
L1082504
EQUIPMENT RINSE BLANK
Collected date/time: 03/25/19 00:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U 0.361 1.00 1 03/30/2019 15:59 WG1258292
n-Propylbenzene U 0.349 1.00 1 03/30/2019 15:59 WG1258292
o-Xylene U 0.341 1.00 1 03/30/2019 15:59 WG1258292
p-Isopropyltoluene U 0.350 1.00 1 03/30/2019 15:59 WG1258292
sec-Butylbenzene U 0.365 1.00 1 03/30/2019 15:59 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 15:59 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 15:59 WG1258292
(S) Toluene-d8 99.9 80.0-120 03/30/2019 15:59 WG1258292
(S) a,a,a-Trifluorotoluene 95.2 80.0-120 03/30/2019 15:59 WG1258292
(S) 4-Bromofluorobenzene 95.1 77.0-126 03/30/2019 15:59 WG1258292
(S) 1,2-Dichloroethane-d4 108 70.0-130 03/30/2019 15:59 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 9 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 9 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 03
L1082504
MW-01
Collected date/time: 03/25/19 11:50
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 3.85 10.0 10 03/31/2019 15:29 WG1258489
1,1,1-Trichloroethane U 3.19 10.0 10 03/31/2019 15:29 WG1258489
1,1,2,2-Tetrachloroethane U 1.30 10.0 10 03/31/2019 15:29 WG1258489
1,1,2-Trichloroethane U 3.83 10.0 10 03/31/2019 15:29 WG1258489
1,1-Dichloroethane U 2.59 10.0 10 03/31/2019 15:29 WG1258489
1,1-Dichloroethene U 3.98 10.0 10 03/31/2019 15:29 WG1258489
1,1-Dichloropropene U 3.52 10.0 10 03/31/2019 15:29 WG1258489
1,2,3-Trichlorobenzene U 2.30 10.0 10 03/31/2019 15:29 WG1258489
1,2,3-Trichloropropane U 8.07 25.0 10 03/31/2019 15:29 WG1258489
1,2,4-Trichlorobenzene U 3.55 10.0 10 03/31/2019 15:29 WG1258489
1,2,4-Trimethylbenzene 487 3.73 10.0 10 03/31/2019 15:29 WG1258489
1,2-Dibromo-3-Chloropropane U 13.3 50.0 10 03/31/2019 15:29 WG1258489
1,2-Dibromoethane U 3.81 10.0 10 03/31/2019 15:29 WG1258489
1,2-Dichlorobenzene U 3.49 10.0 10 03/31/2019 15:29 WG1258489
1,2-Dichloroethane U 3.61 10.0 10 03/31/2019 15:29 WG1258489
1,2-Dichloropropane U 3.06 10.0 10 03/31/2019 15:29 WG1258489
1,3,5-Trimethylbenzene U 3.87 10.0 10 03/31/2019 15:29 WG1258489
1,3-Dichlorobenzene U 2.20 10.0 10 03/31/2019 15:29 WG1258489
1,3-Dichloropropane U 3.66 10.0 10 03/31/2019 15:29 WG1258489
1,4-Dichlorobenzene U 2.74 10.0 10 03/31/2019 15:29 WG1258489
2,2-Dichloropropane U 3.21 10.0 10 03/31/2019 15:29 WG1258489
2-Butanone (MEK)U 39.3 100 10 03/31/2019 15:29 WG1258489
2-Chlorotoluene U 3.75 10.0 10 03/31/2019 15:29 WG1258489
4-Chlorotoluene U 3.51 10.0 10 03/31/2019 15:29 WG1258489
4-Methyl-2-pentanone (MIBK)U 21.4 100 10 03/31/2019 15:29 WG1258489
Acetone U 100 500 10 03/31/2019 15:29 WG1258489
Acrolein U 88.7 500 10 03/31/2019 15:29 WG1258489
Acrylonitrile U 18.7 100 10 03/31/2019 15:29 WG1258489
Benzene 182 V3 3.31 10.0 10 03/31/2019 15:29 WG1258489
Bromobenzene U 3.52 10.0 10 03/31/2019 15:29 WG1258489
Bromodichloromethane U 3.80 10.0 10 03/31/2019 15:29 WG1258489
Bromoform U 4.69 10.0 10 03/31/2019 15:29 WG1258489
Bromomethane U 8.66 50.0 10 03/31/2019 15:29 WG1258489
Carbon tetrachloride U 3.79 10.0 10 03/31/2019 15:29 WG1258489
Chlorobenzene U 3.48 10.0 10 03/31/2019 15:29 WG1258489
Chloroethane U 4.53 50.0 10 03/31/2019 15:29 WG1258489
Chloroform U 3.24 50.0 10 03/31/2019 15:29 WG1258489
Chloromethane U 2.76 25.0 10 03/31/2019 15:29 WG1258489
Chlorodibromomethane U 3.27 10.0 10 03/31/2019 15:29 WG1258489
Dibromomethane U 3.46 10.0 10 03/31/2019 15:29 WG1258489
Dichlorodifluoromethane U 5.51 50.0 10 03/31/2019 15:29 WG1258489
Di-isopropyl ether 40.7 V3 3.20 10.0 10 03/31/2019 15:29 WG1258489
Ethylbenzene 503 3.84 10.0 10 03/31/2019 15:29 WG1258489
Hexachloro-1,3-butadiene U 2.56 10.0 10 03/31/2019 15:29 WG1258489
Isopropylbenzene 32.6 3.26 10.0 10 03/31/2019 15:29 WG1258489
Methyl tert-butyl ether 23.9 V3 3.67 10.0 10 03/31/2019 15:29 WG1258489
Methylene Chloride U 10.0 50.0 10 03/31/2019 15:29 WG1258489
Naphthalene 114 10.0 50.0 10 03/31/2019 15:29 WG1258489
Styrene U 3.07 10.0 10 03/31/2019 15:29 WG1258489
Tetrachloroethene U 3.72 10.0 10 03/31/2019 15:29 WG1258489
Toluene U 4.12 10.0 10 03/31/2019 15:29 WG1258489
Trichloroethene U 3.98 10.0 10 03/31/2019 15:29 WG1258489
Trichlorofluoromethane U 12.0 50.0 10 03/31/2019 15:29 WG1258489
Vinyl chloride U 2.59 10.0 10 03/31/2019 15:29 WG1258489
cis-1,2-Dichloroethene U 2.60 10.0 10 03/31/2019 15:29 WG1258489
m&p-Xylenes U 7.19 20.0 10 03/31/2019 15:29 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 10 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 10 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 03
L1082504
MW-01
Collected date/time: 03/25/19 11:50
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene 9.98 J 3.61 10.0 10 03/31/2019 15:29 WG1258489
n-Propylbenzene 142 3.49 10.0 10 03/31/2019 15:29 WG1258489
o-Xylene U 3.41 10.0 10 03/31/2019 15:29 WG1258489
p-Isopropyltoluene 4.60 J 3.50 10.0 10 03/31/2019 15:29 WG1258489
sec-Butylbenzene 9.54 J 3.65 10.0 10 03/31/2019 15:29 WG1258489
tert-Butylbenzene U 3.99 10.0 10 03/31/2019 15:29 WG1258489
trans-1,2-Dichloroethene U 3.96 10.0 10 03/31/2019 15:29 WG1258489
(S) Toluene-d8 90.3 80.0-120 03/31/2019 15:29 WG1258489
(S) a,a,a-Trifluorotoluene 132 J1 80.0-120 03/31/2019 15:29 WG1258489
(S) 4-Bromofluorobenzene 89.2 77.0-126 03/31/2019 15:29 WG1258489
(S) 1,2-Dichloroethane-d4 101 70.0-130 03/31/2019 15:29 WG1258489
Sample Narrative:
L1082504-03 WG1258489: Previous run also had low IS/SURR recovery. Matrix effect.
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 11 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 11 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 04
L1082504
MW-03
Collected date/time: 03/25/19 08:50
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 17:37 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 17:37 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 17:37 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 17:37 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 17:37 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 17:37 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 17:37 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 17:37 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 17:37 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 17:37 WG1258292
1,2,4-Trimethylbenzene U 0.373 1.00 1 03/31/2019 13:00 WG1258489
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 17:37 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 17:37 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 17:37 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 17:37 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 17:37 WG1258292
1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2019 17:37 WG1258292
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 17:37 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 17:37 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 17:37 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 17:37 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 17:37 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 17:37 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 17:37 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 17:37 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 17:37 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 17:37 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 17:37 WG1258292
Benzene U 0.331 1.00 1 03/30/2019 17:37 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 17:37 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 17:37 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 17:37 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 17:37 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 17:37 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 17:37 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 17:37 WG1258292
Chloroform 1.24 J 0.324 5.00 1 03/30/2019 17:37 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 17:37 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 17:37 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 17:37 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 17:37 WG1258292
Di-isopropyl ether U 0.320 1.00 1 03/30/2019 17:37 WG1258292
Ethylbenzene U 0.384 1.00 1 03/31/2019 13:00 WG1258489
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 17:37 WG1258292
Isopropylbenzene U 0.326 1.00 1 03/30/2019 17:37 WG1258292
Methyl tert-butyl ether U 0.367 1.00 1 03/30/2019 17:37 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 17:37 WG1258292
Naphthalene 1.78 J 1.00 5.00 1 03/30/2019 17:37 WG1258292
Styrene U 0.307 1.00 1 03/30/2019 17:37 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 17:37 WG1258292
Toluene U 0.412 1.00 1 03/30/2019 17:37 WG1258292
Trichloroethene U 0.398 1.00 1 03/30/2019 17:37 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 17:37 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 17:37 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 17:37 WG1258292
m&p-Xylenes U 0.719 2.00 1 03/30/2019 17:37 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 12 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 12 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 04
L1082504
MW-03
Collected date/time: 03/25/19 08:50
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U 0.361 1.00 1 03/30/2019 17:37 WG1258292
n-Propylbenzene U 0.349 1.00 1 03/30/2019 17:37 WG1258292
o-Xylene U 0.341 1.00 1 03/30/2019 17:37 WG1258292
p-Isopropyltoluene U 0.350 1.00 1 03/30/2019 17:37 WG1258292
sec-Butylbenzene U 0.365 1.00 1 03/30/2019 17:37 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 17:37 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 17:37 WG1258292
(S) Toluene-d8 101 80.0-120 03/30/2019 17:37 WG1258292
(S) Toluene-d8 99.8 80.0-120 03/31/2019 13:00 WG1258489
(S) a,a,a-Trifluorotoluene 95.4 80.0-120 03/30/2019 17:37 WG1258292
(S) a,a,a-Trifluorotoluene 102 80.0-120 03/31/2019 13:00 WG1258489
(S) 4-Bromofluorobenzene 97.8 77.0-126 03/30/2019 17:37 WG1258292
(S) 4-Bromofluorobenzene 90.5 77.0-126 03/31/2019 13:00 WG1258489
(S) 1,2-Dichloroethane-d4 107 70.0-130 03/30/2019 17:37 WG1258292
(S) 1,2-Dichloroethane-d4 99.2 70.0-130 03/31/2019 13:00 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 13 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 13 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 05
L1082504
MW-08
Collected date/time: 03/25/19 11:15
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 17:57 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 17:57 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 17:57 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 17:57 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 17:57 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 17:57 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 17:57 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 17:57 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 17:57 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 17:57 WG1258292
1,2,4-Trimethylbenzene 1500 18.6 50.0 50 03/31/2019 15:51 WG1258489
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 17:57 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 17:57 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 17:57 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 17:57 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 17:57 WG1258292
1,3,5-Trimethylbenzene 356 19.4 50.0 50 03/31/2019 15:51 WG1258489
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 17:57 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 17:57 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 17:57 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 17:57 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 17:57 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 17:57 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 17:57 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 17:57 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 17:57 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 17:57 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 17:57 WG1258292
Benzene 418 16.6 50.0 50 03/31/2019 15:51 WG1258489
Bromobenzene U 0.352 1.00 1 03/30/2019 17:57 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 17:57 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 17:57 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 17:57 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 17:57 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 17:57 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 17:57 WG1258292
Chloroform 3.88 J 0.324 5.00 1 03/30/2019 17:57 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 17:57 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 17:57 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 17:57 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 17:57 WG1258292
Di-isopropyl ether 46.9 0.320 1.00 1 03/30/2019 17:57 WG1258292
Ethylbenzene 668 19.2 50.0 50 03/31/2019 15:51 WG1258489
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 17:57 WG1258292
Isopropylbenzene 41.5 0.326 1.00 1 03/30/2019 17:57 WG1258292
Methyl tert-butyl ether 7.75 0.367 1.00 1 03/30/2019 17:57 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 17:57 WG1258292
Naphthalene 386 50.0 250 50 03/31/2019 15:51 WG1258489
Styrene U 0.307 1.00 1 03/30/2019 17:57 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 17:57 WG1258292
Toluene 1090 20.6 50.0 50 03/31/2019 15:51 WG1258489
Trichloroethene U 0.398 1.00 1 03/30/2019 17:57 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 17:57 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 17:57 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 17:57 WG1258292
m&p-Xylenes 1970 36.0 100 50 03/31/2019 15:51 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 14 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 14 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 05
L1082504
MW-08
Collected date/time: 03/25/19 11:15
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene 13.9 0.361 1.00 1 03/30/2019 17:57 WG1258292
n-Propylbenzene 181 0.349 1.00 1 03/30/2019 17:57 WG1258292
o-Xylene 517 17.0 50.0 50 03/31/2019 15:51 WG1258489
p-Isopropyltoluene 5.05 0.350 1.00 1 03/30/2019 17:57 WG1258292
sec-Butylbenzene 9.51 0.365 1.00 1 03/30/2019 17:57 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 17:57 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 17:57 WG1258292
(S) Toluene-d8 93.8 80.0-120 03/30/2019 17:57 WG1258292
(S) Toluene-d8 94.0 80.0-120 03/31/2019 15:51 WG1258489
(S) a,a,a-Trifluorotoluene 71.9 J2 80.0-120 03/30/2019 17:57 WG1258292
(S) a,a,a-Trifluorotoluene 98.1 80.0-120 03/31/2019 15:51 WG1258489
(S) 4-Bromofluorobenzene 90.0 77.0-126 03/30/2019 17:57 WG1258292
(S) 4-Bromofluorobenzene 91.4 77.0-126 03/31/2019 15:51 WG1258489
(S) 1,2-Dichloroethane-d4 121 70.0-130 03/30/2019 17:57 WG1258292
(S) 1,2-Dichloroethane-d4 97.0 70.0-130 03/31/2019 15:51 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 15 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 15 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 06
L1082504
MW-11
Collected date/time: 03/25/19 09:15
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 18:16 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 18:16 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 18:16 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 18:16 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 18:16 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 18:16 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 18:16 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 18:16 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 18:16 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 18:16 WG1258292
1,2,4-Trimethylbenzene U 0.373 1.00 1 03/31/2019 13:21 WG1258489
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 18:16 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 18:16 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 18:16 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 18:16 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 18:16 WG1258292
1,3,5-Trimethylbenzene U 0.387 1.00 1 03/31/2019 13:21 WG1258489
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 18:16 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 18:16 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 18:16 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 18:16 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 18:16 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 18:16 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 18:16 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 18:16 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 18:16 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 18:16 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 18:16 WG1258292
Benzene U 0.331 1.00 1 03/30/2019 18:16 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 18:16 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 18:16 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 18:16 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 18:16 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 18:16 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 18:16 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 18:16 WG1258292
Chloroform U 0.324 5.00 1 03/30/2019 18:16 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 18:16 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 18:16 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 18:16 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 18:16 WG1258292
Di-isopropyl ether U 0.320 1.00 1 03/30/2019 18:16 WG1258292
Ethylbenzene U 0.384 1.00 1 03/31/2019 13:21 WG1258489
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 18:16 WG1258292
Isopropylbenzene U 0.326 1.00 1 03/30/2019 18:16 WG1258292
Methyl tert-butyl ether U 0.367 1.00 1 03/30/2019 18:16 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 18:16 WG1258292
Naphthalene U 1.00 5.00 1 03/31/2019 13:21 WG1258489
Styrene U 0.307 1.00 1 03/30/2019 18:16 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 18:16 WG1258292
Toluene U 0.412 1.00 1 03/31/2019 13:21 WG1258489
Trichloroethene U 0.398 1.00 1 03/30/2019 18:16 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 18:16 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 18:16 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 18:16 WG1258292
m&p-Xylenes U 0.719 2.00 1 03/31/2019 13:21 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 16 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 16 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 06
L1082504
MW-11
Collected date/time: 03/25/19 09:15
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U 0.361 1.00 1 03/30/2019 18:16 WG1258292
n-Propylbenzene 0.355 J 0.349 1.00 1 03/30/2019 18:16 WG1258292
o-Xylene U 0.341 1.00 1 03/31/2019 13:21 WG1258489
p-Isopropyltoluene U 0.350 1.00 1 03/30/2019 18:16 WG1258292
sec-Butylbenzene U 0.365 1.00 1 03/30/2019 18:16 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 18:16 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 18:16 WG1258292
(S) Toluene-d8 99.5 80.0-120 03/30/2019 18:16 WG1258292
(S) Toluene-d8 102 80.0-120 03/31/2019 13:21 WG1258489
(S) a,a,a-Trifluorotoluene 96.3 80.0-120 03/30/2019 18:16 WG1258292
(S) a,a,a-Trifluorotoluene 100 80.0-120 03/31/2019 13:21 WG1258489
(S) 4-Bromofluorobenzene 96.2 77.0-126 03/30/2019 18:16 WG1258292
(S) 4-Bromofluorobenzene 92.2 77.0-126 03/31/2019 13:21 WG1258489
(S) 1,2-Dichloroethane-d4 105 70.0-130 03/30/2019 18:16 WG1258292
(S) 1,2-Dichloroethane-d4 102 70.0-130 03/31/2019 13:21 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 17 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 17 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 07
L1082504
MW-15
Collected date/time: 03/25/19 10:20
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 18:36 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 18:36 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 18:36 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 18:36 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 18:36 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 18:36 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 18:36 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 18:36 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 18:36 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 18:36 WG1258292
1,2,4-Trimethylbenzene 12.5 0.373 1.00 1 03/30/2019 18:36 WG1258292
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 18:36 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 18:36 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 18:36 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 18:36 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 18:36 WG1258292
1,3,5-Trimethylbenzene 2.07 0.387 1.00 1 03/30/2019 18:36 WG1258292
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 18:36 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 18:36 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 18:36 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 18:36 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 18:36 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 18:36 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 18:36 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 18:36 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 18:36 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 18:36 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 18:36 WG1258292
Benzene 128 0.331 1.00 1 03/30/2019 18:36 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 18:36 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 18:36 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 18:36 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 18:36 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 18:36 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 18:36 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 18:36 WG1258292
Chloroform U 0.324 5.00 1 03/30/2019 18:36 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 18:36 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 18:36 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 18:36 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 18:36 WG1258292
Di-isopropyl ether 1.55 0.320 1.00 1 03/30/2019 18:36 WG1258292
Ethylbenzene 20.0 0.384 1.00 1 03/30/2019 18:36 WG1258292
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 18:36 WG1258292
Isopropylbenzene 4.71 0.326 1.00 1 03/30/2019 18:36 WG1258292
Methyl tert-butyl ether 23.8 0.367 1.00 1 03/30/2019 18:36 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 18:36 WG1258292
Naphthalene 3.48 J 1.00 5.00 1 03/31/2019 13:42 WG1258489
Styrene 0.431 J 0.307 1.00 1 03/30/2019 18:36 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 18:36 WG1258292
Toluene 6.67 0.412 1.00 1 03/30/2019 18:36 WG1258292
Trichloroethene U 0.398 1.00 1 03/30/2019 18:36 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 18:36 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 18:36 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 18:36 WG1258292
m&p-Xylenes 7.24 0.719 2.00 1 03/30/2019 18:36 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 18 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 18 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 07
L1082504
MW-15
Collected date/time: 03/25/19 10:20
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene 1.62 0.361 1.00 1 03/30/2019 18:36 WG1258292
n-Propylbenzene 4.26 0.349 1.00 1 03/30/2019 18:36 WG1258292
o-Xylene 5.05 0.341 1.00 1 03/30/2019 18:36 WG1258292
p-Isopropyltoluene 0.356 J 0.350 1.00 1 03/30/2019 18:36 WG1258292
sec-Butylbenzene 2.64 0.365 1.00 1 03/30/2019 18:36 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 18:36 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 18:36 WG1258292
(S) Toluene-d8 95.0 80.0-120 03/30/2019 18:36 WG1258292
(S) Toluene-d8 104 80.0-120 03/31/2019 13:42 WG1258489
(S) a,a,a-Trifluorotoluene 88.4 80.0-120 03/30/2019 18:36 WG1258292
(S) a,a,a-Trifluorotoluene 91.6 80.0-120 03/31/2019 13:42 WG1258489
(S) 4-Bromofluorobenzene 94.8 77.0-126 03/30/2019 18:36 WG1258292
(S) 4-Bromofluorobenzene 102 77.0-126 03/31/2019 13:42 WG1258489
(S) 1,2-Dichloroethane-d4 115 70.0-130 03/30/2019 18:36 WG1258292
(S) 1,2-Dichloroethane-d4 108 70.0-130 03/31/2019 13:42 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 19 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 19 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 08
L1082504
MW-16
Collected date/time: 03/25/19 09:45
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 18:56 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 18:56 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 18:56 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 18:56 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 18:56 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 18:56 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 18:56 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 18:56 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 18:56 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 18:56 WG1258292
1,2,4-Trimethylbenzene 711 7.46 20.0 20 03/31/2019 16:12 WG1258489
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 18:56 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 18:56 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 18:56 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 18:56 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 18:56 WG1258292
1,3,5-Trimethylbenzene 167 0.387 1.00 1 03/30/2019 18:56 WG1258292
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 18:56 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 18:56 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 18:56 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 18:56 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 18:56 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 18:56 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 18:56 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 18:56 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 18:56 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 18:56 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 18:56 WG1258292
Benzene 2.05 0.331 1.00 1 03/30/2019 18:56 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 18:56 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 18:56 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 18:56 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 18:56 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 18:56 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 18:56 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 18:56 WG1258292
Chloroform U 0.324 5.00 1 03/30/2019 18:56 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 18:56 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 18:56 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 18:56 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 18:56 WG1258292
Di-isopropyl ether U 0.320 1.00 1 03/30/2019 18:56 WG1258292
Ethylbenzene 98.2 0.384 1.00 1 03/30/2019 18:56 WG1258292
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 18:56 WG1258292
Isopropylbenzene 22.5 0.326 1.00 1 03/30/2019 18:56 WG1258292
Methyl tert-butyl ether U 0.367 1.00 1 03/30/2019 18:56 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 18:56 WG1258292
Naphthalene 79.1 1.00 5.00 1 03/30/2019 18:56 WG1258292
Styrene U 0.307 1.00 1 03/30/2019 18:56 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 18:56 WG1258292
Toluene 0.643 J 0.412 1.00 1 03/30/2019 18:56 WG1258292
Trichloroethene U 0.398 1.00 1 03/30/2019 18:56 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 18:56 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 18:56 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 18:56 WG1258292
m&p-Xylenes 324 0.719 2.00 1 03/30/2019 18:56 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 20 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 20 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 08
L1082504
MW-16
Collected date/time: 03/25/19 09:45
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene 4.95 0.361 1.00 1 03/30/2019 18:56 WG1258292
n-Propylbenzene 99.9 0.349 1.00 1 03/30/2019 18:56 WG1258292
o-Xylene 114 0.341 1.00 1 03/30/2019 18:56 WG1258292
p-Isopropyltoluene 8.53 0.350 1.00 1 03/30/2019 18:56 WG1258292
sec-Butylbenzene 4.15 0.365 1.00 1 03/30/2019 18:56 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 18:56 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 18:56 WG1258292
(S) Toluene-d8 98.1 80.0-120 03/30/2019 18:56 WG1258292
(S) Toluene-d8 98.5 80.0-120 03/31/2019 16:12 WG1258489
(S) a,a,a-Trifluorotoluene 88.4 80.0-120 03/30/2019 18:56 WG1258292
(S) a,a,a-Trifluorotoluene 96.3 80.0-120 03/31/2019 16:12 WG1258489
(S) 4-Bromofluorobenzene 87.0 77.0-126 03/30/2019 18:56 WG1258292
(S) 4-Bromofluorobenzene 95.2 77.0-126 03/31/2019 16:12 WG1258489
(S) 1,2-Dichloroethane-d4 112 70.0-130 03/30/2019 18:56 WG1258292
(S) 1,2-Dichloroethane-d4 97.4 70.0-130 03/31/2019 16:12 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 21 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 21 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 09
L1082504
STREAM #1
Collected date/time: 03/25/19 08:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 19:16 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 19:16 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 19:16 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 19:16 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 19:16 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 19:16 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 19:16 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 19:16 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 19:16 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 19:16 WG1258292
1,2,4-Trimethylbenzene 3.25 0.373 1.00 1 03/31/2019 14:04 WG1258489
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 19:16 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 19:16 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 19:16 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 19:16 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 19:16 WG1258292
1,3,5-Trimethylbenzene 1.29 0.387 1.00 1 03/30/2019 19:16 WG1258292
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 19:16 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 19:16 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 19:16 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 19:16 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 19:16 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 19:16 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 19:16 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 19:16 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 19:16 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 19:16 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 19:16 WG1258292
Benzene 0.662 J 0.331 1.00 1 03/30/2019 19:16 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 19:16 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 19:16 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 19:16 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 19:16 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 19:16 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 19:16 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 19:16 WG1258292
Chloroform U 0.324 5.00 1 03/30/2019 19:16 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 19:16 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 19:16 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 19:16 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 19:16 WG1258292
Di-isopropyl ether U 0.320 1.00 1 03/30/2019 19:16 WG1258292
Ethylbenzene 3.00 0.384 1.00 1 03/30/2019 19:16 WG1258292
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 19:16 WG1258292
Isopropylbenzene U 0.326 1.00 1 03/30/2019 19:16 WG1258292
Methyl tert-butyl ether U 0.367 1.00 1 03/30/2019 19:16 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 19:16 WG1258292
Naphthalene 2.67 J 1.00 5.00 1 03/30/2019 19:16 WG1258292
Styrene U 0.307 1.00 1 03/30/2019 19:16 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 19:16 WG1258292
Toluene 2.25 0.412 1.00 1 03/30/2019 19:16 WG1258292
Trichloroethene U 0.398 1.00 1 03/30/2019 19:16 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 19:16 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 19:16 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 19:16 WG1258292
m&p-Xylenes 7.10 0.719 2.00 1 03/30/2019 19:16 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 22 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 22 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 09
L1082504
STREAM #1
Collected date/time: 03/25/19 08:00
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U 0.361 1.00 1 03/30/2019 19:16 WG1258292
n-Propylbenzene 0.794 J 0.349 1.00 1 03/30/2019 19:16 WG1258292
o-Xylene 2.02 0.341 1.00 1 03/30/2019 19:16 WG1258292
p-Isopropyltoluene U 0.350 1.00 1 03/30/2019 19:16 WG1258292
sec-Butylbenzene U 0.365 1.00 1 03/30/2019 19:16 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 19:16 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 19:16 WG1258292
(S) Toluene-d8 99.6 80.0-120 03/30/2019 19:16 WG1258292
(S) Toluene-d8 98.8 80.0-120 03/31/2019 14:04 WG1258489
(S) a,a,a-Trifluorotoluene 94.5 80.0-120 03/30/2019 19:16 WG1258292
(S) a,a,a-Trifluorotoluene 103 80.0-120 03/31/2019 14:04 WG1258489
(S) 4-Bromofluorobenzene 96.6 77.0-126 03/30/2019 19:16 WG1258292
(S) 4-Bromofluorobenzene 98.7 77.0-126 03/31/2019 14:04 WG1258489
(S) 1,2-Dichloroethane-d4 103 70.0-130 03/30/2019 19:16 WG1258292
(S) 1,2-Dichloroethane-d4 99.3 70.0-130 03/31/2019 14:04 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 23 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 23 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 10
L1082504
STREAM #2
Collected date/time: 03/25/19 10:50
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 19:36 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 19:36 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 19:36 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 19:36 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 19:36 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 19:36 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 19:36 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 19:36 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 19:36 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 19:36 WG1258292
1,2,4-Trimethylbenzene 1.03 0.373 1.00 1 03/31/2019 14:25 WG1258489
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 19:36 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 19:36 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 19:36 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 19:36 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 19:36 WG1258292
1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2019 19:36 WG1258292
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 19:36 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 19:36 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 19:36 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 19:36 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 19:36 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 19:36 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 19:36 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 19:36 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 19:36 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 19:36 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 19:36 WG1258292
Benzene U 0.331 1.00 1 03/30/2019 19:36 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 19:36 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 19:36 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 19:36 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 19:36 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 19:36 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 19:36 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 19:36 WG1258292
Chloroform U 0.324 5.00 1 03/30/2019 19:36 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 19:36 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 19:36 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 19:36 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 19:36 WG1258292
Di-isopropyl ether U 0.320 1.00 1 03/30/2019 19:36 WG1258292
Ethylbenzene 0.850 J 0.384 1.00 1 03/30/2019 19:36 WG1258292
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 19:36 WG1258292
Isopropylbenzene U 0.326 1.00 1 03/30/2019 19:36 WG1258292
Methyl tert-butyl ether U 0.367 1.00 1 03/30/2019 19:36 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 19:36 WG1258292
Naphthalene U 1.00 5.00 1 03/30/2019 19:36 WG1258292
Styrene U 0.307 1.00 1 03/30/2019 19:36 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 19:36 WG1258292
Toluene 0.839 J 0.412 1.00 1 03/30/2019 19:36 WG1258292
Trichloroethene U 0.398 1.00 1 03/30/2019 19:36 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 19:36 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 19:36 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 19:36 WG1258292
m&p-Xylenes 2.15 0.719 2.00 1 03/30/2019 19:36 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 24 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 24 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 10
L1082504
STREAM #2
Collected date/time: 03/25/19 10:50
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U 0.361 1.00 1 03/30/2019 19:36 WG1258292
n-Propylbenzene U 0.349 1.00 1 03/30/2019 19:36 WG1258292
o-Xylene 0.593 J 0.341 1.00 1 03/30/2019 19:36 WG1258292
p-Isopropyltoluene U 0.350 1.00 1 03/30/2019 19:36 WG1258292
sec-Butylbenzene U 0.365 1.00 1 03/30/2019 19:36 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 19:36 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 19:36 WG1258292
(S) Toluene-d8 102 80.0-120 03/30/2019 19:36 WG1258292
(S) Toluene-d8 104 80.0-120 03/31/2019 14:25 WG1258489
(S) a,a,a-Trifluorotoluene 96.5 80.0-120 03/30/2019 19:36 WG1258292
(S) a,a,a-Trifluorotoluene 102 80.0-120 03/31/2019 14:25 WG1258489
(S) 4-Bromofluorobenzene 95.1 77.0-126 03/30/2019 19:36 WG1258292
(S) 4-Bromofluorobenzene 98.6 77.0-126 03/31/2019 14:25 WG1258489
(S) 1,2-Dichloroethane-d4 102 70.0-130 03/30/2019 19:36 WG1258292
(S) 1,2-Dichloroethane-d4 95.0 70.0-130 03/31/2019 14:25 WG1258489
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 25 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 25 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 11
L1082504
STREAM #3
Collected date/time: 03/25/19 08:15
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
1,1,1,2-Tetrachloroethane U 0.385 1.00 1 03/30/2019 19:55 WG1258292
1,1,1-Trichloroethane U 0.319 1.00 1 03/30/2019 19:55 WG1258292
1,1,2,2-Tetrachloroethane U 0.130 1.00 1 03/30/2019 19:55 WG1258292
1,1,2-Trichloroethane U 0.383 1.00 1 03/30/2019 19:55 WG1258292
1,1-Dichloroethane U 0.259 1.00 1 03/30/2019 19:55 WG1258292
1,1-Dichloroethene U 0.398 1.00 1 03/30/2019 19:55 WG1258292
1,1-Dichloropropene U 0.352 1.00 1 03/30/2019 19:55 WG1258292
1,2,3-Trichlorobenzene U 0.230 1.00 1 03/30/2019 19:55 WG1258292
1,2,3-Trichloropropane U 0.807 2.50 1 03/30/2019 19:55 WG1258292
1,2,4-Trichlorobenzene U 0.355 1.00 1 03/30/2019 19:55 WG1258292
1,2,4-Trimethylbenzene U 0.373 1.00 1 03/30/2019 19:55 WG1258292
1,2-Dibromo-3-Chloropropane U 1.33 5.00 1 03/30/2019 19:55 WG1258292
1,2-Dibromoethane U 0.381 1.00 1 03/30/2019 19:55 WG1258292
1,2-Dichlorobenzene U 0.349 1.00 1 03/30/2019 19:55 WG1258292
1,2-Dichloroethane U 0.361 1.00 1 03/30/2019 19:55 WG1258292
1,2-Dichloropropane U 0.306 1.00 1 03/30/2019 19:55 WG1258292
1,3,5-Trimethylbenzene U 0.387 1.00 1 03/30/2019 19:55 WG1258292
1,3-Dichlorobenzene U 0.220 1.00 1 03/30/2019 19:55 WG1258292
1,3-Dichloropropane U 0.366 1.00 1 03/30/2019 19:55 WG1258292
1,4-Dichlorobenzene U 0.274 1.00 1 03/30/2019 19:55 WG1258292
2,2-Dichloropropane U 0.321 1.00 1 03/30/2019 19:55 WG1258292
2-Butanone (MEK)U 3.93 10.0 1 03/30/2019 19:55 WG1258292
2-Chlorotoluene U 0.375 1.00 1 03/30/2019 19:55 WG1258292
4-Chlorotoluene U 0.351 1.00 1 03/30/2019 19:55 WG1258292
4-Methyl-2-pentanone (MIBK)U 2.14 10.0 1 03/30/2019 19:55 WG1258292
Acetone U 10.0 50.0 1 03/30/2019 19:55 WG1258292
Acrolein U 8.87 50.0 1 03/30/2019 19:55 WG1258292
Acrylonitrile U 1.87 10.0 1 03/30/2019 19:55 WG1258292
Benzene U 0.331 1.00 1 03/30/2019 19:55 WG1258292
Bromobenzene U 0.352 1.00 1 03/30/2019 19:55 WG1258292
Bromodichloromethane U 0.380 1.00 1 03/30/2019 19:55 WG1258292
Bromoform U 0.469 1.00 1 03/30/2019 19:55 WG1258292
Bromomethane U 0.866 5.00 1 03/30/2019 19:55 WG1258292
Carbon tetrachloride U 0.379 1.00 1 03/30/2019 19:55 WG1258292
Chlorobenzene U 0.348 1.00 1 03/30/2019 19:55 WG1258292
Chloroethane U 0.453 5.00 1 03/30/2019 19:55 WG1258292
Chloroform U 0.324 5.00 1 03/30/2019 19:55 WG1258292
Chloromethane U 0.276 2.50 1 03/30/2019 19:55 WG1258292
Chlorodibromomethane U 0.327 1.00 1 03/30/2019 19:55 WG1258292
Dibromomethane U 0.346 1.00 1 03/30/2019 19:55 WG1258292
Dichlorodifluoromethane U 0.551 5.00 1 03/30/2019 19:55 WG1258292
Di-isopropyl ether U 0.320 1.00 1 03/30/2019 19:55 WG1258292
Ethylbenzene U 0.384 1.00 1 03/30/2019 19:55 WG1258292
Hexachloro-1,3-butadiene U 0.256 1.00 1 03/30/2019 19:55 WG1258292
Isopropylbenzene U 0.326 1.00 1 03/30/2019 19:55 WG1258292
Methyl tert-butyl ether U 0.367 1.00 1 03/30/2019 19:55 WG1258292
Methylene Chloride U 1.00 5.00 1 03/30/2019 19:55 WG1258292
Naphthalene U 1.00 5.00 1 03/30/2019 19:55 WG1258292
Styrene U 0.307 1.00 1 03/30/2019 19:55 WG1258292
Tetrachloroethene U 0.372 1.00 1 03/30/2019 19:55 WG1258292
Toluene U 0.412 1.00 1 03/30/2019 19:55 WG1258292
Trichloroethene U 0.398 1.00 1 03/30/2019 19:55 WG1258292
Trichlorofluoromethane U 1.20 5.00 1 03/30/2019 19:55 WG1258292
Vinyl chloride U 0.259 1.00 1 03/30/2019 19:55 WG1258292
cis-1,2-Dichloroethene U 0.260 1.00 1 03/30/2019 19:55 WG1258292
m&p-Xylenes U 0.719 2.00 1 03/30/2019 19:55 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 26 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 26 of 42
ONE LAB. NATIONWIDE.SAMPLE RESULTS - 11
L1082504
STREAM #3
Collected date/time: 03/25/19 08:15
Volatile Organic Compounds (GC/MS) by Method 6200B-2011
Result Qualifier MDL RDL Dilution Analysis Batch
Analyte ug/l ug/l ug/l date / time
n-Butylbenzene U 0.361 1.00 1 03/30/2019 19:55 WG1258292
n-Propylbenzene U 0.349 1.00 1 03/30/2019 19:55 WG1258292
o-Xylene U 0.341 1.00 1 03/30/2019 19:55 WG1258292
p-Isopropyltoluene U 0.350 1.00 1 03/30/2019 19:55 WG1258292
sec-Butylbenzene U 0.365 1.00 1 03/30/2019 19:55 WG1258292
tert-Butylbenzene U 0.399 1.00 1 03/30/2019 19:55 WG1258292
trans-1,2-Dichloroethene U 0.396 1.00 1 03/30/2019 19:55 WG1258292
(S) Toluene-d8 99.6 80.0-120 03/30/2019 19:55 WG1258292
(S) a,a,a-Trifluorotoluene 93.1 80.0-120 03/30/2019 19:55 WG1258292
(S) 4-Bromofluorobenzene 95.9 77.0-126 03/30/2019 19:55 WG1258292
(S) 1,2-Dichloroethane-d4 97.9 70.0-130 03/30/2019 19:55 WG1258292
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 27 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 27 of 42
ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG1258292
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1082504-01,02,04,05,06,07,08,09,10,11
Method Blank (MB)
(MB) R3396936-4 03/30/19 13:42
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/l ug/l ug/l
Acetone U 10.0 50.0
Acrolein U 8.87 50.0
Acrylonitrile U 1.87 10.0
Benzene U 0.331 1.00
Bromobenzene U 0.352 1.00
Bromodichloromethane U 0.380 1.00
Bromoform U 0.469 1.00
Bromomethane U 0.866 5.00
n-Butylbenzene U 0.361 1.00
sec-Butylbenzene U 0.365 1.00
tert-Butylbenzene U 0.399 1.00
Carbon tetrachloride U 0.379 1.00
Chlorobenzene U 0.348 1.00
Chlorodibromomethane U 0.327 1.00
Chloroethane U 0.453 5.00
Chloroform U 0.324 5.00
Chloromethane U 0.276 2.50
2-Chlorotoluene U 0.375 1.00
4-Chlorotoluene U 0.351 1.00
1,2-Dibromo-3-Chloropropane U 1.33 5.00
1,2-Dibromoethane U 0.381 1.00
Dibromomethane U 0.346 1.00
1,2-Dichlorobenzene U 0.349 1.00
1,3-Dichlorobenzene U 0.220 1.00
1,4-Dichlorobenzene U 0.274 1.00
Dichlorodifluoromethane U 0.551 5.00
1,1-Dichloroethane U 0.259 1.00
1,2-Dichloroethane U 0.361 1.00
1,1-Dichloroethene U 0.398 1.00
cis-1,2-Dichloroethene U 0.260 1.00
trans-1,2-Dichloroethene U 0.396 1.00
1,2-Dichloropropane U 0.306 1.00
1,1-Dichloropropene U 0.352 1.00
1,3-Dichloropropane U 0.366 1.00
2,2-Dichloropropane U 0.321 1.00
Di-isopropyl ether U 0.320 1.00
Ethylbenzene U 0.384 1.00
Hexachloro-1,3-butadiene U 0.256 1.00
Isopropylbenzene U 0.326 1.00
p-Isopropyltoluene U 0.350 1.00
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 28 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 28 of 42
ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG1258292
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1082504-01,02,04,05,06,07,08,09,10,11
Method Blank (MB)
(MB) R3396936-4 03/30/19 13:42
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/l ug/l ug/l
2-Butanone (MEK)U 3.93 10.0
Methylene Chloride U 1.00 5.00
4-Methyl-2-pentanone (MIBK)U 2.14 10.0
Methyl tert-butyl ether U 0.367 1.00
Naphthalene U 1.00 5.00
n-Propylbenzene U 0.349 1.00
Styrene U 0.307 1.00
1,1,1,2-Tetrachloroethane U 0.385 1.00
1,1,2,2-Tetrachloroethane U 0.130 1.00
Tetrachloroethene U 0.372 1.00
Toluene U 0.412 1.00
1,2,3-Trichlorobenzene U 0.230 1.00
1,2,4-Trichlorobenzene U 0.355 1.00
1,1,1-Trichloroethane U 0.319 1.00
1,1,2-Trichloroethane U 0.383 1.00
Trichloroethene U 0.398 1.00
Trichlorofluoromethane U 1.20 5.00
1,2,3-Trichloropropane U 0.807 2.50
1,2,4-Trimethylbenzene U 0.373 1.00
1,3,5-Trimethylbenzene U 0.387 1.00
Vinyl chloride U 0.259 1.00
o-Xylene U 0.341 1.00
m&p-Xylenes U 0.719 2.00
(S) Toluene-d8 99.5 80.0-120
(S) a,a,a-Trifluorotoluene 95.5 80.0-120
(S) 4-Bromofluorobenzene 92.0 77.0-126
(S) 1,2-Dichloroethane-d4 106 70.0-130
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3396936-1 03/30/19 12:24 • (LCSD) R3396936-2 03/30/19 12:43
Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte ug/l ug/l ug/l %%%%%
Acetone 125 156 158 124 126 19.0-160 1.47 27
Acrolein 125 128 121 102 97.0 10.0-160 5.50 26
Acrylonitrile 125 126 123 101 98.1 55.0-149 2.50 20
Benzene 25.0 23.5 22.6 94.0 90.6 70.0-123 3.75 20
Bromobenzene 25.0 27.2 24.4 109 97.5 73.0-121 11.0 20
Bromodichloromethane 25.0 24.1 23.8 96.3 95.3 75.0-120 1.08 20
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 29 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 29 of 42
ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG1258292
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1082504-01,02,04,05,06,07,08,09,10,11
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3396936-1 03/30/19 12:24 • (LCSD) R3396936-2 03/30/19 12:43
Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte ug/l ug/l ug/l %%%%%
Bromoform 25.0 23.0 22.3 92.0 89.1 68.0-132 3.12 20
Bromomethane 25.0 19.3 19.1 77.2 76.4 10.0-160 1.04 25
n-Butylbenzene 25.0 25.8 23.5 103 94.1 73.0-125 9.09 20
sec-Butylbenzene 25.0 26.1 23.1 104 92.6 75.0-125 12.0 20
tert-Butylbenzene 25.0 27.9 25.3 112 101 76.0-124 9.74 20
Carbon tetrachloride 25.0 24.6 24.0 98.4 95.9 68.0-126 2.58 20
Chlorobenzene 25.0 24.3 23.6 97.4 94.5 80.0-121 3.02 20
Chlorodibromomethane 25.0 24.4 23.9 97.6 95.6 77.0-125 2.09 20
Chloroethane 25.0 21.5 20.8 86.0 83.1 47.0-150 3.41 20
Chloroform 25.0 24.6 24.0 98.4 95.8 73.0-120 2.62 20
Chloromethane 25.0 20.9 20.1 83.8 80.2 41.0-142 4.32 20
2-Chlorotoluene 25.0 28.7 25.9 115 104 76.0-123 10.1 20
4-Chlorotoluene 25.0 28.5 25.6 114 103 75.0-122 10.6 20
1,2-Dibromo-3-Chloropropane 25.0 22.9 20.6 91.7 82.5 58.0-134 10.6 20
1,2-Dibromoethane 25.0 24.6 23.8 98.5 95.3 80.0-122 3.28 20
Dibromomethane 25.0 24.8 24.2 99.0 96.8 80.0-120 2.28 20
1,2-Dichlorobenzene 25.0 26.6 23.9 106 95.7 79.0-121 10.6 20
1,3-Dichlorobenzene 25.0 25.4 23.4 102 93.4 79.0-120 8.36 20
1,4-Dichlorobenzene 25.0 25.6 23.4 103 93.7 79.0-120 9.03 20
Dichlorodifluoromethane 25.0 21.5 20.8 85.9 83.2 51.0-149 3.26 20
1,1-Dichloroethane 25.0 24.9 24.3 99.6 97.1 70.0-126 2.53 20
1,2-Dichloroethane 25.0 25.1 24.5 100 97.9 70.0-128 2.60 20
1,1-Dichloroethene 25.0 22.0 21.3 87.8 85.2 71.0-124 3.04 20
cis-1,2-Dichloroethene 25.0 23.8 23.4 95.2 93.5 73.0-120 1.80 20
trans-1,2-Dichloroethene 25.0 23.2 22.3 92.7 89.2 73.0-120 3.94 20
1,2-Dichloropropane 25.0 25.9 25.2 104 101 77.0-125 2.73 20
1,1-Dichloropropene 25.0 23.6 23.3 94.2 93.0 74.0-126 1.26 20
1,3-Dichloropropane 25.0 25.2 24.9 101 99.5 80.0-120 1.30 20
2,2-Dichloropropane 25.0 24.4 23.8 97.4 95.3 58.0-130 2.18 20
Di-isopropyl ether 25.0 25.3 24.4 101 97.5 58.0-138 3.79 20
Ethylbenzene 25.0 24.3 23.8 97.1 95.1 79.0-123 2.09 20
Hexachloro-1,3-butadiene 25.0 25.4 23.0 102 91.9 54.0-138 9.98 20
Isopropylbenzene 25.0 24.1 23.6 96.6 94.6 76.0-127 2.08 20
p-Isopropyltoluene 25.0 26.6 24.2 106 96.9 76.0-125 9.47 20
2-Butanone (MEK)125 145 145 116 116 44.0-160 0.145 20
Methylene Chloride 25.0 23.7 23.0 95.0 91.9 67.0-120 3.32 20
4-Methyl-2-pentanone (MIBK)125 134 131 107 105 68.0-142 2.65 20
Methyl tert-butyl ether 25.0 24.0 23.0 95.9 91.9 68.0-125 4.23 20
Naphthalene 25.0 22.9 20.9 91.5 83.4 54.0-135 9.18 20
n-Propylbenzene 25.0 27.9 25.2 112 101 77.0-124 10.3 20
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:39 30 of 42
ACCOUNT:PROJECT:SDG:DATE/TIME:PAGE:
Mid-Atlantic - Speedway NC R1760.18A L1082504 04/02/19 16:47 30 of 42
ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG1258292
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1082504-01,02,04,05,06,07,08,09,10,11
Laboratory Control Sample (LCS) • Laboratory Control Sample Duplicate (LCSD)
(LCS) R3396936-1 03/30/19 12:24 • (LCSD) R3396936-2 03/30/19 12:43
Spike Amount LCS Result LCSD Result LCS Rec.LCSD Rec.Rec. Limits LCS Qualifier LCSD Qualifier RPD RPD Limits
Analyte ug/l ug/l ug/l %%%%%
Styrene 25.0 24.8 24.3 99.1 97.1 73.0-130 2.08 20
1,1,1,2-Tetrachloroethane 25.0 24.9 24.3 99.5 97.2 75.0-125 2.26 20
1,1,2,2-Tetrachloroethane 25.0 27.0 24.4 108 97.5 65.0-130 10.1 20
Tetrachloroethene 25.0 23.2 22.7 92.7 90.8 72.0-132 2.03 20
Toluene 25.0 22.7 21.8 90.9 87.1 79.0-120 4.33 20
1,2,3-Trichlorobenzene 25.0 24.8 22.5 99.2 90.0 50.0-138 9.73 20
1,2,4-Trichlorobenzene 25.0 25.4 22.8 102 91.1 57.0-137 11.0 20
1,1,1-Trichloroethane 25.0 25.0 23.7 99.8 94.6 73.0-124 5.33 20
1,1,2-Trichloroethane 25.0 24.9 23.5 99.5 93.9 80.0-120 5.74 20
Trichloroethene 25.0 22.6 22.4 90.6 89.5 78.0-124 1.20 20
Trichlorofluoromethane 25.0 22.5 22.1 89.8 88.2 59.0-147 1.80 20
1,2,3-Trichloropropane 25.0 29.9 26.2 120 105 73.0-130 13.3 20
1,2,4-Trimethylbenzene 25.0 27.4 24.7 110 98.7 76.0-121 10.4 20
1,3,5-Trimethylbenzene 25.0 27.5 24.8 110 99.2 76.0-122 10.3 20
Vinyl chloride 25.0 21.7 20.8 86.8 83.1 67.0-131 4.34 20
o-Xylene 25.0 23.7 23.1 94.7 92.3 80.0-122 2.51 20
m&p-Xylenes 50.0 47.7 46.6 95.4 93.2 80.0-122 2.29 20
(S) Toluene-d8 96.8 98.3 80.0-120
(S) a,a,a-Trifluorotoluene 95.7 97.3 80.0-120
(S) 4-Bromofluorobenzene 92.9 95.2 77.0-126
(S) 1,2-Dichloroethane-d4 108 106 70.0-130
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG1258489
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1082504-03,04,05,06,07,08,09,10
Method Blank (MB)
(MB) R3397293-3 03/31/19 11:20
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/l ug/l ug/l
Acetone U 10.0 50.0
Acrolein U 8.87 50.0
Acrylonitrile U 1.87 10.0
Benzene U 0.331 1.00
Bromobenzene U 0.352 1.00
Bromodichloromethane U 0.380 1.00
Bromoform U 0.469 1.00
Bromomethane U 0.866 5.00
n-Butylbenzene U 0.361 1.00
sec-Butylbenzene U 0.365 1.00
tert-Butylbenzene U 0.399 1.00
Carbon tetrachloride U 0.379 1.00
Chlorobenzene U 0.348 1.00
Chlorodibromomethane U 0.327 1.00
Chloroethane U 0.453 5.00
Chloroform U 0.324 5.00
Chloromethane U 0.276 2.50
2-Chlorotoluene U 0.375 1.00
4-Chlorotoluene U 0.351 1.00
1,2-Dibromo-3-Chloropropane U 1.33 5.00
1,2-Dibromoethane U 0.381 1.00
Dibromomethane U 0.346 1.00
1,2-Dichlorobenzene U 0.349 1.00
1,3-Dichlorobenzene U 0.220 1.00
1,4-Dichlorobenzene U 0.274 1.00
Dichlorodifluoromethane U 0.551 5.00
1,1-Dichloroethane U 0.259 1.00
1,2-Dichloroethane U 0.361 1.00
1,1-Dichloroethene U 0.398 1.00
cis-1,2-Dichloroethene U 0.260 1.00
trans-1,2-Dichloroethene U 0.396 1.00
1,2-Dichloropropane U 0.306 1.00
1,1-Dichloropropene U 0.352 1.00
1,3-Dichloropropane U 0.366 1.00
2,2-Dichloropropane U 0.321 1.00
Di-isopropyl ether U 0.320 1.00
Ethylbenzene U 0.384 1.00
Hexachloro-1,3-butadiene U 0.256 1.00
Isopropylbenzene U 0.326 1.00
p-Isopropyltoluene U 0.350 1.00
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG1258489
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1082504-03,04,05,06,07,08,09,10
Method Blank (MB)
(MB) R3397293-3 03/31/19 11:20
MB Result MB Qualifier MB MDL MB RDL
Analyte ug/l ug/l ug/l
2-Butanone (MEK)U 3.93 10.0
Methylene Chloride U 1.00 5.00
4-Methyl-2-pentanone (MIBK)U 2.14 10.0
Methyl tert-butyl ether U 0.367 1.00
Naphthalene U 1.00 5.00
n-Propylbenzene U 0.349 1.00
Styrene U 0.307 1.00
1,1,1,2-Tetrachloroethane U 0.385 1.00
1,1,2,2-Tetrachloroethane U 0.130 1.00
Tetrachloroethene U 0.372 1.00
1,2,3-Trichlorobenzene U 0.230 1.00
Toluene U 0.412 1.00
1,2,4-Trichlorobenzene U 0.355 1.00
1,1,1-Trichloroethane U 0.319 1.00
1,1,2-Trichloroethane U 0.383 1.00
Trichloroethene U 0.398 1.00
Trichlorofluoromethane U 1.20 5.00
1,2,3-Trichloropropane U 0.807 2.50
1,2,4-Trimethylbenzene U 0.373 1.00
1,3,5-Trimethylbenzene U 0.387 1.00
Vinyl chloride U 0.259 1.00
o-Xylene U 0.341 1.00
m&p-Xylenes U 0.719 2.00
(S) Toluene-d8 101 80.0-120
(S) a,a,a-Trifluorotoluene 101 80.0-120
(S) 4-Bromofluorobenzene 95.1 77.0-126
(S) 1,2-Dichloroethane-d4 102 70.0-130
Laboratory Control Sample (LCS)
(LCS) R3397293-1 03/31/19 09:55
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte ug/l ug/l %%
Acetone 125 118 94.1 19.0-160
Acrolein 125 139 111 10.0-160
Acrylonitrile 125 142 114 55.0-149
Bromobenzene 25.0 25.1 101 73.0-121
Bromodichloromethane 25.0 28.7 115 75.0-120
Bromoform 25.0 25.5 102 68.0-132
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG1258489
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1082504-03,04,05,06,07,08,09,10
Laboratory Control Sample (LCS)
(LCS) R3397293-1 03/31/19 09:55
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte ug/l ug/l %%
Bromomethane 25.0 27.6 111 10.0-160
n-Butylbenzene 25.0 28.7 115 73.0-125
sec-Butylbenzene 25.0 26.7 107 75.0-125
tert-Butylbenzene 25.0 27.4 110 76.0-124
Carbon tetrachloride 25.0 29.7 119 68.0-126
Benzene 25.0 28.7 115 70.0-123
Chlorobenzene 25.0 27.0 108 80.0-121
Chlorodibromomethane 25.0 26.1 104 77.0-125
Chloroethane 25.0 24.7 99.0 47.0-150
Chloroform 25.0 28.1 112 73.0-120
Chloromethane 25.0 21.8 87.2 41.0-142
2-Chlorotoluene 25.0 27.6 111 76.0-123
4-Chlorotoluene 25.0 27.3 109 75.0-122
1,2-Dibromo-3-Chloropropane 25.0 25.5 102 58.0-134
1,2-Dibromoethane 25.0 27.7 111 80.0-122
Dibromomethane 25.0 27.3 109 80.0-120
1,2-Dichlorobenzene 25.0 27.1 108 79.0-121
1,3-Dichlorobenzene 25.0 27.2 109 79.0-120
1,4-Dichlorobenzene 25.0 27.3 109 79.0-120
Dichlorodifluoromethane 25.0 25.5 102 51.0-149
1,1-Dichloroethane 25.0 28.9 116 70.0-126
1,2-Dichloroethane 25.0 26.1 105 70.0-128
1,1-Dichloroethene 25.0 24.2 96.8 71.0-124
cis-1,2-Dichloroethene 25.0 29.8 119 73.0-120
trans-1,2-Dichloroethene 25.0 25.8 103 73.0-120
1,2-Dichloropropane 25.0 28.3 113 77.0-125
1,1-Dichloropropene 25.0 29.4 118 74.0-126
1,3-Dichloropropane 25.0 27.4 110 80.0-120
2,2-Dichloropropane 25.0 30.8 123 58.0-130
Hexachloro-1,3-butadiene 25.0 28.0 112 54.0-138
Isopropylbenzene 25.0 26.9 108 76.0-127
p-Isopropyltoluene 25.0 28.3 113 76.0-125
2-Butanone (MEK)125 156 125 44.0-160
Methylene Chloride 25.0 22.8 91.2 67.0-120
4-Methyl-2-pentanone (MIBK)125 142 114 68.0-142
Di-isopropyl ether 25.0 28.6 114 58.0-138
Ethylbenzene 25.0 28.4 113 79.0-123
n-Propylbenzene 25.0 27.5 110 77.0-124
Styrene 25.0 25.9 104 73.0-130
1,1,1,2-Tetrachloroethane 25.0 26.9 108 75.0-125
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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ONE LAB. NATIONWIDE.QUALITY CONTROL SUMMARYWG1258489
Volatile Organic Compounds (GC/MS) by Method 6200B-2011 L1082504-03,04,05,06,07,08,09,10
Laboratory Control Sample (LCS)
(LCS) R3397293-1 03/31/19 09:55
Spike Amount LCS Result LCS Rec.Rec. Limits LCS Qualifier
Analyte ug/l ug/l %%
1,1,2,2-Tetrachloroethane 25.0 26.1 104 65.0-130
Tetrachloroethene 25.0 28.2 113 72.0-132
1,2,3-Trichlorobenzene 25.0 27.9 112 50.0-138
1,2,4-Trichlorobenzene 25.0 27.9 112 57.0-137
1,1,1-Trichloroethane 25.0 28.9 116 73.0-124
Methyl tert-butyl ether 25.0 25.5 102 68.0-125
1,1,2-Trichloroethane 25.0 26.4 106 80.0-120
Trichloroethene 25.0 27.6 110 78.0-124
Naphthalene 25.0 26.6 107 54.0-135
Trichlorofluoromethane 25.0 24.3 97.3 59.0-147
1,2,3-Trichloropropane 25.0 25.0 100 73.0-130
Vinyl chloride 25.0 24.0 96.0 67.0-131
Toluene 25.0 27.3 109 79.0-120
1,2,4-Trimethylbenzene 25.0 27.9 112 76.0-121
1,3,5-Trimethylbenzene 25.0 27.5 110 76.0-122
o-Xylene 25.0 27.3 109 80.0-122
m&p-Xylenes 50.0 56.5 113 80.0-122
(S) Toluene-d8 88.4 80.0-120
(S) a,a,a-Trifluorotoluene 94.5 80.0-120
(S) 4-Bromofluorobenzene 90.2 77.0-126
(S) 1,2-Dichloroethane-d4 108 70.0-130
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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ONE LAB. NATIONWIDE.GLOSSARY OF TERMS
Guide to Reading and Understanding Your Laboratory Report
Abbreviations and Definitions
Qualifier Description
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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ONE LAB. NATIONWIDE.
Pace National is the only environmental laboratory accredited/certified to support your work nationwide from one location. One phone call, one point of contact, one laboratory. No other lab is as
accessible or prepared to handle your needs throughout the country. Our capacity and capability from our single location laboratory is comparable to the collective totals of the network
laboratories in our industry. The most significant benefit to our one location design is the design of our laboratory campus. The model is conducive to accelerated productivity, decreasing
turn-around time, and preventing cross contamination, thus protecting sample integrity. Our focus on premium quality and prompt service allows us to be YOUR LAB OF CHOICE.
* Not all certifications held by the laboratory are applicable to the results reported in the attached report.
* Accreditation is only applicable to the test methods specified on each scope of accreditation held by Pace National.

State Accreditations
Alabama 40660 Nebraska NE-OS-15-05
Alaska 17-026 Nevada TN-03-2002-34
Arizona AZ0612 New Hampshire 2975
Arkansas 88-0469 New Jersey–NELAP TN002
California 2932 New Mexico ¹n/a
Colorado TN00003 New York 11742
Connecticut PH-0197 North Carolina Env375
Florida E87487 North Carolina ¹DW21704
Georgia NELAP North Carolina ³41
Georgia ¹923 North Dakota R-140
Idaho TN00003 Ohio–VAP CL0069
Illinois 200008 Oklahoma 9915
Indiana C-TN-01 Oregon TN200002
Iowa 364 Pennsylvania 68-02979
Kansas E-10277 Rhode Island LAO00356
Kentucky ¹ ⁶90010 South Carolina 84004
Kentucky ²16 South Dakota n/a
Louisiana AI30792 Tennessee ¹ ⁴2006
Louisiana ¹LA180010 Texas T104704245-18-15
Maine TN0002 Texas ⁵LAB0152
Maryland 324 Utah TN00003
Massachusetts M-TN003 Vermont VT2006
Michigan 9958 Virginia 460132
Minnesota 047-999-395 Washington C847
Mississippi TN00003 West Virginia 233
Missouri 340 Wisconsin 9980939910
Montana CERT0086 Wyoming A2LA

Third Party Federal Accreditations
A2LA – ISO 17025 1461.01 AIHA-LAP,LLC EMLAP 100789
A2LA – ISO 17025 ⁵1461.02 DOD 1461.01
Canada 1461.01 USDA P330-15-00234
EPA–Crypto TN00003
ACCREDITATIONS & LOCATIONS

¹ Drinking Water ² Underground Storage Tanks ³ Aquatic Toxicity ⁴ Chemical/Microbiological ⁵ Mold ⁶ Wastewater n/a Accreditation not applicable

Our Locations
Pace National has sixty-four client support centers that provide sample pickup and/or the delivery of sampling supplies. If you would like assistance from one of our support offices, please contact
our main office. Pace National performs all testing at our central laboratory.
1 Cp
2Tc
3Ss
4Cn
5Sr
6Qc
7Gl
8Al
9Sc
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TURN AROUND TIME
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Chain-of-Custody-Record
Printed: 05/18/2019
1,1,1,2-Tetrachloroethane ug/L, 1,1,1-Trichloroethane ug/L, 1,1,2,2-Tetrachloroethane ug/L, 1,1,2-Trichloroethane ug/L, 1,1-Dichloroethane ug/L, 1,1-Dichloroethene ug/L, 1,1-Dichloropropene ug/L,
1,2,3-Trichlorobenzene ug/L, 1,2,3-Trichloropropane ug/L, 1,2,4-Trichlorobenzene ug/L, 1,2,4-Trimethylbenzene ug/L, 1,2-Dibromo-3-chloropropane ug/L, 1,2-Dibromoethane ug/L, 1,2-Dichlorobenzene ug/L,
1,2-Dichloroethane ug/L, 1,2-Dichloropropane ug/L, 1,3,5-Trimethylbenzene ug/L, 1,3-Dichlorobenzene ug/L, 1,3-Dichloropropane ug/L, 1,4-Dichlorobenzene ug/L, 2,2-Dichloropropane ug/L, 2-Butanone ug/L,
2-Chlorotoluene ug/L, 4-Chlorotoluene ug/L, 4-Methyl-2-pentanone ug/L, Acetone ug/L, Acrolein ug/L, Acrylonitrile ug/L, Benzene ug/L, Bromobenzene ug/L, Bromodichloromethane ug/L, Bromoform ug/L, Bromomethane
ug/L, Carbon tetrachloride ug/L, Chlorobenzene ug/L, Chloroethane ug/L, Chloroform ug/L, Chloromethane ug/L, Dibromochloromethane ug/L, Dibromomethane ug/L, Dichlorodifluoromethane ug/L, Diisopropyl ether ug/L,
Ethylbenzene ug/L, Hexachlorobutadiene ug/L, Isopropylbenzene ug/L, Methyl tert butyl ether ug/L, Methylene chloride ug/L, Naphthalene ug/L, Styrene ug/L, Tetrachloroethene ug/L, Toluene ug/L, Trichloroethene ug/L,
Trichlorofluoromethane ug/L, Vinyl chloride ug/L, cis-1,2-Dichloroethene ug/L, m,p-Xylene ug/L, n-Butylbenzene ug/L, n-Propylbenzene ug/L, o-Xylene ug/L, p-Isopropyltoluene ug/L, sec-Butylbenzene ug/L,
tert-Butylbenzene ug/L, trans-1,2-Dichloroethene ug/L
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