HomeMy WebLinkAboutMO-28920_48124_CA_CSA_20231009_Rushco 4
3502 Hayes Road • Monroe, North Carolina 28110
113 West Firetower Road, Suite G • Winterville, North Carolina 28590
Phone (704) 845-4010 • (888) 870-4133 • Fax (704) 845-4012
October 9, 2023
Mr. Ryan Mills
NCDEQ-UST Section
Mooresville Regional Office
610 East Center Ave.
Mooresville, NC 28115
Re: Comprehensive Site Assessment Report
August 2023
Former Rushco Food Store #4
1901 West Innes Street
Salisbury, Rowan County
North Carolina
Facility ID Number: 00-0-0000030414
Incident Number: 48124
GRI Project Number: 5721
Dear Mr. Mills,
Please find enclosed the referenced report for the abovementioned site.
If you have any questions, please contact Sam McKay at 704-845-4010.
Sincerely,
Geological Resources, Inc.
Leslie Maxtone-Graham
Administrative Assistant
Enclosure
Cc: Mr. Joey Rusher; Rusher Oil Company, Inc., file
3502 Hayes Road • Monroe, North Carolina 28110
113 West Firetower Road, Suite G • Winterville, North Carolina 28590
Phone (704) 845-4010 • (888) 870-4133 • Fax (704) 845-4012
Engineering Certification: C-2727 • Geology Certification: C-127
Comprehensive Site Assessment Report
August 2023
Former Rushco Food Store #4
1901 West Innes Street
Salisbury, Rowan County
North Carolina
Facility ID Number: 00-0-0000030414
Incident Number: 48124
GRI Project Number: 5721
Prepared for:
Mr. Joey Rusher
Rusher Oil Company, Inc.
Post Office Box 1483
Salisbury, North Carolina 28145
October 9, 2023
Samuel McKay III, P.G.
Project Manager
Kyle Perry
Report Writer
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
i
EXECUTIVE SUMMARY
Former Rushco Food Store #4 is located at 1901 West Innes Street in Salisbury, Rowan County, North
Carolina The property operates as a petroleum retail facility and convenience store. The site is covered by
concrete and asphalt. There are two 10,000-gallon gasoline USTs and one 7,500-gallon gasoline UST
currently in use at the site with three associated gasoline dispensers. The surrounding properties are
commercial, residential, and institutional. According to the information determined during receptor
survey activities, no water supply wells were identified within 1,500 feet of the site. Public water is
available to the site and surrounding properties within a 1,500-foot radius of the site.
During due diligence activities conducted in October 2021, reportable soil violations were identified at the
site, and an LSA was required by the NCDEQ
A receptor survey was conducted on March 14, 2022. No water supply wells were identified within a
1,500-foot radius of the site. No surface water bodies were identified within a 500-foot radius of the site.
On March 14, 2022, one Type II monitoring well was installed and sampled as part of the LSA activities.
Based on the results of the LSA activities, an ARA was negotiated to be conducted prior to the CSA directed
by the NCDEQ.
ARA activities were conducted between February 20, 2023 and March 1, 2023. Three Type II monitoring
wells and one Type III telescoping well were installed and sampled, soil samples were collected during the
installation of the wells and submitted for laboratory analysis, and slug tests were conducted on two of
the monitoring wells and the telescoping well as part of the ARA activities. Based on the results from the
ARA activities, a CSA was requested by the NCDEQ.
On August 11, 2023, three Type II monitoring wells were installed as part of the CSA activities. After the
new wells were installed, a comprehensive sampling event was conducted. On August 24, 2023, seven
Type II monitoring wells and one Type III telescoping well were gauged, purged, and sampled. The
reported contaminant concentrations of benzene, toluene, ethylbenzene, xylenes, MTBE, naphthalene,
tert-amyl alcohol (TAA), tert-butyl alcohol (TBA), 2-hexanone, isopropylbenzene, MIBK, n-propylbenzene,
IPE, styrene, 1,2,4-triethylbenzene, 1,3,5-trimethylbenzene, lead, C5-C8 aliphatics, C9-C12 aliphatics
and/or C9-C10 aromatics in the ground water samples collected from MW-1 through MW-7 exceeded the
MACs. The reported benzene, TAA and TBA contaminant concentrations in the ground water sample
collected from MW-1 exceeded the GCLs. The reported benzene contaminant concentration in the
ground water sample from MW-4 exceeded the GCL. No free product was encountered at the site during
the CSA activities.
According to the 1985 Geologic Map of North Carolina, the site is located within the Charlotte Belt. The
bedrock is generally described as interbedded felsic to mafic tuffs and flowrock. Based on observations
made during the assessment activities, surficial soils observed at the site consist of various clays and silts
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
ii
to varying depths, with lenses of weathered quartz. Ground water flow was generally toward the
northeast. The horizontal hydraulic gradient calculated between MW-1 and MW-5 was 0.03 feet per foot.
The vertical hydraulic gradient calculated between MW-1 and TW-1 was 0.02 feet per foot in the upward
direction.
The site risk classification has been deemed as intermediate risk based on the presence of GCL
exceedances. Therefore, the ground water contamination must be remediated to concentrations less
than the GCLs.
A comprehensive ground water sampling event should be conducted at the site in March 2024 to confirm
the results of the CSA ground water sampling events. MMPE events should be conducted on monitoring
wells MW-1 , MW-4, and MW-6 to reduce contaminant concentrations in those wells. Based on the results
of the March 2024 sampling event, a decision to pursue corrective action or allow for natural attenuation
can be made.
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
iii
SITE INFORMATION
1. Site Identification
Former Rushco Food Store #4 (Facility ID 00-0-0000030414)
Incident Number 48124 – Intermediate Risk (I-115-D)
Location of Source Area: 1901 West Innes Street
Salisbury, NC 28056
Rowan County
35.2141990°N, 81.1334670°W (Topographical Map)
2. Information about Contacts Associated with the Leaking UST System
UST/AST Owner
Sampson Bladen Oil Company, Inc.
510 Commerce Street
Clinton, NC 28329
Email Unknown
(910) 592-4177
UST/AST Operator
Sampson Bladen Oil Company, Inc.
510 Commerce Street
Clinton, NC 28329
Email Unknown
(910) 592-4177
Property Owner
Sampson Bladen Oil Company, Inc.
510 Commerce Street
Clinton, NC 28329
Email Unknown
(910) 592-4177
Property Occupant
Han-Dee Hugo’s #225
1901 West Innes Street
Salisbury, NC 28144
Email Unknown
(704) 633-7618
Consultant/Contractor
Geological Resources, Inc.
3502 Hayes Road
Monroe, NC 28110
smckay@geologicalresourcesinc.com
(704) 845-4010
Analytical Laboratory
Waypoint Analytical, LLC
449 Springbrook Road
Charlotte, NC 28217
State Cert. Nos. 37735 and 402
(704) 529-6364
3. Information about Release
Release was discovered on October 20, 2021
An unknown amount of product was released from the leaking UST System
Two (2) 10,000-gallon gasoline USTs, one (1) 7,500-gallon gasoline UST, and associated pumps
and product piping are active at the site
Certification:
I, Samuel L. McKay, III, a Licensed Geologist for Geological Resources, Inc., do certify that the information
contained in this report is correct and accurate to the best of my knowledge.
Geological Resources, Inc. is licensed to practice geology and engineering in North Carolina. The
certification numbers of the company are C-127 and C-2727, respectively.
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
iv
ACRONYMS
ACM: Asbestos Containing Materials
AFVR: Aggressive Fluid-Vapor Recovery
ARR: Acknowledgement of Report Receipt
AS: Air Sparging
AST: Aboveground Storage Tank
ASTM: American Society for Testing and
Materials
BGS: Below Ground Surface
CAP: Corrective Action Plan
CFR: Code of Federal Regulations
CSA: Comprehensive Site Assessment
DPE: Dual Phase Extraction
DRO: Total Petroleum Hydrocarbons Diesel
Range Organics
DWM: Division of Waste Management
DWR: Department of Water Resources
EPA: Environmental Protection Agency
EPH: Extractible Petroleum Hydrocarbons
ESA: Environmental Site Assessment
GCL: Gross Contamination Level
GRI: Geological Resources, Inc.
GRO: Total Petroleum Hydrocarbons
Gasoline Range Organics
LSA: Limited Site Assessment
MAC: Maximum Allowable Concentration as
specified in T15A NCAC 2L.0202
MADEP: Massachusetts Department of
Environmental Protection
MCC: Maximum Contaminant Concentrations
MMPE: Mobile Multi-Phase Extraction
NAPL: Non-Aqueous Phase Liquid, “Free
Product”
NCDEQ: North Carolina Department of
Environmental Quality
NCDOT: North Carolina Department of
Transportation
NFA: Notice of No Further Action
NORR: Notice of Regulatory Requirements
NOV: Notice of Violation
NPDES: National Pollutant Discharge
Elimination System
NRP: Notice of Residual Petroleum
O&M: Operation and Maintenance
PAHs: Polynuclear Aromatic Hydrocarbons
PCA: Pre-Construction Assessment
RAL: Regulatory Action Level
SCLs: Soil Cleanup Level
SPCC: Spill Prevention Control and
Countermeasures
SVE: Soil Vapor Extraction
SVOCs: Semi-Volatile Organic Compounds
SWAP: Source Water Assessment and
Protection
SWPPP: Stormwater Pollution Prevention Plan
TCLP: Toxicity Characteristic Leaching
Procedure (EPA Method SW-846 1311)
TOC: Top of Casing
TPH: Total Petroleum Hydrocarbons
USGS: United States Geological Survey
UST: Underground Storage Tank
UVF: Ultraviolet Fluorescence
VOCs: Volatile Organic Compounds
VPH: Volatile Petroleum Hydrocarbons
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report Prepared on: October 9, 2023 Former Rushco Food Store #4 Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
TABLE OF CONTENTS
EXECUTIVE SUMMARY ....................................................................................................................... i
SITE INFORMATION ........................................................................................................................... iii
ACRONYMS ....................................................................................................................................... iv
1.0 SITE HISTORY AND CHARACTERIZATION ...................................................................................1
2.0 RECEPTOR INFORMATION ........................................................................................................2
3.0 LAND USE ................................................................................................................................3
4.0 SOIL ASSESSMENT ...................................................................................................................3
5.0 GROUND WATER ASSESSMENT ................................................................................................4
6.0 HYDROGEOLOGIC INVESTIGATION ...........................................................................................6
7.0 REGIONAL GEOLOGY AND HYDROGEOLOGY .............................................................................6
8.0 SITE GEOLOGY AND HYDROGEOLOGY ......................................................................................6
9.0 DISCUSSION ............................................................................................................................7
10.0 CONCLUSIONS AND RECOMMENDATIONS ...............................................................................7
11.0 PUBLIC NOTICE ........................................................................................................................7
12.0 LIMITATIONS ...........................................................................................................................8
13.0 REFERENCES ............................................................................................................................8
FIGURES
Figure 1: Site Location Map
Figure 2A: Site Vicinity Map
Figure 2B: Zoning Map
Figure 3: Site Map
Figure 4: Cross-Section A-A’
Figure 5: Cross-Section B-B’
Figure 6: Ground Water Quality Map
Figure 7: Benzene Isoconcentration Map
Figure 8: TAA Isoconcentration Map
Figure 9: TBA Isoconcentration Map
Figure 10: Estimated Contaminant Mass Area Map
Figure 11: Water Table Surface Map
TABLES
Table 1: UST Owner and Operator Information
Table 2: UST System Information
Table 3: Adjacent Property Owner Information
Table 4: Land Use Information
Table 5: Summary of Ground Water Sample Analytical Results
Table 6: Well Construction and Gauging Information
Table 7: Summary of Slug Test Analyses
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
Table 7: Well Construction and Gauging Information
Table 8: Summary of Slug Test Analyses
APPENDICES
Appendix A: State Correspondence
Appendix B: Site Specific Health and Safety Plan
Appendix C: Well Photos
Appendix D: Well Construction Records and Subsurface Logs
Appendix E: Laboratory Analytical Report
Appendix F: Contaminant Mass Calculations
Appendix G: Notification of Local Officials
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
1
1.0 SITE HISTORY AND CHARACTERIZATION
GRI presents the results of the August 2023 CSA activities at the Former Rushco Food Store #4 site; located
at 1901 West Innes Street in Salisbury, Rowan County, North Carolina. A topographic map of the general
site location and the surrounding area is included as Figure 1. These activities were conducted in
accordance with GRI Proposal No. 23-283, which was submitted to the NCDEQ on May 24, 2023, and
approved as Task Authorization No. 48124-3 on June 20, 2023. State correspondence is included as
Appendix A.
The site is currently owned by Sampson Bladen Oil Company, Inc. and is operated by Han-Dee Hugo as a
petroleum retail facility and convenience store. Two 10,000-gallon gasoline USTs, one 7,500-gallon
gasoline UST, and associated pumps and product piping are active at the site. UST owner/operator
information and UST system information are included as Table 1 and Table 2, respectively. The Registered
Tank Report is shown below:
During due diligence activities conducted in October 2021, reportable soil violations were identified at the
site, and an LSA was required by the NCDEQ.
On March 14, 2022, during the LSA activities, one monitoring well (MW-1) was installed in the
approximate location of the soil boring with the highest concentrations during the due diligence activities.
The monitoring well was installed to a depth of approximately 35 feet BGS and soil samples were collected
at 10-foot intervals. The reported contaminant concentrations of benzene, toluene, xylenes, MTBE,
naphthalene, TBA, p-isopropyltoluene, n-propylbezene, and/or C9-C10 aromatics reported in soil samples
MW-1-5’, MW-1-15’, and MW-1-25’ exceeded the soil-to-water MCCs. All target contaminant
concentrations were below the residential SCLs.
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
2
Monitoring well MW-1 was gauged, purged, and sampled on March 14, 2022. The reported contaminant
concentrations of benzene, toluene, ethylbenzene, xylenes, MTBE, naphthalene, TAA, TBA,
isopropylbenzene, IPE, n-propylbenzene, 1,2,4-trimethylbenzene, 1,3,5-trimethylbenzene, EDB, lead, C5-
C8 aliphatics and C9-C10 aromatics reported in the ground water sample collected from MW-1 exceeded
the MACs. The reported concentration of benzene in the ground water sample collected from MW-1
exceeded the GCL. Free product was not observed at the site. Based on the results from the LSA activities,
an ARA was negotiated to be conducted prior to the CSA directed by the NCDEQ.
On February 20, 2023, and February 21, 2023, three Type II monitoring wells (MW-2 through MW-4) and
one Type III monitoring well (TW-1) were installed at the site during the ARA activities. Monitoring wells
MW-2 through MW-4 were installed to a total depth of 30 feet with a screened interval of 10 feet.
Telescoping well TW-1 was installed to a total depth of 55 feet with a screened interval of 5 feet. Soil
samples (MW-2-15’, MW-2-25’, MW-3-15’, MW-3-25’, MW-4-15’, MW-4-25’, TW-1-15’, and TW-2-25’)
were collected from 15 feet BGS and 25 feet BGS during the installation of each new well. The soil samples
were submitted for TPH-GRO analysis with UVF technology. The GRO concentration in soil sample MW-
4-25 exceeded the RAL.
On March 1, 2023, slug tests were conducted on MW-2, MW-3, and TW-1, and four Type II monitoring
wells (MW-1 through MW-4) and one telescoping well (TW-1) were gauged, purged, and sampled. The
concentrations of benzene, toluene, ethylbenzene, xylenes, MTBE, naphthalene, acetone, TAA, TBA, 1,2-
dichloroethane, 2-hexanone, isopropylbenzene, di-isopropyl ether, methylene chloride, MIBK, n-
propylbenzene, styrene, 1,2,4-trimethylbenzene, 1,3,5-trimethylbenzene, EDB, C5-C8 aliphatics, C9-C12
aliphatics, and/or C9-C10 aliphatics reported in the ground water samples collected from MW-1 through
MW-4 exceeded the MACs. The reported concentrations of benzene and/or MTBE reported in the ground
water samples collected from MW-1 and MW-4 exceeded the GCLs. Based on the results from the ARA
activities, a CSA was requested by the NCDEQ. A Site Map showing the locations of the monitoring wells
and the structures on-site is included as Figure 2. A copy of the site specific Health and Safety Plan is
included as Appendix B.
2.0 RECEPTOR INFORMATION
Water Supply Wells:
According to the information determined during receptor survey activities conducted on March 14, 2022,
no water supply wells were identified within a 1,500-foot radius of the site. A Site Vicinity Map is included
as Figure 2A.
Public Water Supplies:
Public water is available to the site and all of the surrounding properties. Water lines run along the public
streets in the area. Public water is supplied by Salisbury-Rowan Utilities.
Surface Water:
No surface water bodies were identified within a 500-foot radius of the site during the March 14, 2022,
receptor survey.
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
3
Wellhead Protection Areas:
On August 22, 2023, GRI personnel accessed the NCDEQ SWAP Program’s website to identify wellhead
protection areas in the vicinity of the subject site. The site is not located within a wellhead protection
area.
Deep Aquifers in the Coastal Plain Physiographic Region:
The site is not located in the Coastal Plain Physiographic Region.
Subsurface Structures:
No structures with basements were observed in the vicinity of the source area. Public utilities in the
source area are located along West Innes Street and Statesville Boulevard, and do not appear to intersect
the seasonal high ground water table.
3.0 LAND USE
The site is currently occupied by a petroleum retail facility and convenience store. The closest primary
residence is located approximately 400 feet northeast of the source area. The buildings of the Catawba
College are located as little as 1,080 feet northeast of the source area. The Salisbury VA Medical Center
is located approximately 1,130 feet to the southwest of the source area. Knox Junior High School, which
is currently closed for renovations and new construction, is located approximately 1,460 feet east of the
source area. The adjoining properties are commercial. According to the City of Salisbury Official Zoning
Map, the surrounding areas are zoned commercial or residential. Adjacent property owner information
and land use information is summarized in Table 3 and Table 4. Land use and zoning information is
included on Figure 2B.
4.0 SOIL ASSESSMENT
During due diligence activities conducted in October 2021, reportable soil violations were identified at the
site.
During the installation of monitoring well MW-1, soil samples were collected at 10-foot intervals above
the seasonally high ground water table (MW-1-5’, MW-1-15’, and MW-1-15’) and submitted for laboratory
analysis of VOCs by EPA Method 8260B and VPH by the MADEP method. The reported contaminant
concentrations of benzene, toluene, xylenes, MTBE, naphthalene, TBA, p-isopropyltoluene, n-
propylbezene, and/or C9-C10 aromatics reported in soil samples MW-1-5’, MW-1-15’, and MW-1-25’
exceeded the soil-to-water MCCs. All target contaminant concentrations were below the residential SCLs.
Between February 20, 2023, and February 21, 2023, monitoring wells MW-2 through MW-4 and
telescoping well TW-1 were installed at the site. Soil samples (MW-2-15’, MW-2-25’, MW-3-15’, MW-3-
25’, MW-4-15’, MW-4-25’, TW-1-15’, and TW-2-25’) were collected from 15 feet BGS and 25 feet BGS
during the installation of each new well. The soil samples were submitted for TPH-GRO analysis with UVF
technology. The TPH-GRO concentration in soil sample MW-4-25 exceeded the RAL.
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
4
No soil assessment activities were conducted during the August 2023 CSA activities. Historical soil
sampling analytical results are included in Table 5.
Clean, disposable nitrile gloves were used for the collection of the soil samples. The samples were
collected in laboratory supplied containers and shipped to the laboratory in a cooler following proper
chain-of-custody procedures.
5.0 GROUND WATER ASSESSMENT
On March 14, 2022, during LSA activities, one Type II monitoring well (MW-1) was installed to a total depth
of 35 feet BGS with a 20-foot screened interval. Monitoring well MW-1 was sampled after the March 14,
2022 installation. The reported contaminant concentrations of benzene, toluene, ethylbenzene, xylenes,
MTBE, naphthalene, TAA, TBA, isopropylbenzene, IPE, n-propylbenzene, 1,2,4-trimethylbenzene, 1,3,5-
trimethylbenzene, EDB, lead, C5-C8 aliphatics and C9-C10 aromatics reported in the ground water sample
collected from MW-1 exceeded the MACs. The reported concentration of benzene in the ground water
sample collected from MW-1 exceeded the GCL. Free product was not observed at the site. Based on the
results of the LSA, an ARA was negotiated to be conducted prior to the CSA directed by the NCDEQ.
On February 20, 2023, and February 21, 2023, three additional Type II monitoring wells (MW-2 through
MW-4) and one Type III monitoring well (TW-1) were installed at the site during the ARA activities.
Monitoring wells MW-2 through MW-4 were installed to a total depth of 30 feet with a 10-foot screened
interval. Telescoping well TW-1 was installed to a total depth of 55 feet with a 5-foot screened interval.
A comprehensive sampling event was conducted on March 1, 2023. The concentrations of benzene,
toluene, ethylbenzene, xylenes, MTBE, naphthalene, acetone, TAA, TBA, 1,2-dichloroethane, 2-hexanone,
isopropylbenzene, di-isopropyl ether, methylene chloride, MIBK, n-propylbenzene, styrene, 1,2,4-
trimethylbenzene, 1,3,5-trimethylbenzene, EDB, C5-C8 aliphatics, C9-C12 aliphatics, and/or C9-C10
aliphatics reported in the ground water samples collected from MW-1 through MW-4 exceeded the MACs.
The reported concentrations of benzene and/or MTBE reported in the ground water samples collected
from MW-1 and MW-4 exceeded the GCLs. Free product was not observed at the site. Based on the
results from the ARA activities, a CSA was requested by the NCDEQ.
On August 11, 2023, three Type II monitoring wells (MW-5 through MW-7) were installed as part of the
CSA activities. Monitoring wells MW-5 through MW-7 were drilled to a total depth of 30 feet with a 10-
foot screened interval. Well photos are included in Appendix C.
After the additional wells were installed, a comprehensive sampling event was conducted. On August 24,
2023, seven Type II monitoring wells and one Type III telescoping well were gauged, purged, and sampled.
The reported contaminant concentrations of benzene, toluene, ethylbenzene, xylenes, MTBE,
naphthalene, tert-amyl alcohol (TAA), tert-butyl alcohol (TBA), 2-hexanone, isopropylbenzene, MIBK, n-
propylbenzene, IPE, styrene, 1,2,4-triethylbenzene, 1,3,5-trimethylbenzene, lead, C5-C8 aliphatics, C9-
C12 aliphatics and/or C9-C10 aromatics in the ground water samples collected from MW-1 through MW-
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
5
7 exceeded the MACs. The reported benzene, TAA and TBA contaminant concentrations in the ground
water sample collected from MW-1 exceeded the GCLs. The reported benzene contaminant
concentration in the ground water sample from MW-4 exceeded the GCL. No free product was
encountered at the site during the CSA activities. Based on the established site cleanup goals, it was
determined that no additional delineation is required at this time. A summary of the August 24, 2023,
ground water analytical data is shown below:
Contaminant
of Concern
Be
n
z
e
n
e
To
l
u
e
n
e
Et
h
y
l
b
e
n
z
e
n
e
Xy
l
e
n
e
s
MT
B
E
Na
p
h
t
h
a
l
e
n
e
Well
ID
MACs (μg/l) 1 600 600 500 20 6
GCL (μg/l) 5,000 260,000 80,000 50,000 20,000 6,000
MW-1 13,000 30,800 3,220 16,500 11,300 1,150
MW-2 161 66.0 43.9 J 44.2 J 713 <47.0
MW-3 1,340 13,400 4,170 17,800 16.5 1,130
MW-4 22,100 46,900 3,180 18,600 15,400 892
MW-5 760 1,150 2,560 10,300 7,580 1,310
MW-6 4,530 27,400 3,900 17,200 <14.0 1,080
MW-7 1.36 3.11 0.668 2.75 30.0 <0.470
TW-1 <0.180 <0.220 <0.170 0.211 J <0.140 <0.470
All samples were collected in accordance with the NCDEQ guidelines. Clean, disposable bailers and nitrile
gloves were used for the collection of the ground water samples. The samples were collected in
laboratory supplied containers and shipped to the laboratory in a cooler following proper chain-of-custody
procedures. A laboratory supplied trip blank was included in the sample cooler. No detectable
concentrations of requested method constituents were reported in the trip blank.
The locations of the monitoring wells are shown on Figure 3. Well construction records and boring logs
for the monitoring wells installed during CSA activities is included as Appendix D.
Cross sections A-A’ and B-B’ are included as Figure 4 and Figure 5; the lines of cross section are included
on Figure 3. A Ground Water Quality Map for the August 2023 ground water sampling event is included
as Figure 6. Contaminant specific isoconcentration maps for benzene, TAA, and TBA are included as
Figure 7, Figure 8, and Figure 9, respectively. A summary of laboratory analyses for the ground water
samples collected during CSA activities is included as Table 6. Complete copies of the laboratory reports
for the ground water samples are included as Appendix E.
The baseline contaminant mass at the site was determined based on the total BTEX, Naphthalene, and
MTBE concentrations from the August 2023 ground water sampling event, as well as the maximum
historical water column height. Three theoretical contaminant mass areas were calculated. Area 1
contains MW-1 and MW-4, Area 2 contains MW-3 and MW-6, and Area 3 contains MW-2 and MW-5.
Contaminant mass calculations are included as Appendix F. A map of the estimated contaminant mass
area is included as Figure 10.
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
6
6.0 HYDROGEOLOGIC INVESTIGATION
The depths to ground water in the Type II monitoring wells (MW-1 through MW-7) measured on August
24, 2023, ranged from 21.96 to 25.38 feet below the tops of well casings. Ground water elevations at the
site, based on an assumed datum of 100 feet, ranged from 74.74 to 77.41 feet relative to a temporary
benchmark. Based on this information, the ground water flow direction was generally toward the
northeast. The horizontal hydraulic gradient across the site was approximately 0.03 feet per foot. The
vertical hydraulic gradient calculated for paired wells MW-1/TW-1 was approximate 0.02 feet per foot in
the upward direction. A summary of ground water elevation data obtained during assessment activities
to date is included in Table 7. A Water Table Surface Map based on the August 24, 2023, gauging data is
included as Figure 10.
Rising head slug tests were conducted in MW-1, MW-2 and TW-1 on March 1, 2023. Hydraulic
conductivities in the Type II monitoring wells calculated using the Bouwer and Rice method, ranged from
4.028 x 10-5 feet per minute (0.058 feet per day) to 6.052 x 10-5 feet per minute (0.08715 feet per day). The
average hydraulic conductivity was 5.055 x 10-5 feet per minute (0.072575 feet per day). Seepage
velocities, calculated using the equation V = k(dh/dl)/ne, ranged from 5.80 x 10-3 to 8.71 x 10-3 feet per day
(2.12 to 3.18 feet per year). The average seepage velocity was 7.255 x 10-3 feet per day (2.65 feet per
year). The hydraulic conductivity in the Type III monitoring well calculated using the Bouwer and Rice
method was 3.126 x 10-4 feet per minute (0.4501 feet per day). The seepage velocity calculated for the
Type III monitoring well was 4.50 x 10-2 feet per day (16.40 feet per year). A summary of the results of
slug test analyses is presented in Table 8.
7.0 REGIONAL GEOLOGY AND HYDROGEOLOGY
According to the 1985 Geologic Map of North Carolina, the site is located within the Charlotte Belt. The
bedrock is generally described as interbedded felsic to mafic tuffs and flowrock. Based on observations
made during the assessment activities, surficial soils observed at the site consist of various clays and silts
to varying depths, with lenses of weathered rock. Ground water flow was generally toward the northeast.
The vertical hydraulic gradient was upward.
8.0 SITE GEOLOGY AND HYDROGEOLOGY
Based on observations made during assessment activities, surficial soils observed at the site consist of
various clays, silts and sands to varying depths (approximately 7 to 28 feet) where weathered rock is
encountered, grading into competent granitic rock. A summary of the current ground water gauging data
is shown below:
Well ID
Screened
Interval
(x to y ft.
BGS)
Bottom
of Well
(ft. BGS)
Top of
Casing
Elevation
(ft.)
Depth to
Water from
Top of Casing
(feet)
Free
Product
Thickness
(ft.)
Ground
Water
Elevation
(ft.)
MW-1 15 - 35 35 100.00 22.98 --- 77.02
MW-2 20 - 30 30 99.91 23.34 --- 76.57
MW-3 20 - 30 30 99.92 23.01 --- 76.91
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
7
MW-4 20 - 30 30 99.53 22.59 --- 76.94
MW-5 20 - 30 30 100.12 25.38 --- 74.74
MW-6 20 - 30 30 100.10 23.48 --- 76.62
MW-7 20 - 30 30 99.37 21.96 --- 77.41
TW-1 50 - 55 55 100.43 22.90 --- 77.53
On August 24, 2023, monitoring wells MW-1 through MW-7 and telescoping well TW-1 were gauged,
purged, and sampled. Depths to ground water in the Type II monitoring wells ranged from 21.96 to 25.38
feet below the tops of well casings. Ground water elevations at the site, based on an assumed datum of
100.00 feet, ranged from 74.74 to 77.41 feet. Ground water flow was generally toward the northeast.
9.0 DISCUSSION
During due diligence activities conducted in October 2021, reportable soil violations were identified at the
site, and an LSA was required by the NCDEQ.
To date, seven Type II monitoring wells and one telescoping well have been installed to determine the
horizontal and vertical extent of the release. Monitoring wells MW-1 and MW-4 contained the highest
ground water contamination levels during the CSA activities with the GCLs below the reported
concentrations of benzene, TBA and/or TAA. Please note that MW-1 and MW-4 are also in the vicinity of
the UST basin and dispensers. Free product has not been present at the site during any phase of
assessment. Based on the current risk ranking of the site, it was determined that the contaminant plume
is sufficiently delineated.
The risk ranking for the site has been established as intermediate due to GCL exceedances in the ground
water. In order to lower the risk ranking of the site, ground water sampling should continue at the site
until ground water concentrations are below GCLs.
10.0 CONCLUSIONS AND RECOMMENDATIONS
No further soil assessment should be required.
Ground water flow direction is to the northeast.
The ground water contaminant plume is defined to the level of GCL concentrations for the site
specific cleanup goals.
Based on this site assessment, the site risk classification should remain intermediate.
MMPE events should be conducted on MW-1, MW-4, and MW-6 to reduce contaminants.
Ground water sampling should continue until ground water concentrations are below GCLs.
GRI recommends comprehensive ground water sampling should be conducted at the site in March
2024. Based on the results of the March 2024 sampling event, further recommendations can be
made.
11.0 PUBLIC NOTICE
Copies of the applicable portions of this CSA report have been forwarded to the appropriate local officials
by certified mail. Copies of the cover letters have been included in Appendix G.
___________________________________________________________________________________________
Prepared by: Geological Resources, Inc. Comprehensive Site Assessment Report
Prepared on: October 9, 2023 Former Rushco Food Store #4
Project Manager: Samuel McKay III, P.G. GRI Project No. 5721
8
12.0 LIMITATIONS
This report has been prepared for the exclusive use of Rusher Oil Company, Inc. for specific application to
the referenced site in Rowan County, North Carolina. The assessment was conducted based on the scope
of work and level of effort desired by the NCDEQ and with resources adequate only for that scope of work.
Our findings have been developed in accordance with generally accepted standards of environmental
practices in the State of North Carolina, available information, and our professional judgment. No other
warranty is expressed or implied.
The data that is presented in this report is indicative of conditions that existed at the precise locations
sampled and at the time the samples were collected. In addition, the data obtained from samples would
be interpreted as being meaningful with respect to parameters indicated in the laboratory report. No
additional information can logically be inferred from this data.
13.0 REFERENCES
Additional Risk Assessment Report, Former Rushco Food Store #4, Geological Resources, Inc., April 3, 2023
Bouwer, H., 1989, The Bouwer and Rice slug test - an update, Ground Water, vol.27, no. 3, pp.304-309
Bouwer, H. and R.C. Rice, 1976, A slug test method for determining hydraulic conductivity of unconfined
aquifers with completely or partially penetrating wells, Water Resources Research, vol. 12, no.3,
pp. 423-428
Department of Natural Resources and Community Development, 1985, Geologic Map of North Carolina,
1 sheet
Fetter, C. W., 1988, Applied Hydrogeology, Second Edition, Macmillan Publishing Company, 592 p.
North Carolina Department of Environment and Natural Resources, 2000, Ground Water Section
Guidelines for the Investigation and Remediation of Soil and Ground Water, 79 p.
North Carolina Department of Environmental Quality, Division of Waste Management – UST Section
Assessment Guidelines: Petroleum and Hazardous Substances UST Releases; Petroleum Non-UST
Releases, January 19, 2021 Version
Phase I Limited Site Assessment Report, Former Rushco Food Store #4, Geological Resources, Inc., April
29, 2022
FIGURES
SITE LOCATION
Figure 1
Site Location
Rushco Food Store 4
1901 West Innes Street
Salisbury, North Carolina
Rowan County
Incident No. 48124
GRI Project No. 5721
500 M
2000 FT
Date: 02/12/2022 Location: 35.686822° N -80.483554° W
D
a
d
SITE
5750-08-98-7160
5750-08-97-4915
5750-08-98-3254
5750-08-98-4156
5750-08-98-4275
5750-08-97-6839
5750-08-98-3010
W INNES ST
BRENNER AV
LANTZ AV
MAHALEY AV
W PARK RD
E PARK RD
SUMMIT AV
YOST ST
LILLY AV
STATESVILLE BLVD
S LINK AV
ROBIN RD
W CORRIHER AV
PARKVIEW CIR
E CORRIHER AV
OVERMAN AV
EMERALD ST
CATAWBA RDFAIRSON AV
KING ST
N LINK AV
TRUSTEE CIR
WALKER ST
COLONY RD
BARRINGER ST
BRAWLEY AV
BRODBECK DR
S MERRITT AV
HILLCREST PL
SCHOFIELD PL
S LINK AV
BRAWLEY AV
FIGURE 2A: SITE VICINITY MAPRUSHCO FOOD STORE 41901 WEST INNES STREETSALISBURY, ROWAN COUNTYNORTH CAROLINAINCIDENT NO. 48124GRI NO. 5721
PREPARED BY:GEOLOGICAL RESOURCES, INC.FEBRUARY 10, 2022
³
1,500-FOOT RADIUS
1,000-FOOT RADIUS
250-FOOT RADIUS
0 300150Feet1 inch = 300 feet
500-FOOT RADIUS
3
1
2
4
5
6 7
LEGEND
Centerlines
newstreams
Adjacent Properties
Tax_Parcels
1 Land Use Code
SITE
W INNES ST
BRENNER AV
LANTZ AV
MAHALEY AV
W PARK RD
E PARK RD
SUMMIT AV
YOST ST
LILLY AV
STATESVILLE BLVD
S LINK AV
ROBIN RD
W CORRIHER AV
PARKVIEW CIR
E CORRIHER AV
OVERMAN AV
EMERALD ST
CATAWBA RDFAIRSON AV
KING ST
N LINK AV
TRUSTEE CIR
WALKER ST
COLONY RD
BARRINGER ST
BRAWLEY AV
BRODBECK DR
S MERRITT AV
HILLCREST PL
SCHOFIELD PL
S LINK AV
BRAWLEY AV
FIGURE 2B: ZONING MAPRUSHCO FOOD STORE 41901 WEST INNES STREETSALISBURY, ROWAN COUNTYNORTH CAROLINAINCIDENT NO. 48124GRI NO. 5721
PREPARED BY:GEOLOGICAL RESOURCES, INC.FEBRUARY 10, 2022
³
1,500-FOOT RADIUS
1,000-FOOT RADIUS
250-FOOT RADIUS
0 300150Feet1 inch = 300 feet
500-FOOT RADIUS
3
1
2
4
5
6 7
LEGEND
Centerlines
newstreams
ZONING - UR8
ZONING - HS
ZONING - NMX
ZONING - OSP
ZONING - GR6
ZONING - UR12
ZONING - CI
ZONING - RMX
ZONING - CMX
Tax_Parcels
1 Land Use Code
TABLES
UST ID Number 1-3 Facility ID Number
Owner or Operator?
Owner/Operator
UST ID Number 1-3 Facility ID Number
Owner or Operator?
Owner/Operator
UST ID Number 1-3 Facility ID Number
Owner or Operator?
Owner/Operator
UST ID Number 1 & 2 Facility ID Number
Owner or Operator?
Owner/Operator
Address Telephone Number
Unknown Unknown
00-0-00000030414
Name of Owner or Operator Dates of Ownership / Operation
Unknown 09/26/1969 - 09/26/1971
Address Telephone Number
P.O. Box 1483, Salisbury, NC, 28145 704-633-3211
00-0-00000030414
Name of Owner or Operator Dates of Ownership / Operation
Rusher Oil Company, Inc.08/17/2004 - 11/10/2021
Address Telephone Number
Unknown Unknown
00-0-00000030414
Name of Owner or Operator Dates of Ownership / Operation
Unknown 09/26/1971 - 08/17/2004
00-0-00000030414
TABLE 1
UST OWNER/OPERATOR INFORMATION
RUSHCO #4 (INCIDENT NO. 48124)
P.O. Box 469, Clinton, NC 28328 910-862-3197
Name of Owner or Operator Dates of Ownership / Operation
Sampson-Bladen Oil Com 11/10/2021
Address Telephone Number
Page 1 of 1
Was Release
Associated
with UST
System?
(Yes / No)
1 Gasoline,
Gas Mix NA 10,000 9/26/1969 Single Wall Steel Unknwon Single Wall FRP Current Yes
2 Gasoline,
Gas Mix NA 10,000 9/26/1969 Single Wall Steel Unknwon Single Wall FRP Current No
3 Gasoline,
Gas Mix NA 7,500 9/26/1971 Single Wall Steel Unknwon Single Wall FRP Current No
TABLE 2
UST SYSTEM INFORMATION
RUSHCO #4 (INCIDENT NO. 48124)
UST
ID
No.
Current
or Most
Recent
Contents
Previous
Contents
Capacity
(gallons)
Date
Installed
Construction
Details
Tank
Dimensions
Description of
Associated
Product Piping
and
Pumps
Status
of
UST
Facility ID #: 00-0-0000030414Date: 02/10/22
Page 1 of 1
Date: 03/21/23 Facility ID #: 00-0-0000030414
Parcel ID PIN Number Property Owner Name Property Owner Address
001 105 (Site)5750-08-98-4156 Sampson-Bladen Oil Company P.O. Box 469
Clinton, NC, 28329-0469
001 106 5750-08-98-3254 Rusher Oil Company P.O. Box 1483
Salisbury, NC, 28145
001 104 5750-08-98-4275 Rusher Oil Company P.O. Box 1483
Salisbury, NC, 28145
021 043 5750-08-98-7160 DLP Salisbury C/O Walgreen Co.P.O. Box 901
Deerfield, IL, 60015
021 021 5750-08-97-4915 Rima Estate, LLC 11340 Twin Lakes Drive,
Orland Park, IL, 60647
021 020 5750-08-98-3010 Jeo Realty, LLC 207 Ferris Avenue,
Rockwell, NC, 28138
021 019A 5750-08-98-2014 James Owen Management, LLC 208 Ferris Avenue,
Rockwell, NC, 28138
Note:
• Properties are keyed to Figure 2A.
TABLE 3
ADJACENT PROPERTY OWNER INFORMATION
RUSHCO #4 (INCIDENT NO. 48124)
Page 1 of 1
Date: 02/10/22 Facility ID # : 00-0-0000030414
Map ID No.Land Use Feature Zoning Description Address
Distance from
Source Area
(feet)
1 Catabwa College CI College 2300 West Innes Street, Salisbury,
NC ~1,145
2 Noah's Play Loft Preschool UR8 Preschool 305 South Link Street, Salisbury, NC ~1,325
3 Temple Israel UR8 Church 1600 Brenner Avenue, Salisbury, NC
28144 ~1,150
4 W.G. Hefner VA Medical
Center HS Hospital 1601 Brenner Avenue, Salisbury, NC
28144 ~1,400
5 John Calvin Prebyterian
Church UR8 Church 1620 Brenner Avenue, Salisbury, NC
28144 ~955
6 Mission House CMX Church 121 Statesville Boulevard, Salisbury,
NC ~185
7 Iglesia Nuevo Renacer CMX Church 126 Statesville Boulevard, Salisbury,
NC 28144 ~250
n/a CMX Corridor Mixed Use n/a n/a
n/a UR8 Urban Residential 8 n/a n/a
n/a UR12 Urban Residential 12 n/a n/a
n/a CI Community/
Institutional n/a n/a
n/a NMX Neighborhood Mixed
Use n/a n/a
n/a GR6 General Residential 6 n/a n/a
n/a RMX Residential Mixed Use n/a n/a
Note:
• Properties are keyed to Figure 2B.
TABLE 4
LAND USE INFORMATION
RUSHCO #4 (INCIDENT NO. 48124)
Page 1 of 1
Date: 10/12/2021 Facility ID #: 00-0-0000030414
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0.0072 5.4 8 6 0.085 0.2 0.04 2.4 2.2 1.3 0.12 1.4 0.9 0.005 6.6 6.6 68 540 31
12 1,250 60.3 3,120 156 5.5 1,400 782 1,560 1,560 1,560 1,560 3,120 93.8 156 156 625 1,560 469
59.4 18,600 297 46,700 1,810 27 21,000 11,600 23,300 23,300 23,300 23,300 46,700 1,400 2,330 2,330 9,340 23,300 7,000
SB-1-10'10/12/21 10 0.069 J 3.76 3.86 23.0 <0.020 3.09 <0.032 1.13 0.378 0.675 0.246 2.80 <0.045 0.060 J 18.6 5.25 NR NR NR
SB-2-15'10/12/21 15 <0.019 0.031 J 0.394 1.30 J 0.077 J 5.12 <0.033 0.916 0.261 0.130 J 0.396 0.502 <0.047 <0.030 3.84 1.60 NR NR NR
SB-3-5'10/12/21 5 0.020 0.002 J 0.012 0.018 J 0.012 <0.001 0.038 J <0.0006 <0.0006 0.0008 J <0.001 0.001 J <0.001 <0.001 0.001 J 0.002 J NR NR NR
SB-4-10'10/12/21 10 16.9 459 221 1,210 <0.212 97.8 <0.340 21.3 7.49 19.2 3.74 65.9 3.97 <0.309 473 113 NR NR NR
SB-5-10'10/12/21 10 0.132 0.004 J 0.031 0.033 0.084 0.001 J 0.057 J <0.0007 <0.0008 0.001 J <0.001 0.003 J <0.001 <0.001 0.003 J 0.002 J NR NR NR
MW-1-5'03/14/22 5 0.295 E <0.010 1.53 J 9.79 J 0.289 E 0.319 E 25.4 E 0.111 0.0500 0.158 0.131 0.977 J <0.0010 <0.0013 6.68 2.24 J 27.8 <2.6 52.5
MW-1-15'03/14/22 10 NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR NR 32.7 <2.6 52.2
MW-1-25'03/14/22 15 0.921 J 9.39 J 6.57 38.8 1.43 J 4.08 2.77 E 1.28 J <0.0011 0.892 J 39.9 E 3.43 <0.67 <0.86 23.5 7.48 38.0 <2.3 90.8
Notes:
• Results reported in mg/kg (milligrams per kilograms)
• Trip Blank results reported in ug/l (micrograms per liter)
• ft-BGS: feet below ground surface.
• RAL: Regulatory Action Level.
• MCCs: Maximum Contaminant Concentrations (soils).
• SCLs: Soil Cleanup Levels.
• < : Less than the method detection limit specified in the laboratory report
• Concentrations in bold face type indicate the soil to water MCCs were below the reported concentrations.
• Concentrations in italic type indicate the Residential SCLs were below the report concentrations.
• Concentrations in underline type indicate the Industrial SCLs were below the report concentrations.
• NE: Not Established
• NR: Not Requested.
• E: Indicates value exceeds calibration range.
SW846 8260D
TABLE 5
SUMMARY OF SOIL SAMPLE ANALYTICAL RESULTS
RUSHCO #4 (INCIDENT NO. 48124)
MADEP VPH
Industrial SCLs (mg/kg)
Soil to Water MSCC (mg/kg)
Analytical Method
Residential SCLs (mg/kg)
Page 1 of 1
Date: 03/21/23 Facility ID #: 00-0-0000030414
EPA 504.1 SW846 6010D
Well
ID
Date Sampled
(mm/dd/yy)
1 600 600 500 20 6 6,000 40 10 0.4 40 70 70 5 100 70 70 400 400 0.02 15 400 700 200
5,000 260,000 80,000 50,000 20,000 6,000 6,000,000 40,000 10,000 400 40,000 30,500 70,000 5,000 100,000 26,100 70,000 28,500 24100 50 15,000 NE NE NE
03/14/22 5,710 11,300 4,200 13,700 3,740 829 *17,500 5,210 J **130 J 276 J **411 J *2,470 707 0.025 74.7 10,800 <35 5,860
03/01/23 6,290 6,390 2,420 6,320 4,070 543 J <1,800 10,700 3,220 J 9.94 186 101 300 <3.30 132 281 48.6 1,710 381 NR NR NR NR NR
08/24/23 13,000 30,800 3,220 16,500 11,300 1,150 3,020 41,400 17,600 <15.0 238 107 602 <33.0 151 296 71.8 2,170 546 NR NR NR NR NR
03/01/23 91.1 60.2 971 657 458 662 <18.0 348 512 <1.50 <3.80 80.6 47.6 7.14 J 14.1 190 32.8 867 39.8 <0.0222 <2 2,180 1,930 4,320
08/24/23 161 66.0 43.9 J 44.2 J 713 <47.0 <180 1,000 <35.0 <15.0 <38.0 <18.0 51.3 <33.0 <7.80 30.2 J <22.0 45.4 J <18.0 NR NR NR NR NR
03/01/23 3,430 21,400 4,490 19,100 32.7 918 <18.0 196 <16.0 <1.50 <3.80 104 9.03 <3.30 <0.780 296 170 2,210 547 <0.0206 <2 26,400 15,200 5,660
08/24/23 1,340 13,400 4,170 17,800 16.5 1,130 <1.80 440.50 E 11.4 <0.150 <0.380 117 3.91 <0.330 <0.078 330 163 2,860 701 NR NR NR NR NR
03/01/23 26,900 54,700 4,130 19,600 32,400 967 6,600 J 23,700 4,670 J <1.50 233 100 1,190 <3.30 <0.780 307 155 2,450 588 0.810 3 J 51,400 15,600 5,690
08/24/23 22,100 46,900 3,180 18,600 15,400 892 1,590 5,310 1,420 <15.0 <38.0 84.9 686 <33.0 <7.80 234 135 2,060 552 NR NR NR NR NR
MW-5 08/24/23 760 1,150 2,560 10,300 7,580 1,310 495 J 858 J 877 J <15.0 <38.0 130 232 <33.0 <7.80 372 102 2,740 668 <0.0207 2 J 5,650 5,990 10,300
MW-6 08/24/23 4,530 27,400 3,900 17,200 <14.0 1,080 831 J 2,260 <160 <15.0 <38.0 101 135 <33.0 <7.80 308 206 2,260 551 <0.0207 6 33,100 14,900 7,430
MW-7 08/24/23 1.36 3.11 0.668 2.75 30.0 <0.470 18.2 24.8 14.4 <0.150 <0.380 <0.180 9.05 0.454 J <0.078 <0.190 <0.220 0.769 0.256 J <0.0208 8 89.2 26.0 <4.02
03/01/23 0.508 3.31 1.21 5.16 0.496 J <0.470 32.1 <1.90 <1.60 <0.150 <0.380 <0.180 <0.500 <0.330 <0.078 <0.190 <0.220 1.40 0.461 J <0.0208 <2 <11.5 37.0 J 13.9 J
08/24/23 <0.180 <0.220 <0.170 0.211 J <0.140 <0.470 5.58 J <1.90 <1.60 <0.150 <0.380 0.222 J <0.500 <0.330 <0.078 <0.190 <0.220 <0.190 <0.180 NR NR NR NR NR
03/14/22 <0.13 <0.13 <0.13 <0.25 <0.13 <0.13 *NR NR **<0.13 <0.13 **<0.13 *<0.13 <0.13 NR NR NR NR NR
03/01/23 <0.180 <0.220 <0.170 <0.210 <0.140 <0.470 <1.80 NR NR <0.150 <0.380 <0.180 <0.500 0.336 J <0.078 <0.190 <0.220 <0.190 <0.180 NR NR NR NR NR
08/24/23 <0.180 <0.220 <0.170 <0.21 <0.140 <0.470 <1.80 NR NR <0.150 <0.380 <0.180 <0.500 <0.330 <0.078 <0.190 <0.220 <0.190 <0.180 NR NR NR NR NR
Notes:
• Results reported in micrograms per liter (µg/l).
• MAC: Maximum Allowable Concentration as specified in T15A NCAC 2L.0202.
• 2B Standard: North Carolina surface water standards for Class C waters specified in T15A NCAC 2B.0200 or EPA Nathional Criteria.
• < : Less than the method detection limit specified in the laboratory report.
• GCL: Gross contamination level.
• Concentrations in bold face type indicate the MAC was below the reported concentration.
• Underlined results indicate 10 times the 2B Standards were below the reported concentrations.
• Results in italics indicate the GCLs were below the reported concentrations.
• J: Estimated value.
• NE: Not established.
• S: Toxicity exceeds solubility, no visible sheen or free product in water or on sediment or shoreline per 15A NCAC 02B .0211 & .0220
• NR: Not reported.
TABLE 6
SUMMARY OF GROUND WATER SAMPLE ANALYTICAL RESULTS
RUSHCO #4 (INCIDENT NO. 48124)
Analytical Method
SM 6200B MADEP VPH REV 2.1
Contaminant of Concern
Be
n
z
e
n
e
To
l
u
e
n
e
Et
h
y
l
b
e
n
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e
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e
To
t
a
l
X
y
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e
s
C9
-
C
1
0
A
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a
t
i
c
s
Le
a
d
C5
-
C
8
A
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C9
-
C
1
2
A
l
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P
r
o
p
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o
p
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o
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Me
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(M
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-
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r
t
-
A
m
y
l
a
l
c
o
h
o
l
(T
A
A
)
• Refer to laboratory report for other detectable concentrations which did not exceed the MACs.
MAC (μg/l)
GCL (μg/l)
te
r
t
-
B
u
t
y
l
a
l
c
o
h
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l
(T
B
A
)
Me
t
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-
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(M
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B
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)
Na
p
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1,
2
-
D
i
b
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(E
D
B
)
1,
2
,
4
-
T
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b
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1,
3
,
5
-
T
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t
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b
e
n
z
e
n
e
Trip Blank
MW-4
MW-3
MW-2
MW-1
TW-1
Facility ID #: 00-0-0000030414
Well ID Date Installed
(mm/dd/yy)
Date Water
Level
Measured
(mm/dd/yy)
Well Casing
Depth
(ft. BGS)
Screened
Interval
(x to y ft.
BGS)
Bottom
of Well
(ft. BGS)
Top of
Casing
Elevation
(ft.)
Depth to
Water from
Top of Casing
(ft.)
Free Product
Thickness
(ft.)
Groundwater
Elevation
(ft.)
Comments
03/14/22 NM 23.73 ---NM
03/01/23 23.88 ---76.12
08/24/23 22.98 ---77.02
03/01/23 25.35 ---74.56
08/24/23 23.34 ---76.57
03/01/23 23.96 ---75.96
08/24/23 23.01 ---76.91
03/01/23 23.51 ---76.02
08/24/23 22.59 ---76.94
MW-5 08/11/23 08/24/23 20 20-30 30 100.12 25.38 ---74.74
MW-6 08/11/23 08/24/23 20 20-30 30 100.10 23.48 ---76.62
MW-7 08/11/23 08/24/23 20 20-30 30 99.37 21.96 ---77.41
03/01/23 23.87 ---76.56
08/24/23 22.90 ---77.53
Notes:
• ft BGS : feet below ground surface.
• NM: Not measured.
TABLE 7
WELL CONSTRUCTION AND GAUGING INFORMATION
RUSHCO #4 (INCIDENT NO. 48124)
Date: 08/25/23
3515-3515
3020-30
50
20
20
20
30
30
5550-55
20-30
20-30
02/21/23
02/20/23
02/20/23
02/20/23
03/14/22
TW-1
MW-4
MW-3
MW-2
MW-1
100.43
99.53
99.92
99.91
100.00
Page 1 of 1
Facility ID#: 0-030414
ft/min ft/day ft/day ft/year
MW-2 4.028E-05 5.800E-02 5.80E-03 2.12E+00
MW-3 6.052E-05 8.715E-02 8.71E-03 3.18E+00
TW-1 3.126E-04 4.501E-01 4.50E-02 1.64E+01
Note:
Seepage velocities calculated using the equation v = K(dh/dl)/ne , where:
K = hydraulic conductivity
ne = effective porosity = 0.20
dh/dl = hydraulic gradient = 0.02 ft/ft
TABLE 8
SUMMARY OF SLUG TEST ANALYSES
RUSHCO #4 (INCIDENT NO. 48124)
Date : 03/21/2023
Well Hydraulic Conductivity (K)Seepage Velocity (v)
Page 1 of 1
APPENDICES
APPENDIX A
State Correspondence
North Carolina Department of Environmental Quality | Division of Waste Management
Mooresville Regional Office | 610 East Center Avenue | Suite 301 | Mooresville, NC
28115 | (704) 663-1699
May 5, 2023
Rusher Oil Company Inc.
Joey Rusher 2201 Executive Drive Salisbury, NC 28147
Re: Notice of Regulatory Requirements 15A NCAC 2L .0407 (d) Risk-Based Assessment and Corrective Action for Petroleum Underground Storage Tanks
Former Rushco Food Store #4 1901 West Innes Street Salisbury, Rowan County Incident Number: 48124
Risk Classification: Intermediate
Dear Mr. Rusher:
The Additional Risk Assessment Report received by the UST Section, Division of Waste Management, on April 3, 20232 has been reviewed. The risk posed by the discharge or release at the subject site is classified
by the Department of Environmental Quality as intermediate, as stipulated under Title 15A NCAC 2L .0406. The land use at the site is classified as industrial/commercial. Title 15A NCAC 2L .0407(d) requires you to notify the Department of any changes that might affect the risk or land use
classifications that have been assigned.
Title 15A NCAC 2L .0407 (d) requires you to comply with assessment and cleanup requirements of Title 15A NCAC 2N .0706 and Title 15A NCAC 2L .0106(c) and 2L .0106(g). A Comprehensive Site Assessment (CSA) Report prepared in accordance with these requirements and the most recent version of the UST Section Assessment Guidelines must be received by this office within 90 days of the date of this notice. In addition, you must submit a summary of the CSA Report to the local
Health Director and the local Chief Administrative Officer in accordance with 15A NCAC 2L .0114. The summary should be submitted to these persons no later than five working days after submittal of the CSA Report to this office. Failure to comply in the manner and time specified, may result in the assessment of civil penalties and /or the use of other enforcement mechanisms.
The Department requires that all work following the submittal of the Limited Site Assessment Report (Title 15A NCAC 2L .0405) be preapproved if State Trust Fund reimbursement is anticipated. To comply with this requirement, a completed Preapproval/Claim Authorization Form, encompassing the required remedial activities, must be received in this office within 14 days of the date of this letter. Upon completion of the preapproved activities, you should submit your claim promptly. Reimbursement funds are budgeted based
on completed preapprovals, but lengthy delays in reimbursement can occur if claims are not submitted immediately following work completion.
5721 Received MAY 05 2023
Page 2 of 2 Incident Number 48124 May 5, 2023
North Carolina Department of Environmental Quality | Division of Waste Management
Mooresville Regional Office | 610 East Center Avenue | Suite 301 | Mooresville, NC
28115 | (704) 663-1699
Because a release or discharge has been confirmed, a Licensed Geologist or a Professional Engineer, certified by the State of North Carolina, is required to prepare, and certify all reports submitted to the
Department in accordance with Title 15A NCAC 2L .0103(e) and 2L .0111(e).
Please note that before you sell, transfer, or request a “No Further Action” determination for a property that has not been remediated to below “unrestricted use” standards, you must file a Notice of Residual Petroleum ("Notice") with the Register of Deeds in the county where the property is located (NCGS 143B-279.9 and 143B-279.11).
If you have any questions regarding trust fund eligibility or reimbursement from the Commercial Petroleum Underground Storage Tank Cleanup Fund, please contact the UST Section Trust Fund Branch at (919) 707-8171. If you have any questions regarding the actions that must be taken or the rules mentioned in this letter, please contact Ryan Mills at Ryan.Mills@ncdenr.gov or at 704-235-2175.
Sincerely,
Ryan C Mills Environmental Program Consultant
Mooresville Regional Office UST Section, Division of Waste Management, NCDEQ
Cc: Adrian Pruett, Rowan County Health Department (Via Email) Samuel L. McKay, III, P.G., Geological Resources, Inc. (Via Email)
APPENDIX B
Site Specific Health and Safety Plan
1
GEOLOGICAL RESOURCES, INC.
Site Specific Health and Safety Plan
1.0 General Information:
a. Project name: Comprehensive Site Assessment – Rushco #4
b. Location: 1901 West Innes Street Salisbury, NC
c. GRI Job #: 5721
2.0 Project Organization:
a. Site Supervisor/H&S Officer: Sam McKay, III
b. Project Manager: Sam McKay, III
c. Subcontractor(s):
3.0 Safety Plan Preparation:
a. Prepared by & date: Sam McKay, III 7/24/2023
b. Reviewed/approved by & date:
4.0 Site History and Description:
a. Type of site (i.e., spill, leaking UST system, etc.): Comprehensive Site Assessment
b. Site/project description: MW installation, Survey
well locations
5.0 Potential Hazards:
Physical Hazards: (check)
X Slips X Overhead X Explosion X Sun burn X Electricity
X Trips utilities X Noise Cold Weather X Pressurized line/vessels
X Falls X Underground X Pinch points X Hot Weather
X Fire utilities X Burns X Crush
Chemical Hazards: (check)
X Gasoline Used Oil
Diesel Solvents
Kerosene Antifreeze
New Oil Acid (sample preservative)
Equipment/Vehicular/Other: (i.e., Geoprobe, drill rig, back hoe, track hoe, traffic, skid steer etc.)
Drill rig
Biological Hazards: (i.e., toxic insects, spiders, poisonous plants, poisonous snakes, aggressive dogs)
2
6.0 Site Organization and Safety Control: (Evaluate the need for site control to protect
persons from exposure to hazardous conditions; i.e. work permits, cones, barricade tape,
exclusion zones, etc.)
a. Work area(s) identified: ____________________________________________________
b. Work area marked ___X__ Yes _____ No
c. Work area barricaded _____ Yes _X____ No
d. Support area established:
_Yes_________________________________________________
e. Entry and escape routes identified: ___________________________________________
f. Rally point identified: _____ Yes ____ No Location:________________
g. Emergency shut-off for water identified _____ Yes _____ No
h. Emergency fuel shut-off identified _____ Yes _____ No
i. Site map attached: __X__ Yes _____ No
**Emergency Response Procedures**
Action (i.e. shut off all power equipment) Assemble at rally point
Call 911 for medical or utilities emergency Do NOT enter confined spaces
Discuss what to do if …..cut product line, water line, cable/electric line
7.0 Job Activities in Work Plan:
UST Removal X Soil Sampling Manual FP Recovery
Soil Excavation System O&M _X Survey Well locations
_X_Powered Drilling MMPE/AFVR ___ AST Removal
Hand Augering X Water sampling _X_SLUG testing
8.0 Required Education and/or Training:
X OSHA 40 hr X Annual 8 hr Refresher OSHA Site Supervisor
9.0 Air Monitoring:
If, in the opinion of the site supervisor, petroleum hydrocarbon vapor concentrations are excessive,
site activities will cease until petroleum hydrocarbon vapor concentrations diminish to acceptable
levels.
10.0 Equipment:
FID/PID Combustible gas indicator Interface Probe
O2 meter X Other UVF
11.0 Personnel Protection Equipment:
X Hard hat Rubber boots Respirator X Hearing
X Safety glasses X Work gloves Sun screen protection
X Steel toe boots X First aid kit Repellent X Nitrile
Tyvek suit X Fire extinguisher Dust mask gloves
12.0 Decontamination Procedures: (evaluate need for decon, describe procedures)
Decon between each well install, or if clean rods are not available.
4
15.0 Amendments:
a. Site Specific Health and Safety Plans are based on information available at the time of
plan preparation. Unexpected conditions may arise. It is important that personal
protective measures be thoroughly assessed prior to and during the planned activities.
Unplanned activities and/or changes in the hazard status should initiate a review of this
plan and may result in major changes to it.
b. Changes in the hazard status or unplanned activities are to be submitted on “Amendment
to the Site Specific Health and Safety Plan” which is included bellow.
c. Amendment must be approved by the Project Manager prior to implementation of the
amendment.
AMENDMENT TO THE SITE SPECIFIC HEALTH AND SAFETY PLAN
A. Changes in field activities or hazards:
B. Proposed amendment:
C. Approval:
Proposed by: ___________________________________date ______________________
Approved by: ___________________________________date _____________________
Amendment number: ____________________________
Amendment effective date: _______________________
Appendix C
Well Photos
Former Rushco Food Store #4
GRI Project No. 5721
MW-1
MW-2
Former Rushco Food Store #4
GRI Project No. 5721
MW-3
MW-4
Former Rushco Food Store #4
GRI Project No. 5721
MW-5
MW-6
Former Rushco Food Store #4
GRI Project No. 5721
MW-7
TW-1
Appendix D
Well Construction Records and Subsurface Logs
Geological Resources, Inc.Phone:(704) 845-4010
3502 Hayes Road Fax:(704) 845-4012
Monroe, NC 28110
SUBSURFACE LOG
Project Rushco #4
Address 1901 West Innes St. Salisbury, NC
Boring Number MW-5 Date Drilled
Sample Method N/A Drilling Method 6" SSA
Completion Details Well set @ 30.0' w/ 10' of screen
Driller Matt Steele; 4548A Log By Eric Eubanks, P.G.
Lab Sample PID
Depth Sample Interval(ft)ppm LITHOLOGY
0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
32
34
36
3.0' - 5.0' brownish-gray CLAY; moist; petroleum odor
08/11/23
0.0' - 0.5' asphalt
0.5' - 1.5' greenish-gray silty CLAY; moist; petroleum odor
1.5' - 3.0' dark gray sandy SILT; moist; petroleum odor
5.0' - 11.0' light tan clayey SILT
11.0' - 30.0' light gray CLAY
boring terminated; well set @ 30.0'
WELL CONSTRUCTION RECORD
This form can be used for single or multiple wells
Form GW-1 North Carolina Department of Environment and Natural Resources – Division of Water 5HVRXUFHV Revised AXJXVW 2013
1. Well Contractor Information:
Well Contractor Name
NC Well Contractor Certification Number
Company Name 2. Well Construction Permit #: List all applicable well permits (i.e. County, State, Variance, ,QMHFWLRQetc.) 3. Well Use (check well use): Water Supply Well: □Agricultural □Municipal/Public □Geothermal (Heating/Cooling Supply) □Residential Water Supply (single)
□Industrial/Commercial □Residential Water Supply (shared) □Irrigation
Non-Water Supply Well: □Monitoring □Recovery
Injection Well: □Aquifer Recharge □Groundwater Remediation
□Aquifer Storage and Recovery □Salinity Barrier □Aquifer Test □Stormwater Drainage
□Experimental Technology □Subsidence Control
□Geothermal (Closed Loop) □Tracer □Geothermal (Heating/Cooling Return) □Other (explain under #21 Remarks)
4. Date Well(s) Completed: ____________ Well ID#______________________ 5a. Well Location:
Facility/Owner Name Facility ID# (if applicable)
Physical Address, City, and Zip
County Parcel Identification No. (PIN) 5b. Latitude and Longitude in degrees/minutes/seconds or decimal degrees: (if well field, one lat/long is sufficient) N W
6. Is (are) the well(s): □Permanent or □Temporary
7. Is this a repair to an existing well: □Yes or □No If this is a repair, fill out known well construction information and explain the nature of the repair under #21 remarks section or on the back of this form.
8. Number of wells constructed: For multiple injection or non-water supply wells ONLY with the same construction, you can submit one form. 9. Total well depth below land surface: (ft.) For multiple wells list all depths if different (example- 3@200’ and 2@100′) 10. Static water level below top of casing: (ft.) If water level is above casing, use “+” 11. Borehole diameter: (in.) 12. Well construction method: (i.e. auger, rotary, cable, direct push, etc.) FOR WATER SUPPLY WELLS ONLY: 13a. Yield (gpm) Method of test: 13b. Disinfection type: Amount:
14. WATER ZONES
FROM TO DESCRIPTION
ft. ft.
ft. ft.
15. OUTER CASING (for multi-cased wells) OR LINER (if applicable) FROM TO DIAMETER THICKNESS MATERIAL
ft. ft. in.
16. INNER CASING OR TUBING (geothermal closed-loop)
FROM TO DIAMETER THICKNESS MATERIAL
ft. ft. in.
ft. ft. in.
17. SCREEN FROM TO DIAMETER SLOT SIZE THICKNESS MATERIAL
ft. ft. in.
ft. ft. in.
18. GROUT
FROM TO MATERIAL EMPLACEMENT METHOD & AMOUNT
ft. ft.
ft. ft.
ft. ft.
19. SAND/GRAVEL PACK (if applicable)
FROM TO MATERIAL EMPLACEMENT METHOD
ft. ft.
ft. ft.
20. DRILLING LOG (attach additional sheets if necessary) FROM TO DESCRIPTION (color, hardness, soil/rock type, grain size, etc.)
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
21. REMARKS
22. Certification:
Signature of Certified Well Contractor Date By signing this form, I hereby certify that the well(s) was (were) constructed in accordance with 15A NCAC 02C .0100 or 15A NCAC 02C .0200 Well Construction Standards and that a copy of this record has been provided to the well owner.
23. Site diagram or additional well details: You may use the back of this page to provide additional well site details or well construction details. You may also attach additional pages if necessary. SUBMITTAL INSTUCTIONS 24a. For All Wells: Submit this form within 30 days of completion of well construction to the following: Division of Water Resources, Information Processing Unit, 1617 Mail Service Center, Raleigh, NC 27699-1617
24b. For Injection Wells ONLY: In addition to sending the form to the address in
24a above, also submit a copy of this form within 30 days of completion of well construction to the following: Division of Water Resources, Underground Injection Control Program, 1636 Mail Service Center, Raleigh, NC 27699-1636
24c. For Water Supply & Injection Wells:
Also submit one copy of this form within 30 days of completion ofwell construction to the county health department of the county whereconstructed.
For Internal Use ONLY:
Matt Steele
4548-A
Geological Resources, Inc.
WM0301300
4
08/11/2023 MW-5
Rushco Food Store #4 00-0-0000030414
1901 W. Innes St. Salisbury, NC
Rowan 5750-08-98-4156
35.686822 80.483554
1
30
6
Augers
Sch 40 PVC
0 20 2 Sch 40 PVC
20 30 2 0.010 Sch 40 PVC
0 16 cement pour
16 18 bentonite pour
18 30 #2 sand pour
0.0 0.5 asphalt
0.5 1.5 greenish-gray silty CLAY
1.5 3.0 dark gray sandy SILT
3.0 5.0 brownish-gray CLAY
5.0 11.0 light tan clayey SILT
11.0 30.0 light gray CLAY
08/11/2023
_______________
Geological Resources, Inc.Phone:(704) 845-4010
3502 Hayes Road Fax:(704) 845-4012
Monroe, NC 28110
SUBSURFACE LOG
Project Rushco #4
Address 1901 West Innes St. Salisbury, NC
Boring Number MW-6 Date Drilled
Sample Method N/A Drilling Method 6" SSA
Completion Details Well set @ 30.0' w/ 10' of screen
Driller Matt Steele; 4548A Log By Eric Eubanks, P.G.
Lab Sample PID
Depth Sample Interval(ft)ppm LITHOLOGY
0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
32
34
36
08/11/23
0.0' - 0.5' asphalt
0.5' - 8.0' brownish-red CLAY; moist
8.0' - 10.0' brown CLAY; petroleum odor
10.0' - 17.0' greenish-gray CLAY; petroleum odor
27.0' - 30.0' green/gray CLAY; moist; petroleum odor
17.0' - 18.0' greenish-gray CLAY w/ weathered quartz; petroleum odor
18.0' - 27.0' brown CLAY w/ weathered quartz; moist
boring terminated; well set @ 30.0'
WELL CONSTRUCTION RECORD
This form can be used for single or multiple wells
Form GW-1 North Carolina Department of Environment and Natural Resources – Division of Water 5HVRXUFHV Revised AXJXVW 2013
1. Well Contractor Information:
Well Contractor Name
NC Well Contractor Certification Number
Company Name 2. Well Construction Permit #: List all applicable well permits (i.e. County, State, Variance, ,QMHFWLRQetc.) 3. Well Use (check well use): Water Supply Well: □Agricultural □Municipal/Public □Geothermal (Heating/Cooling Supply) □Residential Water Supply (single)
□Industrial/Commercial □Residential Water Supply (shared) □Irrigation
Non-Water Supply Well: □Monitoring □Recovery
Injection Well: □Aquifer Recharge □Groundwater Remediation
□Aquifer Storage and Recovery □Salinity Barrier □Aquifer Test □Stormwater Drainage
□Experimental Technology □Subsidence Control
□Geothermal (Closed Loop) □Tracer □Geothermal (Heating/Cooling Return) □Other (explain under #21 Remarks)
4. Date Well(s) Completed: ____________ Well ID#______________________ 5a. Well Location:
Facility/Owner Name Facility ID# (if applicable)
Physical Address, City, and Zip
County Parcel Identification No. (PIN) 5b. Latitude and Longitude in degrees/minutes/seconds or decimal degrees: (if well field, one lat/long is sufficient) N W
6. Is (are) the well(s): □Permanent or □Temporary
7. Is this a repair to an existing well: □Yes or □No If this is a repair, fill out known well construction information and explain the nature of the repair under #21 remarks section or on the back of this form.
8. Number of wells constructed: For multiple injection or non-water supply wells ONLY with the same construction, you can submit one form. 9. Total well depth below land surface: (ft.) For multiple wells list all depths if different (example- 3@200’ and 2@100′) 10. Static water level below top of casing: (ft.) If water level is above casing, use “+” 11. Borehole diameter: (in.) 12. Well construction method: (i.e. auger, rotary, cable, direct push, etc.) FOR WATER SUPPLY WELLS ONLY: 13a. Yield (gpm) Method of test: 13b. Disinfection type: Amount:
14. WATER ZONES
FROM TO DESCRIPTION
ft. ft.
ft. ft.
15. OUTER CASING (for multi-cased wells) OR LINER (if applicable) FROM TO DIAMETER THICKNESS MATERIAL
ft. ft. in.
16. INNER CASING OR TUBING (geothermal closed-loop)
FROM TO DIAMETER THICKNESS MATERIAL
ft. ft. in.
ft. ft. in.
17. SCREEN FROM TO DIAMETER SLOT SIZE THICKNESS MATERIAL
ft. ft. in.
ft. ft. in.
18. GROUT
FROM TO MATERIAL EMPLACEMENT METHOD & AMOUNT
ft. ft.
ft. ft.
ft. ft.
19. SAND/GRAVEL PACK (if applicable)
FROM TO MATERIAL EMPLACEMENT METHOD
ft. ft.
ft. ft.
20. DRILLING LOG (attach additional sheets if necessary) FROM TO DESCRIPTION (color, hardness, soil/rock type, grain size, etc.)
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
21. REMARKS
22. Certification:
Signature of Certified Well Contractor Date By signing this form, I hereby certify that the well(s) was (were) constructed in accordance with 15A NCAC 02C .0100 or 15A NCAC 02C .0200 Well Construction Standards and that a copy of this record has been provided to the well owner.
23. Site diagram or additional well details: You may use the back of this page to provide additional well site details or well construction details. You may also attach additional pages if necessary. SUBMITTAL INSTUCTIONS 24a. For All Wells: Submit this form within 30 days of completion of well construction to the following: Division of Water Resources, Information Processing Unit, 1617 Mail Service Center, Raleigh, NC 27699-1617
24b. For Injection Wells ONLY: In addition to sending the form to the address in
24a above, also submit a copy of this form within 30 days of completion of well construction to the following: Division of Water Resources, Underground Injection Control Program, 1636 Mail Service Center, Raleigh, NC 27699-1636
24c. For Water Supply & Injection Wells:
Also submit one copy of this form within 30 days of completion ofwell construction to the county health department of the county whereconstructed.
For Internal Use ONLY:
Matt Steele
4548-A
Geological Resources, Inc.
WM0301300
4
08/11/2023 MW-6
Rushco Food Store #4 00-0-0000030414
1901 W. Innes St. Salisbury, NC
Rowan 5750-08-98-4156
35.686822 80.483554
1
30
6
Augers
Sch 40 PVC
0 20 2 Sch 40 PVC
20 30 2 0.010 Sch 40 PVC
0 16 cement pour
16 18 bentonite pour
18 30 #2 sand pour
0.0 0.5 asphalt
0.5 8.0 brownish-red CLAY
8.0 10.0 brown CLAY
10.0 17.0 greenish-gray CLAY
17.0 18.0 greenish-gray CLAY w/ weathered quartz
18.0 27.0 brown CLAY w/ weathered quartz
27.0 30.0 green/gray CLAY
08/11/2023
_______________
Geological Resources, Inc.Phone:(704) 845-4010
3502 Hayes Road Fax:(704) 845-4012
Monroe, NC 28110
SUBSURFACE LOG
Project Rushco #4
Address 1901 West Innes St. Salisbury, NC
Boring Number MW-7 Date Drilled
Sample Method N/A Drilling Method 6" SSA
Completion Det.Well set @ 30.0' w/ 10' of screen
Driller Matt Steele; 4548A Log By Eric Eubanks, P.G.
Lab Sample PID
Depth Sample Interval(ft)ppm LITHOLOGY
0
2
4
6
8
10
12
14
16
18
20
22
24
26
28
30
32
34
36
08/11/23
0.0' - 0.5' asphalt
0.5' - 1.5' concrete
1.5' - 22.0' light brown/gray CLAY; moist
22.0' - 26.0' light brown/gray CLAY; saturated
26.0' - 30.0' dark gray/brown CLAY; saturated
boring terminated; well set @ 30.0'
WELL CONSTRUCTION RECORD
This form can be used for single or multiple wells
Form GW-1 North Carolina Department of Environment and Natural Resources – Division of Water 5HVRXUFHV Revised AXJXVW 2013
1. Well Contractor Information:
Well Contractor Name
NC Well Contractor Certification Number
Company Name 2. Well Construction Permit #: List all applicable well permits (i.e. County, State, Variance, ,QMHFWLRQetc.) 3. Well Use (check well use): Water Supply Well: □Agricultural □Municipal/Public □Geothermal (Heating/Cooling Supply) □Residential Water Supply (single)
□Industrial/Commercial □Residential Water Supply (shared) □Irrigation
Non-Water Supply Well: □Monitoring □Recovery
Injection Well: □Aquifer Recharge □Groundwater Remediation
□Aquifer Storage and Recovery □Salinity Barrier □Aquifer Test □Stormwater Drainage
□Experimental Technology □Subsidence Control
□Geothermal (Closed Loop) □Tracer □Geothermal (Heating/Cooling Return) □Other (explain under #21 Remarks)
4. Date Well(s) Completed: ____________ Well ID#______________________ 5a. Well Location:
Facility/Owner Name Facility ID# (if applicable)
Physical Address, City, and Zip
County Parcel Identification No. (PIN) 5b. Latitude and Longitude in degrees/minutes/seconds or decimal degrees: (if well field, one lat/long is sufficient) N W
6. Is (are) the well(s): □Permanent or □Temporary
7. Is this a repair to an existing well: □Yes or □No If this is a repair, fill out known well construction information and explain the nature of the repair under #21 remarks section or on the back of this form.
8. Number of wells constructed: For multiple injection or non-water supply wells ONLY with the same construction, you can submit one form. 9. Total well depth below land surface: (ft.) For multiple wells list all depths if different (example- 3@200’ and 2@100′) 10. Static water level below top of casing: (ft.) If water level is above casing, use “+” 11. Borehole diameter: (in.) 12. Well construction method: (i.e. auger, rotary, cable, direct push, etc.) FOR WATER SUPPLY WELLS ONLY: 13a. Yield (gpm) Method of test: 13b. Disinfection type: Amount:
14. WATER ZONES
FROM TO DESCRIPTION
ft. ft.
ft. ft.
15. OUTER CASING (for multi-cased wells) OR LINER (if applicable) FROM TO DIAMETER THICKNESS MATERIAL
ft. ft. in.
16. INNER CASING OR TUBING (geothermal closed-loop)
FROM TO DIAMETER THICKNESS MATERIAL
ft. ft. in.
ft. ft. in.
17. SCREEN FROM TO DIAMETER SLOT SIZE THICKNESS MATERIAL
ft. ft. in.
ft. ft. in.
18. GROUT
FROM TO MATERIAL EMPLACEMENT METHOD & AMOUNT
ft. ft.
ft. ft.
ft. ft.
19. SAND/GRAVEL PACK (if applicable)
FROM TO MATERIAL EMPLACEMENT METHOD
ft. ft.
ft. ft.
20. DRILLING LOG (attach additional sheets if necessary) FROM TO DESCRIPTION (color, hardness, soil/rock type, grain size, etc.)
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
ft. ft.
21. REMARKS
22. Certification:
Signature of Certified Well Contractor Date By signing this form, I hereby certify that the well(s) was (were) constructed in accordance with 15A NCAC 02C .0100 or 15A NCAC 02C .0200 Well Construction Standards and that a copy of this record has been provided to the well owner.
23. Site diagram or additional well details: You may use the back of this page to provide additional well site details or well construction details. You may also attach additional pages if necessary. SUBMITTAL INSTUCTIONS 24a. For All Wells: Submit this form within 30 days of completion of well construction to the following: Division of Water Resources, Information Processing Unit, 1617 Mail Service Center, Raleigh, NC 27699-1617
24b. For Injection Wells ONLY: In addition to sending the form to the address in
24a above, also submit a copy of this form within 30 days of completion of well construction to the following: Division of Water Resources, Underground Injection Control Program, 1636 Mail Service Center, Raleigh, NC 27699-1636
24c. For Water Supply & Injection Wells:
Also submit one copy of this form within 30 days of completion ofwell construction to the county health department of the county whereconstructed.
For Internal Use ONLY:
Matt Steele
4548-A
Geological Resources, Inc.
WM0301300
4
08/11/2023 MW-7
Rushco Food Store #4 00-0-0000030414
1901 W. Innes St. Salisbury, NC
Rowan 5750-08-98-4156
35.686822 80.483554
1
30
6
Augers
Sch 40 PVC
0 20 2 Sch 40 PVC
20 30 2 0.010 Sch 40 PVC
0 16 cement pour
16 18 bentonite pour
18 30 #2 sand pour
0.0 1.5 asphalt/concrete
1.5 26.0 light brown/gray CLAY
26.0 30.0 dark gray/brown CLAY
08/11/2023
_______________
Appendix E
Laboratory Analytical Report
Laboratory's liability in any claim relating to analyses performed shall be limited to, at laboratory's option, repeating the
analysis in question at laboratory's expense, or the refund of the charges paid for performance of said analysis.
9/8/2023
Geological Resources, Inc. Sam McKay
3502 Hayes Road Monroe, NC, 28110
Ref: Analytical Testing
Lab Report Number: 23-240-0002 Client Project Description: Rushco 4 (Former)
GRI #5721
Dear Sam McKay:
Waypoint Analytical, LLC (Charlotte) received sample(s) on 8/25/2023 for the analyses presented in the following report.
The above referenced project has been analyzed per your instructions. The analyses were performed in
accordance with the applicable analytical method.
The analytical data has been validated using standard quality control measures performed as required by the analytical method. Quality Assurance, method validations, instrumentation maintenance and calibration for all
parameters were performed in accordance with guidelines established by the USEPA (including 40 CFR 136 Method Update Rule May 2021) unless otherwise indicated. Certain parameters (chlorine, pH, dissolved oxygen, sulfite...) are required to be analyzed within 15 minutes of
sampling. Usually, but not always, any field parameter analyzed at the laboratory is outside of this holding time. Refer to sample analysis time for confirmation of holding time compliance.
The results are shown on the attached Report of Analysis(s). Results for solid matrices are reported on an as-
received basis unless otherwise indicated. This report shall not be reproduced except in full and relates only to the samples included in this report. Please do not hesitate to contact me or client services if you have any questions or need additional information.
Sincerely,
Danyale Love Project Manager
Page 1 of 74
Certification Summary
Laboratory ID: WP CNC: Waypoint Analytical Carolina, Inc. (C), Charlotte, NC
State Program Lab ID Expiration Date
07/31/202437735State ProgramNorth Carolina
12/31/2023402State ProgramNorth Carolina
07/31/202399012State ProgramSouth Carolina
12/31/202299012State ProgramSouth Carolina
Page 1 of 1 00016/23-240-0002
Page 2 of 74
Report Number:
Sample Summary Table
Client Project Description:
23-240-0002
Rushco 4 (Former)
GRI #5721
Lab No Client Sample ID Matrix Date Collected Date Received
08/24/2023 08:23Aqueous 93503 MW-1 08/25/2023 15:17
08/24/2023 08:30Aqueous 93504 MW-2 08/25/2023 15:17
08/24/2023 08:39Aqueous 93505 MW-3 08/25/2023 15:17
08/24/2023 08:47Aqueous 93506 MW-4 08/25/2023 15:17
08/24/2023 09:18Aqueous 93507 MW-5 08/25/2023 15:17
08/24/2023 09:09Aqueous 93508 MW-6 08/25/2023 15:17
08/24/2023 08:58Aqueous 93509 MW-7 08/25/2023 15:17
08/24/2023 08:15Aqueous 93510 TW-1 08/25/2023 15:17
08/24/2023 07:30Aqueous 93511 TB 08/25/2023 15:17
Page 3 of 74
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
23-240-0002
Report Limit
Project:Rushco 4 (Former)
V 93503MW-1
3020 09/01/2023 10:566200BAcetoneµg/L 180
13000 09/02/2023 00:066200BBenzeneµg/L 180
J33.7 09/01/2023 10:566200Bn-Butylbenzene µg/L 18.0
J22.0 09/01/2023 10:566200BChloroformµg/L 22.0
602 09/01/2023 10:566200BDi-Isopropyl Ether (DIPE)µg/L 50.0
3220 09/01/2023 10:566200BEthylbenzeneµg/L 17.0
238 09/01/2023 10:566200B2-Hexanone µg/L 38.0
107 09/01/2023 10:566200BIsopropylbenzeneµg/L 18.0
1440 09/01/2023 10:566200BMethyl Ethyl Ketone (MEK)µg/L 71.0
11300 09/02/2023 00:066200BMethyl tert-butyl ether (MTBE)µg/L 140
151 09/01/2023 10:566200B4-Methyl-2-Pentanone µg/L 7.80
1150 09/01/2023 10:566200BNaphthaleneµg/L 47.0
296 09/01/2023 10:566200Bn-Propylbenzene µg/L 19.0
71.8 09/01/2023 10:566200BStyreneµg/L 22.0
17600 09/01/2023 10:566200Btert-Butyl Alcohol (TBA)µg/L 160
41400 09/02/2023 00:066200Btert-Amyl Alcohol (TAA)µg/L 1900
J49.6 09/01/2023 10:566200Btert-Amyl Methyl Ether (TAME)µg/L 28.0
30800 09/02/2023 00:066200BTolueneµg/L 220
2170 09/01/2023 10:566200B1,2,4-Trimethylbenzene µg/L 19.0
546 09/01/2023 10:566200B1,3,5-Trimethylbenzene µg/L 18.0
5170 09/01/2023 10:566200Bo-Xylene µg/L 21.0
11300 09/01/2023 10:566200Bm,p-Xylene µg/L 42.0
16500 09/01/2023 10:566200BXylene (Total)µg/L 21.0
V 93504MW-2
161 09/01/2023 11:226200BBenzeneµg/L 18.0
51.3 09/01/2023 11:226200BDi-Isopropyl Ether (DIPE)µg/L 50.0
33600 09/01/2023 11:226200BEthanolµg/L 4200
J43.9 09/01/2023 11:226200BEthylbenzeneµg/L 17.0
713 09/01/2023 11:226200BMethyl tert-butyl ether (MTBE)µg/L 14.0
J30.2 09/01/2023 11:226200Bn-Propylbenzene µg/L 19.0
1060 09/01/2023 11:226200Btert-Butyl Alcohol (TBA)µg/L 160
1000 09/01/2023 11:226200Btert-Amyl Alcohol (TAA)µg/L 190
66.0 09/01/2023 11:226200BTolueneµg/L 22.0
J45.4 09/01/2023 11:226200B1,2,4-Trimethylbenzene µg/L 19.0
J44.2 09/01/2023 11:226200Bm,p-Xylene µg/L 42.0
J44.2 09/01/2023 11:226200BXylene (Total)µg/L 21.0
Page 4 of 74
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
23-240-0002
Report Limit
Project:Rushco 4 (Former)
V 93505MW-3
1340 09/01/2023 23:146200BBenzeneµg/L 18.0
24.6 09/01/2023 07:316200Bn-Butylbenzene µg/L 0.180
14.3 09/01/2023 07:316200Bsec-Butyl benzene µg/L 0.200
3.91 09/01/2023 07:316200BDi-Isopropyl Ether (DIPE)µg/L 0.500
4170 09/01/2023 23:146200BEthylbenzeneµg/L 17.0
117 09/01/2023 23:146200BIsopropylbenzeneµg/L 18.0
7.01 09/01/2023 07:316200B4-Isopropyl toluene µg/L 0.089
16.5 09/01/2023 07:316200BMethyl tert-butyl ether (MTBE)µg/L 0.140
1130 09/01/2023 23:146200BNaphthaleneµg/L 47.0
330 09/01/2023 23:146200Bn-Propylbenzene µg/L 19.0
163 09/01/2023 23:146200BStyreneµg/L 22.0
11.4 09/01/2023 07:316200Btert-Butyl Alcohol (TBA)µg/L 1.60
E440.50 09/01/2023 07:316200Btert-Amyl Alcohol (TAA)µg/L 1.90
0.623 09/01/2023 07:316200BTetrachloroetheneµg/L 0.220
13400 09/06/2023 22:556200BTolueneµg/L 220
9.57 09/01/2023 07:316200B1,1,2-Trichloroethane µg/L 0.096
0.745 09/01/2023 07:316200BTrichloroetheneµg/L 0.180
2860 09/01/2023 23:146200B1,2,4-Trimethylbenzene µg/L 19.0
701 09/01/2023 23:146200B1,3,5-Trimethylbenzene µg/L 18.0
5640 09/01/2023 23:146200Bo-Xylene µg/L 21.0
12200 09/01/2023 23:146200Bm,p-Xylene µg/L 42.0
17800 09/01/2023 23:146200BXylene (Total)µg/L 21.0
V 93506MW-4
1590 09/01/2023 11:486200BAcetoneµg/L 180
22100 09/02/2023 00:316200BBenzeneµg/L 180
686 09/01/2023 11:486200BDi-Isopropyl Ether (DIPE)µg/L 50.0
3180 09/01/2023 11:486200BEthylbenzeneµg/L 17.0
84.9 09/01/2023 11:486200BIsopropylbenzeneµg/L 18.0
768 09/01/2023 11:486200BMethyl Ethyl Ketone (MEK)µg/L 71.0
15400 09/02/2023 00:316200BMethyl tert-butyl ether (MTBE)µg/L 140
892 09/01/2023 11:486200BNaphthaleneµg/L 47.0
234 09/01/2023 11:486200Bn-Propylbenzene µg/L 19.0
135 09/01/2023 11:486200BStyreneµg/L 22.0
1420 09/01/2023 11:486200Btert-Butyl Alcohol (TBA)µg/L 160
5310 09/01/2023 11:486200Btert-Amyl Alcohol (TAA)µg/L 190
J91.0 09/01/2023 11:486200Btert-Amyl Methyl Ether (TAME)µg/L 28.0
Page 5 of 74
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
23-240-0002
Report Limit
Project:Rushco 4 (Former)
V 93506MW-4
46900 09/02/2023 00:316200BTolueneµg/L 220
2060 09/01/2023 11:486200B1,2,4-Trimethylbenzene µg/L 19.0
552 09/01/2023 11:486200B1,3,5-Trimethylbenzene µg/L 18.0
6050 09/01/2023 11:486200Bo-Xylene µg/L 21.0
12500 09/01/2023 11:486200Bm,p-Xylene µg/L 42.0
18600 09/01/2023 11:486200BXylene (Total)µg/L 21.0
V 93507MW-5
J0.002 08/29/2023 22:156010DLeadmg/L 0.002
J49509/01/2023 12:146200BAcetoneµg/L 180
760 09/01/2023 12:146200BBenzeneµg/L 18.0
J35.8 09/01/2023 12:146200Bn-Butylbenzene µg/L 18.0
232 09/01/2023 12:146200BDi-Isopropyl Ether (DIPE)µg/L 50.0
2560 09/01/2023 12:146200BEthylbenzeneµg/L 17.0
130 09/01/2023 12:146200BIsopropylbenzeneµg/L 18.0
7580 09/01/2023 12:146200BMethyl tert-butyl ether (MTBE)µg/L 14.0
1310 09/01/2023 12:146200BNaphthaleneµg/L 47.0
372 09/01/2023 12:146200Bn-Propylbenzene µg/L 19.0
102 09/01/2023 12:146200BStyreneµg/L 22.0
J87709/01/2023 12:146200Btert-Butyl Alcohol (TBA)µg/L 160
J85809/01/2023 12:146200Btert-Amyl Alcohol (TAA)µg/L 190
J24109/01/2023 12:146200Btert-Amyl Methyl Ether (TAME)µg/L 28.0
1150 09/01/2023 12:146200BTolueneµg/L 22.0
2740 09/01/2023 12:146200B1,2,4-Trimethylbenzene µg/L 19.0
668 09/01/2023 12:146200B1,3,5-Trimethylbenzene µg/L 18.0
2270 09/01/2023 12:146200Bo-Xylene µg/L 21.0
7980 09/01/2023 12:146200Bm,p-Xylene µg/L 42.0
10300 09/01/2023 12:146200BXylene (Total)µg/L 21.0
5650 08/28/2023 22:49CALCULATIONAliphatic C5-C8 (Adjusted)µg/L 500
5990 08/29/2023 07:22CALCULATIONAliphatics C9-C12 (Adjusted)µg/L 2500
10300 08/29/2023 07:22CALCULATIONAromatic C9-C10 (Adjusted)µg/L 2500
7560 08/28/2023 22:49MADEP-VPH Aliphatic C5-C8 µg/L 115
29100 08/29/2023 07:22MADEP-VPH Aliphatic C9-C12 µg/L 1290
10300 08/29/2023 07:22MADEP-VPH Aromatic C9-C10 µg/L 201
V 93508MW-6
0.006 08/29/2023 22:196010DLeadmg/L 0.002
J83109/01/2023 12:396200BAcetoneµg/L 180
Page 6 of 74
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
23-240-0002
Report Limit
Project:Rushco 4 (Former)
V 93508MW-6
4530 09/01/2023 12:396200BBenzeneµg/L 18.0
135 09/01/2023 12:396200BDi-Isopropyl Ether (DIPE)µg/L 50.0
3900 09/01/2023 12:396200BEthylbenzeneµg/L 17.0
101 09/01/2023 12:396200BIsopropylbenzeneµg/L 18.0
1080 09/01/2023 12:396200BNaphthaleneµg/L 47.0
308 09/01/2023 12:396200Bn-Propylbenzene µg/L 19.0
206 09/01/2023 12:396200BStyreneµg/L 22.0
2260 09/01/2023 12:396200Btert-Amyl Alcohol (TAA)µg/L 190
27400 09/02/2023 00:576200BTolueneµg/L 220
2260 09/01/2023 12:396200B1,2,4-Trimethylbenzene µg/L 19.0
551 09/01/2023 12:396200B1,3,5-Trimethylbenzene µg/L 18.0
5140 09/01/2023 12:396200Bo-Xylene µg/L 21.0
12100 09/01/2023 12:396200Bm,p-Xylene µg/L 42.0
17200 09/01/2023 12:396200BXylene (Total)µg/L 21.0
33100 08/29/2023 08:09CALCULATIONAliphatic C5-C8 (Adjusted)µg/L 5000
14900 08/29/2023 08:09CALCULATIONAliphatics C9-C12 (Adjusted)µg/L 5000
7430 08/29/2023 08:09CALCULATIONAromatic C9-C10 (Adjusted)µg/L 5000
65000 08/29/2023 08:09MADEP-VPH Aliphatic C5-C8 µg/L 1150
43500 08/29/2023 08:09MADEP-VPH Aliphatic C9-C12 µg/L 2580
7430 08/29/2023 08:09MADEP-VPH Aromatic C9-C10 µg/L 402
V 93509MW-7
0.008 08/29/2023 22:246010DLeadmg/L 0.002
18.2 09/01/2023 20:146200BAcetoneµg/L 1.80
1.36 09/01/2023 20:146200BBenzeneµg/L 0.180
0.928 09/01/2023 20:146200BChloroformµg/L 0.220
9.05 09/01/2023 20:146200BDi-Isopropyl Ether (DIPE)µg/L 0.500
0.668 09/01/2023 20:146200BEthylbenzeneµg/L 0.170
30.0 09/01/2023 20:146200BMethyl tert-butyl ether (MTBE)µg/L 0.140
J0.454 09/01/2023 20:146200BMethylene Chloride µg/L 0.330
14.4 09/01/2023 20:146200Btert-Butyl Alcohol (TBA)µg/L 1.60
24.8 09/01/2023 20:146200Btert-Amyl Alcohol (TAA)µg/L 1.90
J0.370 09/01/2023 20:146200BTetrachloroetheneµg/L 0.220
3.11 09/01/2023 20:146200BTolueneµg/L 0.220
0.769 09/01/2023 20:146200B1,2,4-Trimethylbenzene µg/L 0.190
J0.256 09/01/2023 20:146200B1,3,5-Trimethylbenzene µg/L 0.180
0.858 09/01/2023 20:146200Bo-Xylene µg/L 0.210
Page 7 of 74
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
23-240-0002
Report Limit
Project:Rushco 4 (Former)
V 93509MW-7
1.89 09/01/2023 20:146200Bm,p-Xylene µg/L 0.420
2.75 09/01/2023 20:146200BXylene (Total)µg/L 0.210
89.2 08/28/2023 19:41CALCULATIONAliphatic C5-C8 (Adjusted)µg/L 50.0
26.0 08/28/2023 19:41CALCULATIONAliphatics C9-C12 (Adjusted)µg/L 50.0
93.7 08/28/2023 19:41MADEP-VPH Aliphatic C5-C8 µg/L 11.5
J29.4 08/28/2023 19:41MADEP-VPH Aliphatic C9-C12 µg/L 25.8
V 93510TW-1
J5.58 09/01/2023 20:406200BAcetoneµg/L 1.80
1.94 09/01/2023 20:406200BChloroformµg/L 0.220
J0.222 09/01/2023 20:406200BIsopropylbenzeneµg/L 0.180
J0.211 09/01/2023 20:406200Bo-Xylene µg/L 0.210
J0.211 09/01/2023 20:406200BXylene (Total)µg/L 0.210
Page 8 of 74
Client: Geological Resources, Inc. CASE NARRATIVE
Project: Rushco 4 (Former) Lab Report Number: 23-240-0002
Date: 9/8/2023
Volatile Organic Compounds - GC/MS Method 6200B Analyte: 3,3-Dimethyl-1-butanol QC Batch No: V37379/V37378
Relative Percent Difference (RPD) for the duplicate analysis was outside of the allowable QC limits.
Analyte: tert-Amyl alcohol QC Batch No: V37379/V37436
Relative Percent Difference (RPD) for the duplicate analysis was outside of the allowable QC limits.
Analyte: tert-Amyl alcohol QC Batch No: V37437/V37436
Relative Percent Difference (RPD) for the duplicate analysis was outside of the allowable QC limits.
Page 9 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-1
93503 Matrix:
8/24/2023 8:23
Aqueous
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
<100 µg/L 100 10003,3-Dimethyl-1-butanol 100 09/01/23 10:56 6200BMSA
Surrogate: 4-Bromofluorobenzene 94.0 Limits: 70-130%09/01/23 10:56100 MSA V37379
Surrogate: Dibromofluoromethane 98.4 Limits: 70-130%09/01/23 10:56100 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 89.6 Limits: 70-130%09/01/23 10:56100 MSA V37379
Surrogate: Toluene-d8 99.8 Limits: 70-130%09/01/23 10:56100 MSA V37379
Surrogate: 4-Bromofluorobenzene 94.4 Limits: 70-130%09/02/23 00:061000 MSA V37437
Surrogate: Dibromofluoromethane 101 Limits: 70-130%09/02/23 00:061000 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 88.0 Limits: 70-130%09/02/23 00:061000 MSA V37437
Surrogate: Toluene-d8 99.2 Limits: 70-130%09/02/23 00:061000 MSA V37437
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 10 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-1
93503 Matrix:
8/24/2023 8:23
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
3020 µg/L 180 1000Acetone 100 09/01/23 10:56 V37379MSA
13000 µg/L 180 500Benzene 1000 09/02/23 00:06 V37437MSA
<21.0 µg/L 21.0 50.0Bromobenzene 100 09/01/23 10:56 V37379MSA
<42.0 µg/L 42.0 100Bromochloromethane 100 09/01/23 10:56 V37379MSA
<16.0 µg/L 16.0 50.0Bromodichloromethane 100 09/01/23 10:56 V37379MSA
<150 µg/L 150 500Bromoform 100 09/01/23 10:56 V37379MSA
<28.0 µg/L 28.0 100Bromomethane 100 09/01/23 10:56 V37379MSA
33.7 J µg/L 18.0 50.0n-Butylbenzene 100 09/01/23 10:56 V37379MSA
<20.0 µg/L 20.0 50.0sec-Butyl benzene 100 09/01/23 10:56 V37379MSA
<92.0 µg/L 92.0 200tert-Butyl benzene 100 09/01/23 10:56 V37379MSA
<18.0 µg/L 18.0 50.0Carbon Tetrachloride 100 09/01/23 10:56 V37379MSA
<19.0 µg/L 19.0 50.0Chlorobenzene 100 09/01/23 10:56 V37379MSA
<19.0 µg/L 19.0 50.0Chlorodibromomethane 100 09/01/23 10:56 V37379MSA
<43.0 µg/L 43.0 100Chloroethane 100 09/01/23 10:56 V37379MSA
22.0 J µg/L 22.0 50.0Chloroform 100 09/01/23 10:56 V37379MSA
<22.0 µg/L 22.0 50.0Chloromethane 100 09/01/23 10:56 V37379MSA
<20.0 µg/L 20.0 50.02-Chlorotoluene 100 09/01/23 10:56 V37379MSA
<20.0 µg/L 20.0 50.04-Chlorotoluene 100 09/01/23 10:56 V37379MSA
602 µg/L 50.0 50.0Di-Isopropyl Ether (DIPE)100 09/01/23 10:56 V37379MSA
<110 µg/L 110 2001,2-Dibromo-3-Chloropropane 100 09/01/23 10:56 V37379MSA
<23.0 µg/L 23.0 50.0Dibromomethane 100 09/01/23 10:56 V37379MSA
<22.0 µg/L 22.0 50.01,2-Dichlorobenzene 100 09/01/23 10:56 V37379MSA
<19.0 µg/L 19.0 50.01,3-Dichlorobenzene 100 09/01/23 10:56 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 11 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-1
93503 Matrix:
8/24/2023 8:23
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
<21.0 µg/L 21.0 50.01,4-Dichlorobenzene 100 09/01/23 10:56 V37379MSA
<120 µg/L 120 500Dichlorodifluoromethane 100 09/01/23 10:56 V37379MSA
<24.0 µg/L 24.0 50.01,1-Dichloroethane 100 09/01/23 10:56 V37379MSA
<15.0 µg/L 15.0 50.01,2-Dichloroethane 100 09/01/23 10:56 V37379MSA
<15.0 µg/L 15.0 50.01,1-Dichloroethene 100 09/01/23 10:56 V37379MSA
<20.0 µg/L 20.0 50.0cis-1,2-Dichloroethene 100 09/01/23 10:56 V37379MSA
<18.0 µg/L 18.0 50.0trans-1,2-Dichloroethene 100 09/01/23 10:56 V37379MSA
<19.0 µg/L 19.0 50.01,2-Dichloropropane 100 09/01/23 10:56 V37379MSA
<13.0 µg/L 13.0 50.01,3-Dichloropropane 100 09/01/23 10:56 V37379MSA
<21.0 µg/L 21.0 2002,2-Dichloropropane 100 09/01/23 10:56 V37379MSA
<20.0 µg/L 20.0 50.01,1-Dichloropropene 100 09/01/23 10:56 V37379MSA
<21.0 µg/L 21.0 50.0cis-1,3-Dichloropropene 100 09/01/23 10:56 V37379MSA
<15.0 µg/L 15.0 50.0trans-1,3-Dichloropropene 100 09/01/23 10:56 V37379MSA
<4200 µg/L 4200 20000Ethanol 100 09/01/23 10:56 V37379MSA
3220 µg/L 17.0 50.0Ethylbenzene 100 09/01/23 10:56 V37379MSA
<35.0 µg/L 35.0 300Hexachlorobutadiene 100 09/01/23 10:56 V37379MSA
238 µg/L 38.0 1002-Hexanone 100 09/01/23 10:56 V37379MSA
107 µg/L 18.0 50.0Isopropylbenzene 100 09/01/23 10:56 V37379MSA
<8.90 µg/L 8.90 50.04-Isopropyl toluene 100 09/01/23 10:56 V37379MSA
1440 µg/L 71.0 500Methyl Ethyl Ketone (MEK)100 09/01/23 10:56 V37379MSA
11300 µg/L 140 1000Methyl tert-butyl ether (MTBE)1000 09/02/23 00:06 V37437MSA
151 µg/L 7.80 1004-Methyl-2-Pentanone 100 09/01/23 10:56 V37379MSA
<33.0 µg/L 33.0 200Methylene Chloride 100 09/01/23 10:56 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 12 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-1
93503 Matrix:
8/24/2023 8:23
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
1150 µg/L 47.0 100Naphthalene 100 09/01/23 10:56 V37379MSA
296 µg/L 19.0 50.0n-Propylbenzene 100 09/01/23 10:56 V37379MSA
71.8 µg/L 22.0 50.0Styrene 100 09/01/23 10:56 V37379MSA
17600 µg/L 160 1000tert-Butyl Alcohol (TBA)100 09/01/23 10:56 V37379MSA
<35.0 µg/L 35.0 1000tert-Butyl formate (TBF)100 09/01/23 10:56 V37379MSA
41400 µg/L 1900 10000tert-Amyl Alcohol (TAA)1000 09/02/23 00:06 V37437MSA
49.6 J µg/L 28.0 1000tert-Amyl Methyl Ether (TAME)100 09/01/23 10:56 V37379MSA
<16.0 µg/L 16.0 50.01,1,1,2-Tetrachloroethane 100 09/01/23 10:56 V37379MSA
<16.0 µg/L 16.0 50.01,1,2,2-Tetrachloroethane 100 09/01/23 10:56 V37379MSA
<22.0 µg/L 22.0 50.0Tetrachloroethene 100 09/01/23 10:56 V37379MSA
30800 µg/L 220 500Toluene 1000 09/02/23 00:06 V37437MSA
<38.0 µg/L 38.0 50.01,2,3-Trichlorobenzene 100 09/01/23 10:56 V37379MSA
<31.0 µg/L 31.0 50.01,2,4-Trichlorobenzene 100 09/01/23 10:56 V37379MSA
<16.0 µg/L 16.0 50.01,1,1-Trichloroethane 100 09/01/23 10:56 V37379MSA
<9.60 µg/L 9.60 50.01,1,2-Trichloroethane 100 09/01/23 10:56 V37379MSA
<18.0 µg/L 18.0 50.0Trichloroethene 100 09/01/23 10:56 V37379MSA
<18.0 µg/L 18.0 50.0Trichlorofluoromethane 100 09/01/23 10:56 V37379MSA
<27.0 µg/L 27.0 50.01,2,3-Trichloropropane 100 09/01/23 10:56 V37379MSA
2170 µg/L 19.0 50.01,2,4-Trimethylbenzene 100 09/01/23 10:56 V37379MSA
546 µg/L 18.0 50.01,3,5-Trimethylbenzene 100 09/01/23 10:56 V37379MSA
<100 µg/L 100 500Vinyl Acetate 100 09/01/23 10:56 V37379MSA
<17.0 µg/L 17.0 50.0Vinyl Chloride 100 09/01/23 10:56 V37379MSA
5170 µg/L 21.0 50.0o-Xylene 100 09/01/23 10:56 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 13 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-1
93503 Matrix:
8/24/2023 8:23
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
11300 µg/L 42.0 100m,p-Xylene 100 09/01/23 10:56 V37379MSA
16500 µg/L 21.0 50.0Xylene (Total)100 09/01/23 10:56 V37379
Surrogate: 4-Bromofluorobenzene 94.0 Limits: 70-130%09/01/23 10:56100 MSA V37379
Surrogate: Dibromofluoromethane 98.4 Limits: 70-130%09/01/23 10:56100 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 89.6 Limits: 70-130%09/01/23 10:56100 MSA V37379
Surrogate: Toluene-d8 99.8 Limits: 70-130%09/01/23 10:56100 MSA V37379
Surrogate: 4-Bromofluorobenzene 94.4 Limits: 70-130%09/02/23 00:061000 MSA V37437
Surrogate: Dibromofluoromethane 101 Limits: 70-130%09/02/23 00:061000 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 88.0 Limits: 70-130%09/02/23 00:061000 MSA V37437
Surrogate: Toluene-d8 99.2 Limits: 70-130%09/02/23 00:061000 MSA V37437
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 14 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-2
93504 Matrix:
8/24/2023 8:30
Aqueous
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
<100 µg/L 100 10003,3-Dimethyl-1-butanol 100 09/01/23 11:22 6200BMSA
Surrogate: 4-Bromofluorobenzene 93.6 Limits: 70-130%09/01/23 11:22100 MSA V37379
Surrogate: Dibromofluoromethane 100 Limits: 70-130%09/01/23 11:22100 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 89.0 Limits: 70-130%09/01/23 11:22100 MSA V37379
Surrogate: Toluene-d8 99.2 Limits: 70-130%09/01/23 11:22100 MSA V37379
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 15 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-2
93504 Matrix:
8/24/2023 8:30
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
<180 µg/L 180 1000Acetone 100 09/01/23 11:22 V37379MSA
161 µg/L 18.0 50.0Benzene 100 09/01/23 11:22 V37379MSA
<21.0 µg/L 21.0 50.0Bromobenzene 100 09/01/23 11:22 V37379MSA
<42.0 µg/L 42.0 100Bromochloromethane 100 09/01/23 11:22 V37379MSA
<16.0 µg/L 16.0 50.0Bromodichloromethane 100 09/01/23 11:22 V37379MSA
<150 µg/L 150 500Bromoform 100 09/01/23 11:22 V37379MSA
<28.0 µg/L 28.0 100Bromomethane 100 09/01/23 11:22 V37379MSA
<18.0 µg/L 18.0 50.0n-Butylbenzene 100 09/01/23 11:22 V37379MSA
<20.0 µg/L 20.0 50.0sec-Butyl benzene 100 09/01/23 11:22 V37379MSA
<92.0 µg/L 92.0 200tert-Butyl benzene 100 09/01/23 11:22 V37379MSA
<18.0 µg/L 18.0 50.0Carbon Tetrachloride 100 09/01/23 11:22 V37379MSA
<19.0 µg/L 19.0 50.0Chlorobenzene 100 09/01/23 11:22 V37379MSA
<19.0 µg/L 19.0 50.0Chlorodibromomethane 100 09/01/23 11:22 V37379MSA
<43.0 µg/L 43.0 100Chloroethane 100 09/01/23 11:22 V37379MSA
<22.0 µg/L 22.0 50.0Chloroform 100 09/01/23 11:22 V37379MSA
<22.0 µg/L 22.0 50.0Chloromethane 100 09/01/23 11:22 V37379MSA
<20.0 µg/L 20.0 50.02-Chlorotoluene 100 09/01/23 11:22 V37379MSA
<20.0 µg/L 20.0 50.04-Chlorotoluene 100 09/01/23 11:22 V37379MSA
51.3 µg/L 50.0 50.0Di-Isopropyl Ether (DIPE)100 09/01/23 11:22 V37379MSA
<110 µg/L 110 2001,2-Dibromo-3-Chloropropane 100 09/01/23 11:22 V37379MSA
<23.0 µg/L 23.0 50.0Dibromomethane 100 09/01/23 11:22 V37379MSA
<22.0 µg/L 22.0 50.01,2-Dichlorobenzene 100 09/01/23 11:22 V37379MSA
<19.0 µg/L 19.0 50.01,3-Dichlorobenzene 100 09/01/23 11:22 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 16 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-2
93504 Matrix:
8/24/2023 8:30
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
<21.0 µg/L 21.0 50.01,4-Dichlorobenzene 100 09/01/23 11:22 V37379MSA
<120 µg/L 120 500Dichlorodifluoromethane 100 09/01/23 11:22 V37379MSA
<24.0 µg/L 24.0 50.01,1-Dichloroethane 100 09/01/23 11:22 V37379MSA
<15.0 µg/L 15.0 50.01,2-Dichloroethane 100 09/01/23 11:22 V37379MSA
<15.0 µg/L 15.0 50.01,1-Dichloroethene 100 09/01/23 11:22 V37379MSA
<20.0 µg/L 20.0 50.0cis-1,2-Dichloroethene 100 09/01/23 11:22 V37379MSA
<18.0 µg/L 18.0 50.0trans-1,2-Dichloroethene 100 09/01/23 11:22 V37379MSA
<19.0 µg/L 19.0 50.01,2-Dichloropropane 100 09/01/23 11:22 V37379MSA
<13.0 µg/L 13.0 50.01,3-Dichloropropane 100 09/01/23 11:22 V37379MSA
<21.0 µg/L 21.0 2002,2-Dichloropropane 100 09/01/23 11:22 V37379MSA
<20.0 µg/L 20.0 50.01,1-Dichloropropene 100 09/01/23 11:22 V37379MSA
<21.0 µg/L 21.0 50.0cis-1,3-Dichloropropene 100 09/01/23 11:22 V37379MSA
<15.0 µg/L 15.0 50.0trans-1,3-Dichloropropene 100 09/01/23 11:22 V37379MSA
33600 µg/L 4200 20000Ethanol 100 09/01/23 11:22 V37379MSA
43.9 J µg/L 17.0 50.0Ethylbenzene 100 09/01/23 11:22 V37379MSA
<35.0 µg/L 35.0 300Hexachlorobutadiene 100 09/01/23 11:22 V37379MSA
<38.0 µg/L 38.0 1002-Hexanone 100 09/01/23 11:22 V37379MSA
<18.0 µg/L 18.0 50.0Isopropylbenzene 100 09/01/23 11:22 V37379MSA
<8.90 µg/L 8.90 50.04-Isopropyl toluene 100 09/01/23 11:22 V37379MSA
<71.0 µg/L 71.0 500Methyl Ethyl Ketone (MEK)100 09/01/23 11:22 V37379MSA
713 µg/L 14.0 100Methyl tert-butyl ether (MTBE)100 09/01/23 11:22 V37379MSA
<7.80 µg/L 7.80 1004-Methyl-2-Pentanone 100 09/01/23 11:22 V37379MSA
<33.0 µg/L 33.0 200Methylene Chloride 100 09/01/23 11:22 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 17 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-2
93504 Matrix:
8/24/2023 8:30
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
<47.0 µg/L 47.0 100Naphthalene 100 09/01/23 11:22 V37379MSA
30.2 J µg/L 19.0 50.0n-Propylbenzene 100 09/01/23 11:22 V37379MSA
<22.0 µg/L 22.0 50.0Styrene 100 09/01/23 11:22 V37379MSA
1060 µg/L 160 1000tert-Butyl Alcohol (TBA)100 09/01/23 11:22 V37379MSA
<35.0 µg/L 35.0 1000tert-Butyl formate (TBF)100 09/01/23 11:22 V37379MSA
1000 µg/L 190 1000tert-Amyl Alcohol (TAA)100 09/01/23 11:22 V37379MSA
<28.0 µg/L 28.0 1000tert-Amyl Methyl Ether (TAME)100 09/01/23 11:22 V37379MSA
<16.0 µg/L 16.0 50.01,1,1,2-Tetrachloroethane 100 09/01/23 11:22 V37379MSA
<16.0 µg/L 16.0 50.01,1,2,2-Tetrachloroethane 100 09/01/23 11:22 V37379MSA
<22.0 µg/L 22.0 50.0Tetrachloroethene 100 09/01/23 11:22 V37379MSA
66.0 µg/L 22.0 50.0Toluene 100 09/01/23 11:22 V37379MSA
<38.0 µg/L 38.0 50.01,2,3-Trichlorobenzene 100 09/01/23 11:22 V37379MSA
<31.0 µg/L 31.0 50.01,2,4-Trichlorobenzene 100 09/01/23 11:22 V37379MSA
<16.0 µg/L 16.0 50.01,1,1-Trichloroethane 100 09/01/23 11:22 V37379MSA
<9.60 µg/L 9.60 50.01,1,2-Trichloroethane 100 09/01/23 11:22 V37379MSA
<18.0 µg/L 18.0 50.0Trichloroethene 100 09/01/23 11:22 V37379MSA
<18.0 µg/L 18.0 50.0Trichlorofluoromethane 100 09/01/23 11:22 V37379MSA
<27.0 µg/L 27.0 50.01,2,3-Trichloropropane 100 09/01/23 11:22 V37379MSA
45.4 J µg/L 19.0 50.01,2,4-Trimethylbenzene 100 09/01/23 11:22 V37379MSA
<18.0 µg/L 18.0 50.01,3,5-Trimethylbenzene 100 09/01/23 11:22 V37379MSA
<100 µg/L 100 500Vinyl Acetate 100 09/01/23 11:22 V37379MSA
<17.0 µg/L 17.0 50.0Vinyl Chloride 100 09/01/23 11:22 V37379MSA
<21.0 µg/L 21.0 50.0o-Xylene 100 09/01/23 11:22 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 18 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-2
93504 Matrix:
8/24/2023 8:30
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
44.2 J µg/L 42.0 100m,p-Xylene 100 09/01/23 11:22 V37379MSA
44.2 J µg/L 21.0 50.0Xylene (Total)100 09/01/23 11:22 V37379
Surrogate: 4-Bromofluorobenzene 93.6 Limits: 70-130%09/01/23 11:22100 MSA V37379
Surrogate: Dibromofluoromethane 100 Limits: 70-130%09/01/23 11:22100 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 89.0 Limits: 70-130%09/01/23 11:22100 MSA V37379
Surrogate: Toluene-d8 99.2 Limits: 70-130%09/01/23 11:22100 MSA V37379
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 19 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-3
93505 Matrix:
8/24/2023 8:39
Aqueous
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
<1.00 µg/L 1.00 10.03,3-Dimethyl-1-butanol 1 09/01/23 07:31 6200BMSA
Surrogate: 4-Bromofluorobenzene 94.6 Limits: 70-130%09/01/23 07:311 MSA V37379
Surrogate: Dibromofluoromethane 94.8 Limits: 70-130%09/01/23 07:311 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 97.2 Limits: 70-130%09/01/23 07:311 MSA V37379
Surrogate: Toluene-d8 98.6 Limits: 70-130%09/01/23 07:311 MSA V37379
Surrogate: 4-Bromofluorobenzene 93.8 Limits: 70-130%09/01/23 23:14100 MSA V37437
Surrogate: Dibromofluoromethane 101 Limits: 70-130%09/01/23 23:14100 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 88.2 Limits: 70-130%09/01/23 23:14100 MSA V37437
Surrogate: Toluene-d8 100 Limits: 70-130%09/01/23 23:14100 MSA V37437
Surrogate: 4-Bromofluorobenzene 99.0 Limits: 70-130%09/06/23 22:551000 MSA V37553
Surrogate: Dibromofluoromethane 102 Limits: 70-130%09/06/23 22:551000 MSA V37553
Surrogate: 1,2-Dichloroethane - d4 89.6 Limits: 70-130%09/06/23 22:551000 MSA V37553
Surrogate: Toluene-d8 99.0 Limits: 70-130%09/06/23 22:551000 MSA V37553
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 20 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-3
93505 Matrix:
8/24/2023 8:39
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
V37551 09/06/23 09:00
<1.80 µg/L 1.80 10.0Acetone 1 09/01/23 07:31 V37379MSA
1340 µg/L 18.0 50.0Benzene 100 09/01/23 23:14 V37437MSA
<0.210 µg/L 0.210 0.500Bromobenzene 1 09/01/23 07:31 V37379MSA
<0.420 µg/L 0.420 1.00Bromochloromethane 1 09/01/23 07:31 V37379MSA
<0.160 µg/L 0.160 0.500Bromodichloromethane 1 09/01/23 07:31 V37379MSA
<1.50 µg/L 1.50 5.00Bromoform 1 09/01/23 07:31 V37379MSA
<0.280 µg/L 0.280 1.00Bromomethane 1 09/01/23 07:31 V37379MSA
24.6 µg/L 0.180 0.500n-Butylbenzene 1 09/01/23 07:31 V37379MSA
14.3 µg/L 0.200 0.500sec-Butyl benzene 1 09/01/23 07:31 V37379MSA
<0.920 µg/L 0.920 2.00tert-Butyl benzene 1 09/01/23 07:31 V37379MSA
<0.180 µg/L 0.180 0.500Carbon Tetrachloride 1 09/01/23 07:31 V37379MSA
<0.190 µg/L 0.190 0.500Chlorobenzene 1 09/01/23 07:31 V37379MSA
<0.190 µg/L 0.190 0.500Chlorodibromomethane 1 09/01/23 07:31 V37379MSA
<0.430 µg/L 0.430 1.00Chloroethane 1 09/01/23 07:31 V37379MSA
<0.220 µg/L 0.220 0.500Chloroform 1 09/01/23 07:31 V37379MSA
<0.220 µg/L 0.220 0.500Chloromethane 1 09/01/23 07:31 V37379MSA
<0.200 µg/L 0.200 0.5002-Chlorotoluene 1 09/01/23 07:31 V37379MSA
<0.200 µg/L 0.200 0.5004-Chlorotoluene 1 09/01/23 07:31 V37379MSA
3.91 µg/L 0.500 0.500Di-Isopropyl Ether (DIPE)1 09/01/23 07:31 V37379MSA
<1.10 µg/L 1.10 2.001,2-Dibromo-3-Chloropropane 1 09/01/23 07:31 V37379MSA
<0.230 µg/L 0.230 0.500Dibromomethane 1 09/01/23 07:31 V37379MSA
<0.220 µg/L 0.220 0.5001,2-Dichlorobenzene 1 09/01/23 07:31 V37379MSA
<0.190 µg/L 0.190 0.5001,3-Dichlorobenzene 1 09/01/23 07:31 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 21 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-3
93505 Matrix:
8/24/2023 8:39
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
V37551 09/06/23 09:00
<0.210 µg/L 0.210 0.5001,4-Dichlorobenzene 1 09/01/23 07:31 V37379MSA
<1.20 µg/L 1.20 5.00Dichlorodifluoromethane 1 09/01/23 07:31 V37379MSA
<0.240 µg/L 0.240 0.5001,1-Dichloroethane 1 09/01/23 07:31 V37379MSA
<0.150 µg/L 0.150 0.5001,2-Dichloroethane 1 09/01/23 07:31 V37379MSA
<0.150 µg/L 0.150 0.5001,1-Dichloroethene 1 09/01/23 07:31 V37379MSA
<0.200 µg/L 0.200 0.500cis-1,2-Dichloroethene 1 09/01/23 07:31 V37379MSA
<0.180 µg/L 0.180 0.500trans-1,2-Dichloroethene 1 09/01/23 07:31 V37379MSA
<0.190 µg/L 0.190 0.5001,2-Dichloropropane 1 09/01/23 07:31 V37379MSA
<0.130 µg/L 0.130 0.5001,3-Dichloropropane 1 09/01/23 07:31 V37379MSA
<0.210 µg/L 0.210 2.002,2-Dichloropropane 1 09/01/23 07:31 V37379MSA
<0.200 µg/L 0.200 0.5001,1-Dichloropropene 1 09/01/23 07:31 V37379MSA
<0.210 µg/L 0.210 0.500cis-1,3-Dichloropropene 1 09/01/23 07:31 V37379MSA
<0.150 µg/L 0.150 0.500trans-1,3-Dichloropropene 1 09/01/23 07:31 V37379MSA
<42.0 µg/L 42.0 200Ethanol 1 09/01/23 07:31 V37379MSA
4170 µg/L 17.0 50.0Ethylbenzene 100 09/01/23 23:14 V37437MSA
<0.350 µg/L 0.350 3.00Hexachlorobutadiene 1 09/01/23 07:31 V37379MSA
<0.380 µg/L 0.380 1.002-Hexanone 1 09/01/23 07:31 V37379MSA
117 µg/L 18.0 50.0Isopropylbenzene 100 09/01/23 23:14 V37437MSA
7.01 µg/L 0.089 0.5004-Isopropyl toluene 1 09/01/23 07:31 V37379MSA
<0.710 µg/L 0.710 5.00Methyl Ethyl Ketone (MEK)1 09/01/23 07:31 V37379MSA
16.5 µg/L 0.140 1.00Methyl tert-butyl ether (MTBE)1 09/01/23 07:31 V37379MSA
<0.078 µg/L 0.078 1.004-Methyl-2-Pentanone 1 09/01/23 07:31 V37379MSA
<0.330 µg/L 0.330 2.00Methylene Chloride 1 09/01/23 07:31 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 22 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-3
93505 Matrix:
8/24/2023 8:39
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
V37551 09/06/23 09:00
1130 µg/L 47.0 100Naphthalene 100 09/01/23 23:14 V37437MSA
330 µg/L 19.0 50.0n-Propylbenzene 100 09/01/23 23:14 V37437MSA
163 µg/L 22.0 50.0Styrene 100 09/01/23 23:14 V37437MSA
11.4 µg/L 1.60 10.0tert-Butyl Alcohol (TBA)1 09/01/23 07:31 V37379MSA
<0.350 µg/L 0.350 10.0tert-Butyl formate (TBF)1 09/01/23 07:31 V37379MSA
440.50 E µg/L 1.90 10tert-Amyl Alcohol (TAA)1 09/01/23 07:31 V37379MSA
<0.280 µg/L 0.280 10.0tert-Amyl Methyl Ether (TAME)1 09/01/23 07:31 V37379MSA
<0.160 µg/L 0.160 0.5001,1,1,2-Tetrachloroethane 1 09/01/23 07:31 V37379MSA
<0.160 µg/L 0.160 0.5001,1,2,2-Tetrachloroethane 1 09/01/23 07:31 V37379MSA
0.623 µg/L 0.220 0.500Tetrachloroethene 1 09/01/23 07:31 V37379MSA
13400 µg/L 220 500Toluene 1000 09/06/23 22:55 V37553MSA
<0.380 µg/L 0.380 0.5001,2,3-Trichlorobenzene 1 09/01/23 07:31 V37379MSA
<0.310 µg/L 0.310 0.5001,2,4-Trichlorobenzene 1 09/01/23 07:31 V37379MSA
<0.160 µg/L 0.160 0.5001,1,1-Trichloroethane 1 09/01/23 07:31 V37379MSA
9.57 µg/L 0.096 0.5001,1,2-Trichloroethane 1 09/01/23 07:31 V37379MSA
0.745 µg/L 0.180 0.500Trichloroethene 1 09/01/23 07:31 V37379MSA
<0.180 µg/L 0.180 0.500Trichlorofluoromethane 1 09/01/23 07:31 V37379MSA
<0.270 µg/L 0.270 0.5001,2,3-Trichloropropane 1 09/01/23 07:31 V37379MSA
2860 µg/L 19.0 50.01,2,4-Trimethylbenzene 100 09/01/23 23:14 V37437MSA
701 µg/L 18.0 50.01,3,5-Trimethylbenzene 100 09/01/23 23:14 V37437MSA
<1.00 µg/L 1.00 5.00Vinyl Acetate 1 09/01/23 07:31 V37379MSA
<0.170 µg/L 0.170 0.500Vinyl Chloride 1 09/01/23 07:31 V37379MSA
5640 µg/L 21.0 50.0o-Xylene 100 09/01/23 23:14 V37437MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 23 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-3
93505 Matrix:
8/24/2023 8:39
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
V37551 09/06/23 09:00
12200 µg/L 42.0 100m,p-Xylene 100 09/01/23 23:14 V37437MSA
17800 µg/L 21.0 50.0Xylene (Total)100 09/01/23 23:14 V37437
Surrogate: 4-Bromofluorobenzene 94.6 Limits: 70-130%09/01/23 07:311 MSA V37379
Surrogate: Dibromofluoromethane 94.8 Limits: 70-130%09/01/23 07:311 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 97.2 Limits: 70-130%09/01/23 07:311 MSA V37379
Surrogate: Toluene-d8 98.6 Limits: 70-130%09/01/23 07:311 MSA V37379
Surrogate: 4-Bromofluorobenzene 93.8 Limits: 70-130%09/01/23 23:14100 MSA V37437
Surrogate: Dibromofluoromethane 101 Limits: 70-130%09/01/23 23:14100 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 88.2 Limits: 70-130%09/01/23 23:14100 MSA V37437
Surrogate: Toluene-d8 100 Limits: 70-130%09/01/23 23:14100 MSA V37437
Surrogate: 4-Bromofluorobenzene 99.0 Limits: 70-130%09/06/23 22:551000 MSA V37553
Surrogate: Dibromofluoromethane 102 Limits: 70-130%09/06/23 22:551000 MSA V37553
Surrogate: 1,2-Dichloroethane - d4 89.6 Limits: 70-130%09/06/23 22:551000 MSA V37553
Surrogate: Toluene-d8 99.0 Limits: 70-130%09/06/23 22:551000 MSA V37553
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 24 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-4
93506 Matrix:
8/24/2023 8:47
Aqueous
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
<100 µg/L 100 10003,3-Dimethyl-1-butanol 100 09/01/23 11:48 6200BMSA
Surrogate: 4-Bromofluorobenzene 95.0 Limits: 70-130%09/01/23 11:48100 MSA V37379
Surrogate: Dibromofluoromethane 97.8 Limits: 70-130%09/01/23 11:48100 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 89.6 Limits: 70-130%09/01/23 11:48100 MSA V37379
Surrogate: Toluene-d8 101 Limits: 70-130%09/01/23 11:48100 MSA V37379
Surrogate: 4-Bromofluorobenzene 95.0 Limits: 70-130%09/02/23 00:311000 MSA V37437
Surrogate: Dibromofluoromethane 102 Limits: 70-130%09/02/23 00:311000 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 87.8 Limits: 70-130%09/02/23 00:311000 MSA V37437
Surrogate: Toluene-d8 100 Limits: 70-130%09/02/23 00:311000 MSA V37437
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 25 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-4
93506 Matrix:
8/24/2023 8:47
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
1590 µg/L 180 1000Acetone 100 09/01/23 11:48 V37379MSA
22100 µg/L 180 500Benzene 1000 09/02/23 00:31 V37437MSA
<21.0 µg/L 21.0 50.0Bromobenzene 100 09/01/23 11:48 V37379MSA
<42.0 µg/L 42.0 100Bromochloromethane 100 09/01/23 11:48 V37379MSA
<16.0 µg/L 16.0 50.0Bromodichloromethane 100 09/01/23 11:48 V37379MSA
<150 µg/L 150 500Bromoform 100 09/01/23 11:48 V37379MSA
<28.0 µg/L 28.0 100Bromomethane 100 09/01/23 11:48 V37379MSA
<18.0 µg/L 18.0 50.0n-Butylbenzene 100 09/01/23 11:48 V37379MSA
<20.0 µg/L 20.0 50.0sec-Butyl benzene 100 09/01/23 11:48 V37379MSA
<92.0 µg/L 92.0 200tert-Butyl benzene 100 09/01/23 11:48 V37379MSA
<18.0 µg/L 18.0 50.0Carbon Tetrachloride 100 09/01/23 11:48 V37379MSA
<19.0 µg/L 19.0 50.0Chlorobenzene 100 09/01/23 11:48 V37379MSA
<19.0 µg/L 19.0 50.0Chlorodibromomethane 100 09/01/23 11:48 V37379MSA
<43.0 µg/L 43.0 100Chloroethane 100 09/01/23 11:48 V37379MSA
<22.0 µg/L 22.0 50.0Chloroform 100 09/01/23 11:48 V37379MSA
<22.0 µg/L 22.0 50.0Chloromethane 100 09/01/23 11:48 V37379MSA
<20.0 µg/L 20.0 50.02-Chlorotoluene 100 09/01/23 11:48 V37379MSA
<20.0 µg/L 20.0 50.04-Chlorotoluene 100 09/01/23 11:48 V37379MSA
686 µg/L 50.0 50.0Di-Isopropyl Ether (DIPE)100 09/01/23 11:48 V37379MSA
<110 µg/L 110 2001,2-Dibromo-3-Chloropropane 100 09/01/23 11:48 V37379MSA
<23.0 µg/L 23.0 50.0Dibromomethane 100 09/01/23 11:48 V37379MSA
<22.0 µg/L 22.0 50.01,2-Dichlorobenzene 100 09/01/23 11:48 V37379MSA
<19.0 µg/L 19.0 50.01,3-Dichlorobenzene 100 09/01/23 11:48 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 26 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-4
93506 Matrix:
8/24/2023 8:47
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
<21.0 µg/L 21.0 50.01,4-Dichlorobenzene 100 09/01/23 11:48 V37379MSA
<120 µg/L 120 500Dichlorodifluoromethane 100 09/01/23 11:48 V37379MSA
<24.0 µg/L 24.0 50.01,1-Dichloroethane 100 09/01/23 11:48 V37379MSA
<15.0 µg/L 15.0 50.01,2-Dichloroethane 100 09/01/23 11:48 V37379MSA
<15.0 µg/L 15.0 50.01,1-Dichloroethene 100 09/01/23 11:48 V37379MSA
<20.0 µg/L 20.0 50.0cis-1,2-Dichloroethene 100 09/01/23 11:48 V37379MSA
<18.0 µg/L 18.0 50.0trans-1,2-Dichloroethene 100 09/01/23 11:48 V37379MSA
<19.0 µg/L 19.0 50.01,2-Dichloropropane 100 09/01/23 11:48 V37379MSA
<13.0 µg/L 13.0 50.01,3-Dichloropropane 100 09/01/23 11:48 V37379MSA
<21.0 µg/L 21.0 2002,2-Dichloropropane 100 09/01/23 11:48 V37379MSA
<20.0 µg/L 20.0 50.01,1-Dichloropropene 100 09/01/23 11:48 V37379MSA
<21.0 µg/L 21.0 50.0cis-1,3-Dichloropropene 100 09/01/23 11:48 V37379MSA
<15.0 µg/L 15.0 50.0trans-1,3-Dichloropropene 100 09/01/23 11:48 V37379MSA
<4200 µg/L 4200 20000Ethanol 100 09/01/23 11:48 V37379MSA
3180 µg/L 17.0 50.0Ethylbenzene 100 09/01/23 11:48 V37379MSA
<35.0 µg/L 35.0 300Hexachlorobutadiene 100 09/01/23 11:48 V37379MSA
<38.0 µg/L 38.0 1002-Hexanone 100 09/01/23 11:48 V37379MSA
84.9 µg/L 18.0 50.0Isopropylbenzene 100 09/01/23 11:48 V37379MSA
<8.90 µg/L 8.90 50.04-Isopropyl toluene 100 09/01/23 11:48 V37379MSA
768 µg/L 71.0 500Methyl Ethyl Ketone (MEK)100 09/01/23 11:48 V37379MSA
15400 µg/L 140 1000Methyl tert-butyl ether (MTBE)1000 09/02/23 00:31 V37437MSA
<7.80 µg/L 7.80 1004-Methyl-2-Pentanone 100 09/01/23 11:48 V37379MSA
<33.0 µg/L 33.0 200Methylene Chloride 100 09/01/23 11:48 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 27 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-4
93506 Matrix:
8/24/2023 8:47
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
892 µg/L 47.0 100Naphthalene 100 09/01/23 11:48 V37379MSA
234 µg/L 19.0 50.0n-Propylbenzene 100 09/01/23 11:48 V37379MSA
135 µg/L 22.0 50.0Styrene 100 09/01/23 11:48 V37379MSA
1420 µg/L 160 1000tert-Butyl Alcohol (TBA)100 09/01/23 11:48 V37379MSA
<35.0 µg/L 35.0 1000tert-Butyl formate (TBF)100 09/01/23 11:48 V37379MSA
5310 µg/L 190 1000tert-Amyl Alcohol (TAA)100 09/01/23 11:48 V37379MSA
91.0 J µg/L 28.0 1000tert-Amyl Methyl Ether (TAME)100 09/01/23 11:48 V37379MSA
<16.0 µg/L 16.0 50.01,1,1,2-Tetrachloroethane 100 09/01/23 11:48 V37379MSA
<16.0 µg/L 16.0 50.01,1,2,2-Tetrachloroethane 100 09/01/23 11:48 V37379MSA
<22.0 µg/L 22.0 50.0Tetrachloroethene 100 09/01/23 11:48 V37379MSA
46900 µg/L 220 500Toluene 1000 09/02/23 00:31 V37437MSA
<38.0 µg/L 38.0 50.01,2,3-Trichlorobenzene 100 09/01/23 11:48 V37379MSA
<31.0 µg/L 31.0 50.01,2,4-Trichlorobenzene 100 09/01/23 11:48 V37379MSA
<16.0 µg/L 16.0 50.01,1,1-Trichloroethane 100 09/01/23 11:48 V37379MSA
<9.60 µg/L 9.60 50.01,1,2-Trichloroethane 100 09/01/23 11:48 V37379MSA
<18.0 µg/L 18.0 50.0Trichloroethene 100 09/01/23 11:48 V37379MSA
<18.0 µg/L 18.0 50.0Trichlorofluoromethane 100 09/01/23 11:48 V37379MSA
<27.0 µg/L 27.0 50.01,2,3-Trichloropropane 100 09/01/23 11:48 V37379MSA
2060 µg/L 19.0 50.01,2,4-Trimethylbenzene 100 09/01/23 11:48 V37379MSA
552 µg/L 18.0 50.01,3,5-Trimethylbenzene 100 09/01/23 11:48 V37379MSA
<100 µg/L 100 500Vinyl Acetate 100 09/01/23 11:48 V37379MSA
<17.0 µg/L 17.0 50.0Vinyl Chloride 100 09/01/23 11:48 V37379MSA
6050 µg/L 21.0 50.0o-Xylene 100 09/01/23 11:48 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 28 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-4
93506 Matrix:
8/24/2023 8:47
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
12500 µg/L 42.0 100m,p-Xylene 100 09/01/23 11:48 V37379MSA
18600 µg/L 21.0 50.0Xylene (Total)100 09/01/23 11:48 V37379
Surrogate: 4-Bromofluorobenzene 95.0 Limits: 70-130%09/01/23 11:48100 MSA V37379
Surrogate: Dibromofluoromethane 97.8 Limits: 70-130%09/01/23 11:48100 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 89.6 Limits: 70-130%09/01/23 11:48100 MSA V37379
Surrogate: Toluene-d8 101 Limits: 70-130%09/01/23 11:48100 MSA V37379
Surrogate: 4-Bromofluorobenzene 95.0 Limits: 70-130%09/02/23 00:311000 MSA V37437
Surrogate: Dibromofluoromethane 102 Limits: 70-130%09/02/23 00:311000 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 87.8 Limits: 70-130%09/02/23 00:311000 MSA V37437
Surrogate: Toluene-d8 100 Limits: 70-130%09/02/23 00:311000 MSA V37437
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 29 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-5
93507 Matrix:
8/24/2023 9:18
Aqueous
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
<100 µg/L 100 10003,3-Dimethyl-1-butanol 100 09/01/23 12:14 6200BMSA
0.002 J mg/L 0.002 0.006Lead 1 08/29/23 22:15 6010DMMR
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 30 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-5
93507 Matrix:
8/24/2023 9:18
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
495 J µg/L 180 1000Acetone 100 09/01/23 12:14 V37379MSA
760 µg/L 18.0 50.0Benzene 100 09/01/23 12:14 V37379MSA
<21.0 µg/L 21.0 50.0Bromobenzene 100 09/01/23 12:14 V37379MSA
<42.0 µg/L 42.0 100Bromochloromethane 100 09/01/23 12:14 V37379MSA
<16.0 µg/L 16.0 50.0Bromodichloromethane 100 09/01/23 12:14 V37379MSA
<150 µg/L 150 500Bromoform 100 09/01/23 12:14 V37379MSA
<28.0 µg/L 28.0 100Bromomethane 100 09/01/23 12:14 V37379MSA
35.8 J µg/L 18.0 50.0n-Butylbenzene 100 09/01/23 12:14 V37379MSA
<20.0 µg/L 20.0 50.0sec-Butyl benzene 100 09/01/23 12:14 V37379MSA
<92.0 µg/L 92.0 200tert-Butyl benzene 100 09/01/23 12:14 V37379MSA
<18.0 µg/L 18.0 50.0Carbon Tetrachloride 100 09/01/23 12:14 V37379MSA
<19.0 µg/L 19.0 50.0Chlorobenzene 100 09/01/23 12:14 V37379MSA
<19.0 µg/L 19.0 50.0Chlorodibromomethane 100 09/01/23 12:14 V37379MSA
<43.0 µg/L 43.0 100Chloroethane 100 09/01/23 12:14 V37379MSA
<22.0 µg/L 22.0 50.0Chloroform 100 09/01/23 12:14 V37379MSA
<22.0 µg/L 22.0 50.0Chloromethane 100 09/01/23 12:14 V37379MSA
<20.0 µg/L 20.0 50.02-Chlorotoluene 100 09/01/23 12:14 V37379MSA
<20.0 µg/L 20.0 50.04-Chlorotoluene 100 09/01/23 12:14 V37379MSA
232 µg/L 50.0 50.0Di-Isopropyl Ether (DIPE)100 09/01/23 12:14 V37379MSA
<110 µg/L 110 2001,2-Dibromo-3-Chloropropane 100 09/01/23 12:14 V37379MSA
<23.0 µg/L 23.0 50.0Dibromomethane 100 09/01/23 12:14 V37379MSA
<22.0 µg/L 22.0 50.01,2-Dichlorobenzene 100 09/01/23 12:14 V37379MSA
<19.0 µg/L 19.0 50.01,3-Dichlorobenzene 100 09/01/23 12:14 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 31 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-5
93507 Matrix:
8/24/2023 9:18
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
<21.0 µg/L 21.0 50.01,4-Dichlorobenzene 100 09/01/23 12:14 V37379MSA
<120 µg/L 120 500Dichlorodifluoromethane 100 09/01/23 12:14 V37379MSA
<24.0 µg/L 24.0 50.01,1-Dichloroethane 100 09/01/23 12:14 V37379MSA
<15.0 µg/L 15.0 50.01,2-Dichloroethane 100 09/01/23 12:14 V37379MSA
<15.0 µg/L 15.0 50.01,1-Dichloroethene 100 09/01/23 12:14 V37379MSA
<20.0 µg/L 20.0 50.0cis-1,2-Dichloroethene 100 09/01/23 12:14 V37379MSA
<18.0 µg/L 18.0 50.0trans-1,2-Dichloroethene 100 09/01/23 12:14 V37379MSA
<19.0 µg/L 19.0 50.01,2-Dichloropropane 100 09/01/23 12:14 V37379MSA
<13.0 µg/L 13.0 50.01,3-Dichloropropane 100 09/01/23 12:14 V37379MSA
<21.0 µg/L 21.0 2002,2-Dichloropropane 100 09/01/23 12:14 V37379MSA
<20.0 µg/L 20.0 50.01,1-Dichloropropene 100 09/01/23 12:14 V37379MSA
<21.0 µg/L 21.0 50.0cis-1,3-Dichloropropene 100 09/01/23 12:14 V37379MSA
<15.0 µg/L 15.0 50.0trans-1,3-Dichloropropene 100 09/01/23 12:14 V37379MSA
<4200 µg/L 4200 20000Ethanol 100 09/01/23 12:14 V37379MSA
2560 µg/L 17.0 50.0Ethylbenzene 100 09/01/23 12:14 V37379MSA
<35.0 µg/L 35.0 300Hexachlorobutadiene 100 09/01/23 12:14 V37379MSA
<38.0 µg/L 38.0 1002-Hexanone 100 09/01/23 12:14 V37379MSA
130 µg/L 18.0 50.0Isopropylbenzene 100 09/01/23 12:14 V37379MSA
<8.90 µg/L 8.90 50.04-Isopropyl toluene 100 09/01/23 12:14 V37379MSA
<71.0 µg/L 71.0 500Methyl Ethyl Ketone (MEK)100 09/01/23 12:14 V37379MSA
7580 µg/L 14.0 100Methyl tert-butyl ether (MTBE)100 09/01/23 12:14 V37379MSA
<7.80 µg/L 7.80 1004-Methyl-2-Pentanone 100 09/01/23 12:14 V37379MSA
<33.0 µg/L 33.0 200Methylene Chloride 100 09/01/23 12:14 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 32 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-5
93507 Matrix:
8/24/2023 9:18
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
1310 µg/L 47.0 100Naphthalene 100 09/01/23 12:14 V37379MSA
372 µg/L 19.0 50.0n-Propylbenzene 100 09/01/23 12:14 V37379MSA
102 µg/L 22.0 50.0Styrene 100 09/01/23 12:14 V37379MSA
877 J µg/L 160 1000tert-Butyl Alcohol (TBA)100 09/01/23 12:14 V37379MSA
<35.0 µg/L 35.0 1000tert-Butyl formate (TBF)100 09/01/23 12:14 V37379MSA
858 J µg/L 190 1000tert-Amyl Alcohol (TAA)100 09/01/23 12:14 V37379MSA
241 J µg/L 28.0 1000tert-Amyl Methyl Ether (TAME)100 09/01/23 12:14 V37379MSA
<16.0 µg/L 16.0 50.01,1,1,2-Tetrachloroethane 100 09/01/23 12:14 V37379MSA
<16.0 µg/L 16.0 50.01,1,2,2-Tetrachloroethane 100 09/01/23 12:14 V37379MSA
<22.0 µg/L 22.0 50.0Tetrachloroethene 100 09/01/23 12:14 V37379MSA
1150 µg/L 22.0 50.0Toluene 100 09/01/23 12:14 V37379MSA
<38.0 µg/L 38.0 50.01,2,3-Trichlorobenzene 100 09/01/23 12:14 V37379MSA
<31.0 µg/L 31.0 50.01,2,4-Trichlorobenzene 100 09/01/23 12:14 V37379MSA
<16.0 µg/L 16.0 50.01,1,1-Trichloroethane 100 09/01/23 12:14 V37379MSA
<9.60 µg/L 9.60 50.01,1,2-Trichloroethane 100 09/01/23 12:14 V37379MSA
<18.0 µg/L 18.0 50.0Trichloroethene 100 09/01/23 12:14 V37379MSA
<18.0 µg/L 18.0 50.0Trichlorofluoromethane 100 09/01/23 12:14 V37379MSA
<27.0 µg/L 27.0 50.01,2,3-Trichloropropane 100 09/01/23 12:14 V37379MSA
2740 µg/L 19.0 50.01,2,4-Trimethylbenzene 100 09/01/23 12:14 V37379MSA
668 µg/L 18.0 50.01,3,5-Trimethylbenzene 100 09/01/23 12:14 V37379MSA
<100 µg/L 100 500Vinyl Acetate 100 09/01/23 12:14 V37379MSA
<17.0 µg/L 17.0 50.0Vinyl Chloride 100 09/01/23 12:14 V37379MSA
2270 µg/L 21.0 50.0o-Xylene 100 09/01/23 12:14 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 33 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-5
93507 Matrix:
8/24/2023 9:18
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
7980 µg/L 42.0 100m,p-Xylene 100 09/01/23 12:14 V37379MSA
10300 µg/L 21.0 50.0Xylene (Total)100 09/01/23 12:14 V37379
Surrogate: 4-Bromofluorobenzene 94.4 Limits: 70-130%09/01/23 12:14100 MSA V37379
Surrogate: Dibromofluoromethane 99.8 Limits: 70-130%09/01/23 12:14100 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 88.6 Limits: 70-130%09/01/23 12:14100 MSA V37379
Surrogate: Toluene-d8 99.6 Limits: 70-130%09/01/23 12:14100 MSA V37379
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
EPA-504.1(PREP)
EPA-504.1 Prep Batch(es):V37272 08/31/23 09:31
<0.0207 µg/L 0.02071,2-Dibromoethane 1 08/31/23 12:58 V37326AMP
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 34 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-5
93507 Matrix:
8/24/2023 9:18
Aqueous
Analytical Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
CALCULATION
5650 µg/L 500Aliphatic C5-C8 (Adjusted)10 08/28/23 22:49
5990 µg/L 2500Aliphatics C9-C12 (Adjusted)100 08/29/23 07:22
10300 µg/L 2500Aromatic C9-C10 (Adjusted)50 08/29/23 07:22
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
MAVPH (Prep)
MADEP-VPH Prep Batch(es):V37164 08/28/23 08:00
7560 µg/L 115 500Aliphatic C5-C8 10 08/28/23 22:49 V37165TBL
29100 µg/L 1290 2500Aliphatic C9-C12 50 08/29/23 07:22 V37165TBL
10300 µg/L 201 2500Aromatic C9-C10 50 08/29/23 07:22 V37165TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (FID)91.1 Limits: 70-130%08/28/23 22:4910 TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (PID)94.8 Limits: 70-130%08/28/23 22:4910 TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (FID)113 Limits: 70-130%08/29/23 07:2250 TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (PID)98.0 Limits: 70-130%08/29/23 07:2250 TBL
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 35 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-6
93508 Matrix:
8/24/2023 9:09
Aqueous
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
<100 µg/L 100 10003,3-Dimethyl-1-butanol 100 09/01/23 12:39 6200BMSA
0.006 mg/L 0.002 0.006Lead 1 08/29/23 22:19 6010DMMR
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 36 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-6
93508 Matrix:
8/24/2023 9:09
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
831 J µg/L 180 1000Acetone 100 09/01/23 12:39 V37379MSA
4530 µg/L 18.0 50.0Benzene 100 09/01/23 12:39 V37379MSA
<21.0 µg/L 21.0 50.0Bromobenzene 100 09/01/23 12:39 V37379MSA
<42.0 µg/L 42.0 100Bromochloromethane 100 09/01/23 12:39 V37379MSA
<16.0 µg/L 16.0 50.0Bromodichloromethane 100 09/01/23 12:39 V37379MSA
<150 µg/L 150 500Bromoform 100 09/01/23 12:39 V37379MSA
<28.0 µg/L 28.0 100Bromomethane 100 09/01/23 12:39 V37379MSA
<18.0 µg/L 18.0 50.0n-Butylbenzene 100 09/01/23 12:39 V37379MSA
<20.0 µg/L 20.0 50.0sec-Butyl benzene 100 09/01/23 12:39 V37379MSA
<92.0 µg/L 92.0 200tert-Butyl benzene 100 09/01/23 12:39 V37379MSA
<18.0 µg/L 18.0 50.0Carbon Tetrachloride 100 09/01/23 12:39 V37379MSA
<19.0 µg/L 19.0 50.0Chlorobenzene 100 09/01/23 12:39 V37379MSA
<19.0 µg/L 19.0 50.0Chlorodibromomethane 100 09/01/23 12:39 V37379MSA
<43.0 µg/L 43.0 100Chloroethane 100 09/01/23 12:39 V37379MSA
<22.0 µg/L 22.0 50.0Chloroform 100 09/01/23 12:39 V37379MSA
<22.0 µg/L 22.0 50.0Chloromethane 100 09/01/23 12:39 V37379MSA
<20.0 µg/L 20.0 50.02-Chlorotoluene 100 09/01/23 12:39 V37379MSA
<20.0 µg/L 20.0 50.04-Chlorotoluene 100 09/01/23 12:39 V37379MSA
135 µg/L 50.0 50.0Di-Isopropyl Ether (DIPE)100 09/01/23 12:39 V37379MSA
<110 µg/L 110 2001,2-Dibromo-3-Chloropropane 100 09/01/23 12:39 V37379MSA
<23.0 µg/L 23.0 50.0Dibromomethane 100 09/01/23 12:39 V37379MSA
<22.0 µg/L 22.0 50.01,2-Dichlorobenzene 100 09/01/23 12:39 V37379MSA
<19.0 µg/L 19.0 50.01,3-Dichlorobenzene 100 09/01/23 12:39 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 37 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-6
93508 Matrix:
8/24/2023 9:09
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
<21.0 µg/L 21.0 50.01,4-Dichlorobenzene 100 09/01/23 12:39 V37379MSA
<120 µg/L 120 500Dichlorodifluoromethane 100 09/01/23 12:39 V37379MSA
<24.0 µg/L 24.0 50.01,1-Dichloroethane 100 09/01/23 12:39 V37379MSA
<15.0 µg/L 15.0 50.01,2-Dichloroethane 100 09/01/23 12:39 V37379MSA
<15.0 µg/L 15.0 50.01,1-Dichloroethene 100 09/01/23 12:39 V37379MSA
<20.0 µg/L 20.0 50.0cis-1,2-Dichloroethene 100 09/01/23 12:39 V37379MSA
<18.0 µg/L 18.0 50.0trans-1,2-Dichloroethene 100 09/01/23 12:39 V37379MSA
<19.0 µg/L 19.0 50.01,2-Dichloropropane 100 09/01/23 12:39 V37379MSA
<13.0 µg/L 13.0 50.01,3-Dichloropropane 100 09/01/23 12:39 V37379MSA
<21.0 µg/L 21.0 2002,2-Dichloropropane 100 09/01/23 12:39 V37379MSA
<20.0 µg/L 20.0 50.01,1-Dichloropropene 100 09/01/23 12:39 V37379MSA
<21.0 µg/L 21.0 50.0cis-1,3-Dichloropropene 100 09/01/23 12:39 V37379MSA
<15.0 µg/L 15.0 50.0trans-1,3-Dichloropropene 100 09/01/23 12:39 V37379MSA
<4200 µg/L 4200 20000Ethanol 100 09/01/23 12:39 V37379MSA
3900 µg/L 17.0 50.0Ethylbenzene 100 09/01/23 12:39 V37379MSA
<35.0 µg/L 35.0 300Hexachlorobutadiene 100 09/01/23 12:39 V37379MSA
<38.0 µg/L 38.0 1002-Hexanone 100 09/01/23 12:39 V37379MSA
101 µg/L 18.0 50.0Isopropylbenzene 100 09/01/23 12:39 V37379MSA
<8.90 µg/L 8.90 50.04-Isopropyl toluene 100 09/01/23 12:39 V37379MSA
<71.0 µg/L 71.0 500Methyl Ethyl Ketone (MEK)100 09/01/23 12:39 V37379MSA
<14.0 µg/L 14.0 100Methyl tert-butyl ether (MTBE)100 09/01/23 12:39 V37379MSA
<7.80 µg/L 7.80 1004-Methyl-2-Pentanone 100 09/01/23 12:39 V37379MSA
<33.0 µg/L 33.0 200Methylene Chloride 100 09/01/23 12:39 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 38 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-6
93508 Matrix:
8/24/2023 9:09
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
1080 µg/L 47.0 100Naphthalene 100 09/01/23 12:39 V37379MSA
308 µg/L 19.0 50.0n-Propylbenzene 100 09/01/23 12:39 V37379MSA
206 µg/L 22.0 50.0Styrene 100 09/01/23 12:39 V37379MSA
<160 µg/L 160 1000tert-Butyl Alcohol (TBA)100 09/01/23 12:39 V37379MSA
<35.0 µg/L 35.0 1000tert-Butyl formate (TBF)100 09/01/23 12:39 V37379MSA
2260 µg/L 190 1000tert-Amyl Alcohol (TAA)100 09/01/23 12:39 V37379MSA
<28.0 µg/L 28.0 1000tert-Amyl Methyl Ether (TAME)100 09/01/23 12:39 V37379MSA
<16.0 µg/L 16.0 50.01,1,1,2-Tetrachloroethane 100 09/01/23 12:39 V37379MSA
<16.0 µg/L 16.0 50.01,1,2,2-Tetrachloroethane 100 09/01/23 12:39 V37379MSA
<22.0 µg/L 22.0 50.0Tetrachloroethene 100 09/01/23 12:39 V37379MSA
27400 µg/L 220 500Toluene 1000 09/02/23 00:57 V37437MSA
<38.0 µg/L 38.0 50.01,2,3-Trichlorobenzene 100 09/01/23 12:39 V37379MSA
<31.0 µg/L 31.0 50.01,2,4-Trichlorobenzene 100 09/01/23 12:39 V37379MSA
<16.0 µg/L 16.0 50.01,1,1-Trichloroethane 100 09/01/23 12:39 V37379MSA
<9.60 µg/L 9.60 50.01,1,2-Trichloroethane 100 09/01/23 12:39 V37379MSA
<18.0 µg/L 18.0 50.0Trichloroethene 100 09/01/23 12:39 V37379MSA
<18.0 µg/L 18.0 50.0Trichlorofluoromethane 100 09/01/23 12:39 V37379MSA
<27.0 µg/L 27.0 50.01,2,3-Trichloropropane 100 09/01/23 12:39 V37379MSA
2260 µg/L 19.0 50.01,2,4-Trimethylbenzene 100 09/01/23 12:39 V37379MSA
551 µg/L 18.0 50.01,3,5-Trimethylbenzene 100 09/01/23 12:39 V37379MSA
<100 µg/L 100 500Vinyl Acetate 100 09/01/23 12:39 V37379MSA
<17.0 µg/L 17.0 50.0Vinyl Chloride 100 09/01/23 12:39 V37379MSA
5140 µg/L 21.0 50.0o-Xylene 100 09/01/23 12:39 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 39 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-6
93508 Matrix:
8/24/2023 9:09
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00 V37436 09/01/23 09:00
12100 µg/L 42.0 100m,p-Xylene 100 09/01/23 12:39 V37379MSA
17200 µg/L 21.0 50.0Xylene (Total)100 09/01/23 12:39 V37379
Surrogate: 4-Bromofluorobenzene 93.8 Limits: 70-130%09/01/23 12:39100 MSA V37379
Surrogate: Dibromofluoromethane 99.0 Limits: 70-130%09/01/23 12:39100 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 89.0 Limits: 70-130%09/01/23 12:39100 MSA V37379
Surrogate: Toluene-d8 99.2 Limits: 70-130%09/01/23 12:39100 MSA V37379
Surrogate: 4-Bromofluorobenzene 95.0 Limits: 70-130%09/02/23 00:571000 MSA V37437
Surrogate: Dibromofluoromethane 102 Limits: 70-130%09/02/23 00:571000 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 88.6 Limits: 70-130%09/02/23 00:571000 MSA V37437
Surrogate: Toluene-d8 99.4 Limits: 70-130%09/02/23 00:571000 MSA V37437
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
EPA-504.1(PREP)
EPA-504.1 Prep Batch(es):V37272 08/31/23 09:31
<0.0207 µg/L 0.02071,2-Dibromoethane 1 08/31/23 13:39 V37326AMP
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 40 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-6
93508 Matrix:
8/24/2023 9:09
Aqueous
Analytical Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
CALCULATION
33100 µg/L 5000Aliphatic C5-C8 (Adjusted)100 08/29/23 08:09
14900 µg/L 5000Aliphatics C9-C12 (Adjusted)100 08/29/23 08:09
7430 µg/L 5000Aromatic C9-C10 (Adjusted)100 08/29/23 08:09
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
MAVPH (Prep)
MADEP-VPH Prep Batch(es):V37164 08/28/23 08:00
65000 µg/L 1150 5000Aliphatic C5-C8 100 08/29/23 08:09 V37165TBL
43500 µg/L 2580 5000Aliphatic C9-C12 100 08/29/23 08:09 V37165TBL
7430 µg/L 402 5000Aromatic C9-C10 100 08/29/23 08:09 V37165TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (FID)87.4 Limits: 70-130%08/29/23 08:09100 TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (PID)90.0 Limits: 70-130%08/29/23 08:09100 TBL
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 41 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-7
93509 Matrix:
8/24/2023 8:58
Aqueous
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
<1.00 µg/L 1.00 10.03,3-Dimethyl-1-butanol 1 09/01/23 20:14 6200BMSA
0.008 mg/L 0.002 0.006Lead 1 08/29/23 22:24 6010DMMR
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 42 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-7
93509 Matrix:
8/24/2023 8:58
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37436 09/01/23 09:00
18.2 µg/L 1.80 10.0Acetone 1 09/01/23 20:14 V37437MSA
1.36 µg/L 0.180 0.500Benzene 1 09/01/23 20:14 V37437MSA
<0.210 µg/L 0.210 0.500Bromobenzene 1 09/01/23 20:14 V37437MSA
<0.420 µg/L 0.420 1.00Bromochloromethane 1 09/01/23 20:14 V37437MSA
<0.160 µg/L 0.160 0.500Bromodichloromethane 1 09/01/23 20:14 V37437MSA
<1.50 µg/L 1.50 5.00Bromoform 1 09/01/23 20:14 V37437MSA
<0.280 µg/L 0.280 1.00Bromomethane 1 09/01/23 20:14 V37437MSA
<0.180 µg/L 0.180 0.500n-Butylbenzene 1 09/01/23 20:14 V37437MSA
<0.200 µg/L 0.200 0.500sec-Butyl benzene 1 09/01/23 20:14 V37437MSA
<0.920 µg/L 0.920 2.00tert-Butyl benzene 1 09/01/23 20:14 V37437MSA
<0.180 µg/L 0.180 0.500Carbon Tetrachloride 1 09/01/23 20:14 V37437MSA
<0.190 µg/L 0.190 0.500Chlorobenzene 1 09/01/23 20:14 V37437MSA
<0.190 µg/L 0.190 0.500Chlorodibromomethane 1 09/01/23 20:14 V37437MSA
<0.430 µg/L 0.430 1.00Chloroethane 1 09/01/23 20:14 V37437MSA
0.928 µg/L 0.220 0.500Chloroform 1 09/01/23 20:14 V37437MSA
<0.220 µg/L 0.220 0.500Chloromethane 1 09/01/23 20:14 V37437MSA
<0.200 µg/L 0.200 0.5002-Chlorotoluene 1 09/01/23 20:14 V37437MSA
<0.200 µg/L 0.200 0.5004-Chlorotoluene 1 09/01/23 20:14 V37437MSA
9.05 µg/L 0.500 0.500Di-Isopropyl Ether (DIPE)1 09/01/23 20:14 V37437MSA
<1.10 µg/L 1.10 2.001,2-Dibromo-3-Chloropropane 1 09/01/23 20:14 V37437MSA
<0.230 µg/L 0.230 0.500Dibromomethane 1 09/01/23 20:14 V37437MSA
<0.220 µg/L 0.220 0.5001,2-Dichlorobenzene 1 09/01/23 20:14 V37437MSA
<0.190 µg/L 0.190 0.5001,3-Dichlorobenzene 1 09/01/23 20:14 V37437MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 43 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-7
93509 Matrix:
8/24/2023 8:58
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37436 09/01/23 09:00
<0.210 µg/L 0.210 0.5001,4-Dichlorobenzene 1 09/01/23 20:14 V37437MSA
<1.20 µg/L 1.20 5.00Dichlorodifluoromethane 1 09/01/23 20:14 V37437MSA
<0.240 µg/L 0.240 0.5001,1-Dichloroethane 1 09/01/23 20:14 V37437MSA
<0.150 µg/L 0.150 0.5001,2-Dichloroethane 1 09/01/23 20:14 V37437MSA
<0.150 µg/L 0.150 0.5001,1-Dichloroethene 1 09/01/23 20:14 V37437MSA
<0.200 µg/L 0.200 0.500cis-1,2-Dichloroethene 1 09/01/23 20:14 V37437MSA
<0.180 µg/L 0.180 0.500trans-1,2-Dichloroethene 1 09/01/23 20:14 V37437MSA
<0.190 µg/L 0.190 0.5001,2-Dichloropropane 1 09/01/23 20:14 V37437MSA
<0.130 µg/L 0.130 0.5001,3-Dichloropropane 1 09/01/23 20:14 V37437MSA
<0.210 µg/L 0.210 2.002,2-Dichloropropane 1 09/01/23 20:14 V37437MSA
<0.200 µg/L 0.200 0.5001,1-Dichloropropene 1 09/01/23 20:14 V37437MSA
<0.210 µg/L 0.210 0.500cis-1,3-Dichloropropene 1 09/01/23 20:14 V37437MSA
<0.150 µg/L 0.150 0.500trans-1,3-Dichloropropene 1 09/01/23 20:14 V37437MSA
<42.0 µg/L 42.0 200Ethanol 1 09/01/23 20:14 V37437MSA
0.668 µg/L 0.170 0.500Ethylbenzene 1 09/01/23 20:14 V37437MSA
<0.350 µg/L 0.350 3.00Hexachlorobutadiene 1 09/01/23 20:14 V37437MSA
<0.380 µg/L 0.380 1.002-Hexanone 1 09/01/23 20:14 V37437MSA
<0.180 µg/L 0.180 0.500Isopropylbenzene 1 09/01/23 20:14 V37437MSA
<0.089 µg/L 0.089 0.5004-Isopropyl toluene 1 09/01/23 20:14 V37437MSA
<0.710 µg/L 0.710 5.00Methyl Ethyl Ketone (MEK)1 09/01/23 20:14 V37437MSA
30.0 µg/L 0.140 1.00Methyl tert-butyl ether (MTBE)1 09/01/23 20:14 V37437MSA
<0.078 µg/L 0.078 1.004-Methyl-2-Pentanone 1 09/01/23 20:14 V37437MSA
0.454 J µg/L 0.330 2.00Methylene Chloride 1 09/01/23 20:14 V37437MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 44 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-7
93509 Matrix:
8/24/2023 8:58
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37436 09/01/23 09:00
<0.470 µg/L 0.470 1.00Naphthalene 1 09/01/23 20:14 V37437MSA
<0.190 µg/L 0.190 0.500n-Propylbenzene 1 09/01/23 20:14 V37437MSA
<0.220 µg/L 0.220 0.500Styrene 1 09/01/23 20:14 V37437MSA
14.4 µg/L 1.60 10.0tert-Butyl Alcohol (TBA)1 09/01/23 20:14 V37437MSA
<0.350 µg/L 0.350 10.0tert-Butyl formate (TBF)1 09/01/23 20:14 V37437MSA
24.8 µg/L 1.90 10.0tert-Amyl Alcohol (TAA)1 09/01/23 20:14 V37437MSA
<0.280 µg/L 0.280 10.0tert-Amyl Methyl Ether (TAME)1 09/01/23 20:14 V37437MSA
<0.160 µg/L 0.160 0.5001,1,1,2-Tetrachloroethane 1 09/01/23 20:14 V37437MSA
<0.160 µg/L 0.160 0.5001,1,2,2-Tetrachloroethane 1 09/01/23 20:14 V37437MSA
0.370 J µg/L 0.220 0.500Tetrachloroethene 1 09/01/23 20:14 V37437MSA
3.11 µg/L 0.220 0.500Toluene 1 09/01/23 20:14 V37437MSA
<0.380 µg/L 0.380 0.5001,2,3-Trichlorobenzene 1 09/01/23 20:14 V37437MSA
<0.310 µg/L 0.310 0.5001,2,4-Trichlorobenzene 1 09/01/23 20:14 V37437MSA
<0.160 µg/L 0.160 0.5001,1,1-Trichloroethane 1 09/01/23 20:14 V37437MSA
<0.096 µg/L 0.096 0.5001,1,2-Trichloroethane 1 09/01/23 20:14 V37437MSA
<0.180 µg/L 0.180 0.500Trichloroethene 1 09/01/23 20:14 V37437MSA
<0.180 µg/L 0.180 0.500Trichlorofluoromethane 1 09/01/23 20:14 V37437MSA
<0.270 µg/L 0.270 0.5001,2,3-Trichloropropane 1 09/01/23 20:14 V37437MSA
0.769 µg/L 0.190 0.5001,2,4-Trimethylbenzene 1 09/01/23 20:14 V37437MSA
0.256 J µg/L 0.180 0.5001,3,5-Trimethylbenzene 1 09/01/23 20:14 V37437MSA
<1.00 µg/L 1.00 5.00Vinyl Acetate 1 09/01/23 20:14 V37437MSA
<0.170 µg/L 0.170 0.500Vinyl Chloride 1 09/01/23 20:14 V37437MSA
0.858 µg/L 0.210 0.500o-Xylene 1 09/01/23 20:14 V37437MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 45 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-7
93509 Matrix:
8/24/2023 8:58
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37436 09/01/23 09:00
1.89 µg/L 0.420 1.00m,p-Xylene 1 09/01/23 20:14 V37437MSA
2.75 µg/L 0.210 0.500Xylene (Total)1 09/01/23 20:14 V37437
Surrogate: 4-Bromofluorobenzene 93.6 Limits: 70-130%09/01/23 20:141 MSA V37437
Surrogate: Dibromofluoromethane 102 Limits: 70-130%09/01/23 20:141 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 89.0 Limits: 70-130%09/01/23 20:141 MSA V37437
Surrogate: Toluene-d8 99.2 Limits: 70-130%09/01/23 20:141 MSA V37437
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
EPA-504.1(PREP)
EPA-504.1 Prep Batch(es):V37272 08/31/23 09:31
<0.0208 µg/L 0.02081,2-Dibromoethane 1 08/31/23 14:19 V37326AMP
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 46 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:MW-7
93509 Matrix:
8/24/2023 8:58
Aqueous
Analytical Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
CALCULATION
89.2 µg/L 50.0Aliphatic C5-C8 (Adjusted)1 08/28/23 19:41
26.0 µg/L 50.0Aliphatics C9-C12 (Adjusted)1 08/28/23 19:41
<4.02 µg/L 50.0Aromatic C9-C10 (Adjusted)1 08/28/23 19:41
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
MAVPH (Prep)
MADEP-VPH Prep Batch(es):V37164 08/28/23 08:00
93.7 µg/L 11.5 50.0Aliphatic C5-C8 1 08/28/23 19:41 V37165TBL
29.4 J µg/L 25.8 50.0Aliphatic C9-C12 1 08/28/23 19:41 V37165TBL
<4.02 µg/L 4.02 50.0Aromatic C9-C10 1 08/28/23 19:41 V37165TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (FID)78.4 Limits: 70-130%08/28/23 19:411 TBL
MADEP-VPHSurrogate: 2,5-Dibromotoluene (PID)94.4 Limits: 70-130%08/28/23 19:411 TBL
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 47 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TW-1
93510 Matrix:
8/24/2023 8:15
Aqueous
Test Results Units MDL MQL By Analytical
Method
Date / Time
Analyzed
DF
<1.00 µg/L 1.00 10.03,3-Dimethyl-1-butanol 1 09/01/23 20:40 6200BMSA
Surrogate: 4-Bromofluorobenzene 94.4 Limits: 70-130%09/01/23 20:401 MSA V37437
Surrogate: Dibromofluoromethane 103 Limits: 70-130%09/01/23 20:401 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 88.4 Limits: 70-130%09/01/23 20:401 MSA V37437
Surrogate: Toluene-d8 98.6 Limits: 70-130%09/01/23 20:401 MSA V37437
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 48 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TW-1
93510 Matrix:
8/24/2023 8:15
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37436 09/01/23 09:00
5.58 J µg/L 1.80 10.0Acetone 1 09/01/23 20:40 V37437MSA
<0.180 µg/L 0.180 0.500Benzene 1 09/01/23 20:40 V37437MSA
<0.210 µg/L 0.210 0.500Bromobenzene 1 09/01/23 20:40 V37437MSA
<0.420 µg/L 0.420 1.00Bromochloromethane 1 09/01/23 20:40 V37437MSA
<0.160 µg/L 0.160 0.500Bromodichloromethane 1 09/01/23 20:40 V37437MSA
<1.50 µg/L 1.50 5.00Bromoform 1 09/01/23 20:40 V37437MSA
<0.280 µg/L 0.280 1.00Bromomethane 1 09/01/23 20:40 V37437MSA
<0.180 µg/L 0.180 0.500n-Butylbenzene 1 09/01/23 20:40 V37437MSA
<0.200 µg/L 0.200 0.500sec-Butyl benzene 1 09/01/23 20:40 V37437MSA
<0.920 µg/L 0.920 2.00tert-Butyl benzene 1 09/01/23 20:40 V37437MSA
<0.180 µg/L 0.180 0.500Carbon Tetrachloride 1 09/01/23 20:40 V37437MSA
<0.190 µg/L 0.190 0.500Chlorobenzene 1 09/01/23 20:40 V37437MSA
<0.190 µg/L 0.190 0.500Chlorodibromomethane 1 09/01/23 20:40 V37437MSA
<0.430 µg/L 0.430 1.00Chloroethane 1 09/01/23 20:40 V37437MSA
1.94 µg/L 0.220 0.500Chloroform 1 09/01/23 20:40 V37437MSA
<0.220 µg/L 0.220 0.500Chloromethane 1 09/01/23 20:40 V37437MSA
<0.200 µg/L 0.200 0.5002-Chlorotoluene 1 09/01/23 20:40 V37437MSA
<0.200 µg/L 0.200 0.5004-Chlorotoluene 1 09/01/23 20:40 V37437MSA
<0.500 µg/L 0.500 0.500Di-Isopropyl Ether (DIPE)1 09/01/23 20:40 V37437MSA
<1.10 µg/L 1.10 2.001,2-Dibromo-3-Chloropropane 1 09/01/23 20:40 V37437MSA
<0.230 µg/L 0.230 0.500Dibromomethane 1 09/01/23 20:40 V37437MSA
<0.220 µg/L 0.220 0.5001,2-Dichlorobenzene 1 09/01/23 20:40 V37437MSA
<0.190 µg/L 0.190 0.5001,3-Dichlorobenzene 1 09/01/23 20:40 V37437MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 49 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TW-1
93510 Matrix:
8/24/2023 8:15
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37436 09/01/23 09:00
<0.210 µg/L 0.210 0.5001,4-Dichlorobenzene 1 09/01/23 20:40 V37437MSA
<1.20 µg/L 1.20 5.00Dichlorodifluoromethane 1 09/01/23 20:40 V37437MSA
<0.240 µg/L 0.240 0.5001,1-Dichloroethane 1 09/01/23 20:40 V37437MSA
<0.150 µg/L 0.150 0.5001,2-Dichloroethane 1 09/01/23 20:40 V37437MSA
<0.150 µg/L 0.150 0.5001,1-Dichloroethene 1 09/01/23 20:40 V37437MSA
<0.200 µg/L 0.200 0.500cis-1,2-Dichloroethene 1 09/01/23 20:40 V37437MSA
<0.180 µg/L 0.180 0.500trans-1,2-Dichloroethene 1 09/01/23 20:40 V37437MSA
<0.190 µg/L 0.190 0.5001,2-Dichloropropane 1 09/01/23 20:40 V37437MSA
<0.130 µg/L 0.130 0.5001,3-Dichloropropane 1 09/01/23 20:40 V37437MSA
<0.210 µg/L 0.210 2.002,2-Dichloropropane 1 09/01/23 20:40 V37437MSA
<0.200 µg/L 0.200 0.5001,1-Dichloropropene 1 09/01/23 20:40 V37437MSA
<0.210 µg/L 0.210 0.500cis-1,3-Dichloropropene 1 09/01/23 20:40 V37437MSA
<0.150 µg/L 0.150 0.500trans-1,3-Dichloropropene 1 09/01/23 20:40 V37437MSA
<42.0 µg/L 42.0 200Ethanol 1 09/01/23 20:40 V37437MSA
<0.170 µg/L 0.170 0.500Ethylbenzene 1 09/01/23 20:40 V37437MSA
<0.350 µg/L 0.350 3.00Hexachlorobutadiene 1 09/01/23 20:40 V37437MSA
<0.380 µg/L 0.380 1.002-Hexanone 1 09/01/23 20:40 V37437MSA
0.222 J µg/L 0.180 0.500Isopropylbenzene 1 09/01/23 20:40 V37437MSA
<0.089 µg/L 0.089 0.5004-Isopropyl toluene 1 09/01/23 20:40 V37437MSA
<0.710 µg/L 0.710 5.00Methyl Ethyl Ketone (MEK)1 09/01/23 20:40 V37437MSA
<0.140 µg/L 0.140 1.00Methyl tert-butyl ether (MTBE)1 09/01/23 20:40 V37437MSA
<0.078 µg/L 0.078 1.004-Methyl-2-Pentanone 1 09/01/23 20:40 V37437MSA
<0.330 µg/L 0.330 2.00Methylene Chloride 1 09/01/23 20:40 V37437MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 50 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TW-1
93510 Matrix:
8/24/2023 8:15
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37436 09/01/23 09:00
<0.470 µg/L 0.470 1.00Naphthalene 1 09/01/23 20:40 V37437MSA
<0.190 µg/L 0.190 0.500n-Propylbenzene 1 09/01/23 20:40 V37437MSA
<0.220 µg/L 0.220 0.500Styrene 1 09/01/23 20:40 V37437MSA
<1.60 µg/L 1.60 10.0tert-Butyl Alcohol (TBA)1 09/01/23 20:40 V37437MSA
<0.350 µg/L 0.350 10.0tert-Butyl formate (TBF)1 09/01/23 20:40 V37437MSA
<1.90 µg/L 1.90 10.0tert-Amyl Alcohol (TAA)1 09/01/23 20:40 V37437MSA
<0.280 µg/L 0.280 10.0tert-Amyl Methyl Ether (TAME)1 09/01/23 20:40 V37437MSA
<0.160 µg/L 0.160 0.5001,1,1,2-Tetrachloroethane 1 09/01/23 20:40 V37437MSA
<0.160 µg/L 0.160 0.5001,1,2,2-Tetrachloroethane 1 09/01/23 20:40 V37437MSA
<0.220 µg/L 0.220 0.500Tetrachloroethene 1 09/01/23 20:40 V37437MSA
<0.220 µg/L 0.220 0.500Toluene 1 09/01/23 20:40 V37437MSA
<0.380 µg/L 0.380 0.5001,2,3-Trichlorobenzene 1 09/01/23 20:40 V37437MSA
<0.310 µg/L 0.310 0.5001,2,4-Trichlorobenzene 1 09/01/23 20:40 V37437MSA
<0.160 µg/L 0.160 0.5001,1,1-Trichloroethane 1 09/01/23 20:40 V37437MSA
<0.096 µg/L 0.096 0.5001,1,2-Trichloroethane 1 09/01/23 20:40 V37437MSA
<0.180 µg/L 0.180 0.500Trichloroethene 1 09/01/23 20:40 V37437MSA
<0.180 µg/L 0.180 0.500Trichlorofluoromethane 1 09/01/23 20:40 V37437MSA
<0.270 µg/L 0.270 0.5001,2,3-Trichloropropane 1 09/01/23 20:40 V37437MSA
<0.190 µg/L 0.190 0.5001,2,4-Trimethylbenzene 1 09/01/23 20:40 V37437MSA
<0.180 µg/L 0.180 0.5001,3,5-Trimethylbenzene 1 09/01/23 20:40 V37437MSA
<1.00 µg/L 1.00 5.00Vinyl Acetate 1 09/01/23 20:40 V37437MSA
<0.170 µg/L 0.170 0.500Vinyl Chloride 1 09/01/23 20:40 V37437MSA
0.211 J µg/L 0.210 0.500o-Xylene 1 09/01/23 20:40 V37437MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 51 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TW-1
93510 Matrix:
8/24/2023 8:15
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37436 09/01/23 09:00
<0.420 µg/L 0.420 1.00m,p-Xylene 1 09/01/23 20:40 V37437MSA
0.211 J µg/L 0.210 0.500Xylene (Total)1 09/01/23 20:40 V37437
Surrogate: 4-Bromofluorobenzene 94.4 Limits: 70-130%09/01/23 20:401 MSA V37437
Surrogate: Dibromofluoromethane 103 Limits: 70-130%09/01/23 20:401 MSA V37437
Surrogate: 1,2-Dichloroethane - d4 88.4 Limits: 70-130%09/01/23 20:401 MSA V37437
Surrogate: Toluene-d8 98.6 Limits: 70-130%09/01/23 20:401 MSA V37437
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 52 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TB
93511 Matrix:
8/24/2023 7:30
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
<1.80 µg/L 1.80 10.0Acetone 1 09/01/23 04:56 V37379MSA
<0.180 µg/L 0.180 0.500Benzene 1 09/01/23 04:56 V37379MSA
<0.210 µg/L 0.210 0.500Bromobenzene 1 09/01/23 04:56 V37379MSA
<0.420 µg/L 0.420 1.00Bromochloromethane 1 09/01/23 04:56 V37379MSA
<0.160 µg/L 0.160 0.500Bromodichloromethane 1 09/01/23 04:56 V37379MSA
<1.50 µg/L 1.50 5.00Bromoform 1 09/01/23 04:56 V37379MSA
<0.280 µg/L 0.280 1.00Bromomethane 1 09/01/23 04:56 V37379MSA
<0.180 µg/L 0.180 0.500n-Butylbenzene 1 09/01/23 04:56 V37379MSA
<0.200 µg/L 0.200 0.500sec-Butyl benzene 1 09/01/23 04:56 V37379MSA
<0.920 µg/L 0.920 2.00tert-Butyl benzene 1 09/01/23 04:56 V37379MSA
<0.180 µg/L 0.180 0.500Carbon Tetrachloride 1 09/01/23 04:56 V37379MSA
<0.190 µg/L 0.190 0.500Chlorobenzene 1 09/01/23 04:56 V37379MSA
<0.190 µg/L 0.190 0.500Chlorodibromomethane 1 09/01/23 04:56 V37379MSA
<0.430 µg/L 0.430 1.00Chloroethane 1 09/01/23 04:56 V37379MSA
<0.220 µg/L 0.220 0.500Chloroform 1 09/01/23 04:56 V37379MSA
<0.220 µg/L 0.220 0.500Chloromethane 1 09/01/23 04:56 V37379MSA
<0.200 µg/L 0.200 0.5002-Chlorotoluene 1 09/01/23 04:56 V37379MSA
<0.200 µg/L 0.200 0.5004-Chlorotoluene 1 09/01/23 04:56 V37379MSA
<0.500 µg/L 0.500 0.500Di-Isopropyl Ether (DIPE)1 09/01/23 04:56 V37379MSA
<1.10 µg/L 1.10 2.001,2-Dibromo-3-Chloropropane 1 09/01/23 04:56 V37379MSA
<0.200 µg/L 0.200 0.5001,2-Dibromoethane 1 09/01/23 04:56 V37379MSA
<0.230 µg/L 0.230 0.500Dibromomethane 1 09/01/23 04:56 V37379MSA
<0.220 µg/L 0.220 0.5001,2-Dichlorobenzene 1 09/01/23 04:56 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 53 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TB
93511 Matrix:
8/24/2023 7:30
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
<0.190 µg/L 0.190 0.5001,3-Dichlorobenzene 1 09/01/23 04:56 V37379MSA
<0.210 µg/L 0.210 0.5001,4-Dichlorobenzene 1 09/01/23 04:56 V37379MSA
<1.20 µg/L 1.20 5.00Dichlorodifluoromethane 1 09/01/23 04:56 V37379MSA
<0.240 µg/L 0.240 0.5001,1-Dichloroethane 1 09/01/23 04:56 V37379MSA
<0.150 µg/L 0.150 0.5001,2-Dichloroethane 1 09/01/23 04:56 V37379MSA
<0.150 µg/L 0.150 0.5001,1-Dichloroethene 1 09/01/23 04:56 V37379MSA
<0.200 µg/L 0.200 0.500cis-1,2-Dichloroethene 1 09/01/23 04:56 V37379MSA
<0.180 µg/L 0.180 0.500trans-1,2-Dichloroethene 1 09/01/23 04:56 V37379MSA
<0.190 µg/L 0.190 0.5001,2-Dichloropropane 1 09/01/23 04:56 V37379MSA
<0.130 µg/L 0.130 0.5001,3-Dichloropropane 1 09/01/23 04:56 V37379MSA
<0.210 µg/L 0.210 2.002,2-Dichloropropane 1 09/01/23 04:56 V37379MSA
<0.200 µg/L 0.200 0.5001,1-Dichloropropene 1 09/01/23 04:56 V37379MSA
<0.210 µg/L 0.210 0.500cis-1,3-Dichloropropene 1 09/01/23 04:56 V37379MSA
<0.150 µg/L 0.150 0.500trans-1,3-Dichloropropene 1 09/01/23 04:56 V37379MSA
<42.0 µg/L 42.0 200Ethanol 1 09/01/23 04:56 V37379MSA
<0.170 µg/L 0.170 0.500Ethylbenzene 1 09/01/23 04:56 V37379MSA
<0.350 µg/L 0.350 3.00Hexachlorobutadiene 1 09/01/23 04:56 V37379MSA
<0.380 µg/L 0.380 1.002-Hexanone 1 09/01/23 04:56 V37379MSA
<0.180 µg/L 0.180 0.500Isopropylbenzene 1 09/01/23 04:56 V37379MSA
<0.089 µg/L 0.089 0.5004-Isopropyl toluene 1 09/01/23 04:56 V37379MSA
<0.710 µg/L 0.710 5.00Methyl Ethyl Ketone (MEK)1 09/01/23 04:56 V37379MSA
<0.140 µg/L 0.140 1.00Methyl tert-butyl ether (MTBE)1 09/01/23 04:56 V37379MSA
<0.078 µg/L 0.078 1.004-Methyl-2-Pentanone 1 09/01/23 04:56 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 54 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TB
93511 Matrix:
8/24/2023 7:30
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
<0.330 µg/L 0.330 2.00Methylene Chloride 1 09/01/23 04:56 V37379MSA
<0.470 µg/L 0.470 1.00Naphthalene 1 09/01/23 04:56 V37379MSA
<0.190 µg/L 0.190 0.500n-Propylbenzene 1 09/01/23 04:56 V37379MSA
<0.220 µg/L 0.220 0.500Styrene 1 09/01/23 04:56 V37379MSA
<0.160 µg/L 0.160 0.5001,1,1,2-Tetrachloroethane 1 09/01/23 04:56 V37379MSA
<0.160 µg/L 0.160 0.5001,1,2,2-Tetrachloroethane 1 09/01/23 04:56 V37379MSA
<0.220 µg/L 0.220 0.500Tetrachloroethene 1 09/01/23 04:56 V37379MSA
<0.220 µg/L 0.220 0.500Toluene 1 09/01/23 04:56 V37379MSA
<0.380 µg/L 0.380 0.5001,2,3-Trichlorobenzene 1 09/01/23 04:56 V37379MSA
<0.310 µg/L 0.310 0.5001,2,4-Trichlorobenzene 1 09/01/23 04:56 V37379MSA
<0.160 µg/L 0.160 0.5001,1,1-Trichloroethane 1 09/01/23 04:56 V37379MSA
<0.096 µg/L 0.096 0.5001,1,2-Trichloroethane 1 09/01/23 04:56 V37379MSA
<0.180 µg/L 0.180 0.500Trichloroethene 1 09/01/23 04:56 V37379MSA
<0.180 µg/L 0.180 0.500Trichlorofluoromethane 1 09/01/23 04:56 V37379MSA
<0.270 µg/L 0.270 0.5001,2,3-Trichloropropane 1 09/01/23 04:56 V37379MSA
<0.190 µg/L 0.190 0.5001,2,4-Trimethylbenzene 1 09/01/23 04:56 V37379MSA
<0.180 µg/L 0.180 0.5001,3,5-Trimethylbenzene 1 09/01/23 04:56 V37379MSA
<1.00 µg/L 1.00 5.00Vinyl Acetate 1 09/01/23 04:56 V37379MSA
<0.170 µg/L 0.170 0.500Vinyl Chloride 1 09/01/23 04:56 V37379MSA
<0.210 µg/L 0.210 0.500o-Xylene 1 09/01/23 04:56 V37379MSA
<0.420 µg/L 0.420 1.00m,p-Xylene 1 09/01/23 04:56 V37379MSA
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 55 of 74
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28110
23-240-0002
00087
Geological Resources, Inc.
3502 Hayes Road
Sam McKay
Monroe
Danyale Love
Project Manager
GRI #5721 Received : 08/25/2023
Rushco 4 (Former)
Report Date : 09/08/2023
Sample ID :
Lab No :
Sampled:TB
93511 Matrix:
8/24/2023 7:30
Aqueous
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
6200 PT
6200B Prep Batch(es):V37378 08/31/23 14:00
<0.21 µg/L 0.210 0.500Xylene (Total)1 09/01/23 04:56 V37379
Surrogate: 4-Bromofluorobenzene 95.4 Limits: 70-130%09/01/23 04:561 MSA V37379
Surrogate: Dibromofluoromethane 102 Limits: 70-130%09/01/23 04:561 MSA V37379
Surrogate: 1,2-Dichloroethane - d4 89.2 Limits: 70-130%09/01/23 04:561 MSA V37379
Surrogate: Toluene-d8 100 Limits: 70-130%09/01/23 04:561 MSA V37379
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 56 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Metals Analysis
6010D
V37225QC Analytical Batch(es):
Analysis Method:
Analysis Description:
3005A
QC Prep:V37177
Associated Lab Samples: 93507, 93508, 93509
LRB-V37177 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
08/29/23 22:050.0060.002<0.002mg/LLead
LCS-V37177Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
1030.1030.100mg/LLead 80-120
V 93426-MS-V37177 V 93426-MSD-V37177Matrix Spike & Matrix Spike Duplicate
MS Result
Parameter
Max
RPD
MS
%Rec
MSD
Result
MSD
Spike
Conc.
MS Spike
Conc.ResultUnits
%Rec
Limits
MSD
%Rec RPD
0.110 1100.1080.1000.100< 0.002mg/LLead 108 75-125 1.8 20.0
V 93426-PDS-V37177Post Digestion Spike
Parameter
Analyzed%
Recovery
PDS
ResultUnits
08/29/23 23:001040.259mg/LLead
Page 1 of 16Date:09/08/2023 12:12 PM
Page 57 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37379QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37378
Associated Lab Samples: 93503, 93504, 93505, 93506, 93507, 93508, 93511
LRB-V37378 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
09/01/23 04:3110.01.80<1.80µg/LAcetone
09/01/23 04:310.5000.180<0.180µg/LBenzene
09/01/23 04:310.5000.210<0.210µg/LBromobenzene
09/01/23 04:311.000.420<0.420µg/LBromochloromethane
09/01/23 04:310.5000.160<0.160µg/LBromodichloromethane
09/01/23 04:315.001.50<1.50µg/LBromoform
09/01/23 04:311.000.280<0.280µg/LBromomethane
09/01/23 04:310.5000.180<0.180µg/Ln-Butylbenzene
09/01/23 04:310.5000.200<0.200µg/Lsec-Butyl benzene
09/01/23 04:312.000.920<0.920µg/Ltert-Butyl benzene
09/01/23 04:310.5000.180<0.180µg/LCarbon Tetrachloride
09/01/23 04:310.5000.190<0.190µg/LChlorobenzene
09/01/23 04:310.5000.190<0.190µg/LChlorodibromomethane
09/01/23 04:311.000.430<0.430µg/LChloroethane
09/01/23 04:310.5000.220<0.220µg/LChloroform
09/01/23 04:310.5000.220<0.220µg/LChloromethane
09/01/23 04:310.5000.200<0.200µg/L2-Chlorotoluene
09/01/23 04:310.5000.200<0.200µg/L4-Chlorotoluene
09/01/23 04:310.5000.500<0.500µg/LDi-Isopropyl Ether (DIPE)
09/01/23 04:312.001.10<1.10µg/L1,2-Dibromo-3-Chloropropane
09/01/23 04:310.5000.200<0.200µg/L1,2-Dibromoethane
09/01/23 04:310.5000.230<0.230µg/LDibromomethane
09/01/23 04:310.5000.220<0.220µg/L1,2-Dichlorobenzene
09/01/23 04:310.5000.190<0.190µg/L1,3-Dichlorobenzene
09/01/23 04:310.5000.210<0.210µg/L1,4-Dichlorobenzene
09/01/23 04:315.001.20<1.20µg/LDichlorodifluoromethane
09/01/23 04:310.5000.240<0.240µg/L1,1-Dichloroethane
Page 2 of 16Date:09/08/2023 12:12 PM
Page 58 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37379QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37378
Associated Lab Samples: 93503, 93504, 93505, 93506, 93507, 93508, 93511
LRB-V37378 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
09/01/23 04:310.5000.150<0.150µg/L1,2-Dichloroethane
09/01/23 04:310.5000.150<0.150µg/L1,1-Dichloroethene
09/01/23 04:310.5000.200<0.200µg/Lcis-1,2-Dichloroethene
09/01/23 04:310.5000.180<0.180µg/Ltrans-1,2-Dichloroethene
09/01/23 04:310.5000.190<0.190µg/L1,2-Dichloropropane
09/01/23 04:310.5000.130<0.130µg/L1,3-Dichloropropane
09/01/23 04:312.000.210<0.210µg/L2,2-Dichloropropane
09/01/23 04:310.5000.200<0.200µg/L1,1-Dichloropropene
09/01/23 04:310.5000.210<0.210µg/Lcis-1,3-Dichloropropene
09/01/23 04:310.5000.150<0.150µg/Ltrans-1,3-Dichloropropene
09/01/23 04:3120042.0<42.0µg/LEthanol
09/01/23 04:310.5000.170<0.170µg/LEthylbenzene
09/01/23 04:313.000.350<0.350µg/LHexachlorobutadiene
09/01/23 04:311.000.380<0.380µg/L2-Hexanone
09/01/23 04:310.5000.180<0.180µg/LIsopropylbenzene
09/01/23 04:310.5000.089<0.089µg/L4-Isopropyl toluene
09/01/23 04:315.000.710<0.710µg/LMethyl Ethyl Ketone (MEK)
09/01/23 04:311.000.140<0.140µg/LMethyl tert-butyl ether (MTBE)
09/01/23 04:311.000.078<0.078µg/L4-Methyl-2-Pentanone
09/01/23 04:312.000.330<0.330µg/LMethylene Chloride
09/01/23 04:311.000.470<0.470µg/LNaphthalene
09/01/23 04:310.5000.190<0.190µg/Ln-Propylbenzene
09/01/23 04:310.5000.220<0.220µg/LStyrene
09/01/23 04:3110.01.60<1.60µg/Ltert-Butyl Alcohol (TBA)
09/01/23 04:3110.00.350<0.350µg/Ltert-Butyl formate (TBF)
09/01/23 04:3110.01.90<1.90µg/Ltert-Amyl Alcohol (TAA)
09/01/23 04:3110.00.280<0.280µg/Ltert-Amyl Methyl Ether (TAME)
Page 3 of 16Date:09/08/2023 12:12 PM
Page 59 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37379QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37378
Associated Lab Samples: 93503, 93504, 93505, 93506, 93507, 93508, 93511
LRB-V37378 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
09/01/23 04:310.5000.160<0.160µg/L1,1,1,2-Tetrachloroethane
09/01/23 04:310.5000.160<0.160µg/L1,1,2,2-Tetrachloroethane
09/01/23 04:310.5000.220<0.220µg/LTetrachloroethene
09/01/23 04:310.5000.220<0.220µg/LToluene
09/01/23 04:310.5000.380<0.380µg/L1,2,3-Trichlorobenzene
09/01/23 04:310.5000.310<0.310µg/L1,2,4-Trichlorobenzene
09/01/23 04:310.5000.160<0.160µg/L1,1,1-Trichloroethane
09/01/23 04:310.5000.096<0.096µg/L1,1,2-Trichloroethane
09/01/23 04:310.5000.180<0.180µg/LTrichloroethene
09/01/23 04:310.5000.180<0.180µg/LTrichlorofluoromethane
09/01/23 04:310.5000.270<0.270µg/L1,2,3-Trichloropropane
09/01/23 04:310.5000.190<0.190µg/L1,2,4-Trimethylbenzene
09/01/23 04:310.5000.180<0.180µg/L1,3,5-Trimethylbenzene
09/01/23 04:315.001.00<1.00µg/LVinyl Acetate
09/01/23 04:310.5000.170<0.170µg/LVinyl Chloride
09/01/23 04:310.5000.210<0.210µg/Lo-Xylene
09/01/23 04:311.000.420<0.420µg/Lm,p-Xylene
09/01/23 04:3110.01.00<1.00µg/L3,3-Dimethyl-1-butanol
09/01/23 04:314-Bromofluorobenzene (S)94.8 70-130
09/01/23 04:31Dibromofluoromethane (S)102 70-130
09/01/23 04:311,2-Dichloroethane - d4 (S)88.8 70-130
09/01/23 04:31Toluene-d8 (S)99.2 70-130
Page 4 of 16Date:09/08/2023 12:12 PM
Page 60 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37379QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37378
LCS-V37378 LCSD-V37378Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
32.3 80.783.033.240.0µg/LAcetone 40-160 2.7 20.0
19.3 96.510020.020.0µg/LBenzene 70-130 3.5 20.0
18.2 91.095.019.020.0µg/LBromobenzene 70-130 4.3 20.0
21.0 10510420.720.0µg/LBromochloromethane 70-130 1.4 20.0
17.9 89.590.018.020.0µg/LBromodichloromethane 70-130 0.5 20.0
17.1 85.590.018.020.0µg/LBromoform 70-130 5.1 20.0
20.1 10199.019.820.0µg/LBromomethane 60-140 1.5 20.0
18.7 93.596.519.320.0µg/Ln-Butylbenzene 70-130 3.1 20.0
18.3 91.598.519.720.0µg/Lsec-Butyl benzene 70-130 7.3 20.0
18.0 90.093.518.720.0µg/Ltert-Butyl benzene 70-130 3.8 20.0
18.4 92.097.519.520.0µg/LCarbon Tetrachloride 70-130 5.8 20.0
18.9 94.510020.020.0µg/LChlorobenzene 70-130 5.6 20.0
18.8 94.097.019.420.0µg/LChlorodibromomethane 70-130 3.1 20.0
19.7 98.510120.220.0µg/LChloroethane 60-140 2.5 20.0
19.0 95.099.519.920.0µg/LChloroform 70-130 4.6 20.0
16.9 84.589.517.920.0µg/LChloromethane 60-140 5.7 20.0
17.6 88.091.518.320.0µg/L2-Chlorotoluene 70-130 3.8 20.0
17.8 89.091.518.320.0µg/L4-Chlorotoluene 70-130 2.7 20.0
18.8 94.098.519.720.0µg/LDi-Isopropyl Ether (DIPE)70-130 4.6 20.0
19.1 95.595.519.120.0µg/L1,2-Dibromo-3-Chloropropane 70-130 0.0 20.0
19.0 95.099.019.820.0µg/L1,2-Dibromoethane 70-130 4.1 20.0
17.7 88.589.017.820.0µg/LDibromomethane 70-130 0.5 20.0
18.8 94.096.019.220.0µg/L1,2-Dichlorobenzene 70-130 2.1 20.0
18.7 93.598.519.720.0µg/L1,3-Dichlorobenzene 70-130 5.2 20.0
18.5 92.594.018.820.0µg/L1,4-Dichlorobenzene 70-130 1.6 20.0
15.9 79.585.517.120.0µg/LDichlorodifluoromethane 60-140 7.2 20.0
Page 5 of 16Date:09/08/2023 12:12 PM
Page 61 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37379QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37378
LCS-V37378 LCSD-V37378Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
18.9 94.598.019.620.0µg/L1,1-Dichloroethane 70-130 3.6 20.0
15.9 79.582.516.520.0µg/L1,2-Dichloroethane 70-130 3.7 20.0
20.0 10098.519.720.0µg/L1,1-Dichloroethene 70-130 1.5 20.0
18.4 92.096.019.220.0µg/Lcis-1,2-Dichloroethene 70-130 4.2 20.0
18.1 90.593.518.720.0µg/Ltrans-1,2-Dichloroethene 70-130 3.2 20.0
19.2 96.098.019.620.0µg/L1,2-Dichloropropane 70-130 2.0 20.0
18.4 92.097.019.420.0µg/L1,3-Dichloropropane 70-130 5.2 20.0
16.8 84.085.017.020.0µg/L2,2-Dichloropropane 70-130 1.1 20.0
20.3 10210821.520.0µg/L1,1-Dichloropropene 70-130 5.7 20.0
17.4 87.089.017.820.0µg/Lcis-1,3-Dichloropropene 70-130 2.2 20.0
17.2 86.087.517.520.0µg/Ltrans-1,3-Dichloropropene 70-130 1.7 20.0
490 98.094.2471500µg/LEthanol 60-140 3.9 20.0
17.6 88.091.518.320.0µg/LEthylbenzene 70-130 3.8 20.0
17.9 89.593.018.620.0µg/LHexachlorobutadiene 70-130 3.8 20.0
17.2 86.084.516.920.0µg/L2-Hexanone 60-140 1.7 20.0
18.5 92.597.019.420.0µg/LIsopropylbenzene 70-130 4.7 20.0
18.4 92.098.019.620.0µg/L4-Isopropyl toluene 70-130 6.3 20.0
19.1 95.584.516.920.0µg/LMethyl Ethyl Ketone (MEK)60-140 12.2 20.0
19.0 95.096.019.220.0µg/LMethyl tert-butyl ether (MTBE)70-130 1.0 20.0
16.6 83.081.016.220.0µg/L4-Methyl-2-Pentanone 60-140 2.4 20.0
19.0 95.096.519.320.0µg/LMethylene Chloride 70-130 1.5 20.0
17.0 85.087.017.420.0µg/LNaphthalene 70-130 2.3 20.0
17.7 88.592.518.520.0µg/Ln-Propylbenzene 70-130 4.4 20.0
19.7 98.510120.120.0µg/LStyrene 70-130 2.0 20.0
48.8 12212550.140.0µg/Ltert-Butyl Alcohol (TBA)40-140 2.6 20.0
28.4 71.072.729.140.0µg/Ltert-Butyl formate (TBF)40-140 2.4 20.0
Page 6 of 16Date:09/08/2023 12:12 PM
Page 62 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37379QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37378
LCS-V37378 LCSD-V37378Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
15.2 76.093.518.720.0µg/Ltert-Amyl Alcohol (TAA)40-140 20.6*20.0
37.7 94.296.538.640.0µg/Ltert-Amyl Methyl Ether (TAME)40-140 2.3 20.0
19.6 98.010220.420.0µg/L1,1,1,2-Tetrachloroethane 70-130 4.0 20.0
18.0 90.093.518.720.0µg/L1,1,2,2-Tetrachloroethane 70-130 3.8 20.0
18.3 91.597.019.420.0µg/LTetrachloroethene 70-130 5.8 20.0
18.0 90.095.519.120.0µg/LToluene 70-130 5.9 20.0
17.4 87.086.517.320.0µg/L1,2,3-Trichlorobenzene 70-130 0.5 20.0
17.5 87.589.017.820.0µg/L1,2,4-Trichlorobenzene 70-130 1.6 20.0
18.7 93.597.519.520.0µg/L1,1,1-Trichloroethane 70-130 4.1 20.0
19.3 96.597.019.420.0µg/L1,1,2-Trichloroethane 70-130 0.5 20.0
20.1 10110320.520.0µg/LTrichloroethene 70-130 1.9 20.0
20.1 10110020.020.0µg/LTrichlorofluoromethane 60-140 0.4 20.0
16.8 84.093.518.720.0µg/L1,2,3-Trichloropropane 70-130 10.7 20.0
18.7 93.596.019.220.0µg/L1,2,4-Trimethylbenzene 70-130 2.6 20.0
18.0 90.093.018.620.0µg/L1,3,5-Trimethylbenzene 70-130 3.2 20.0
13.8 69.071.514.320.0µg/LVinyl Acetate 60-140 3.5 20.0
19.6 98.010520.920.0µg/LVinyl Chloride 60-140 6.4 20.0
18.5 92.597.019.420.0µg/Lo-Xylene 70-130 4.7 20.0
36.8 92.097.038.840.0µg/Lm,p-Xylene 70-130 5.2 20.0
20.6 10373.014.620.0µg/L3,3-Dimethyl-1-butanol 70-130 34.0*20.0
91.291.64-Bromofluorobenzene (S)70-130
10099.8Dibromofluoromethane (S)70-130
89.491.21,2-Dichloroethane - d4 (S)70-130
99.8100Toluene-d8 (S)70-130
Page 7 of 16* QC Fail Date:09/08/2023 12:12 PM
Page 63 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37437QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37436
Associated Lab Samples: 93503, 93505, 93506, 93508, 93509, 93510
LRB-V37436 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
09/01/23 18:3210.01.80<1.80µg/LAcetone
09/01/23 18:320.5000.180<0.180µg/LBenzene
09/01/23 18:320.5000.210<0.210µg/LBromobenzene
09/01/23 18:321.000.420<0.420µg/LBromochloromethane
09/01/23 18:320.5000.160<0.160µg/LBromodichloromethane
09/01/23 18:325.001.50<1.50µg/LBromoform
09/01/23 18:321.000.280<0.280µg/LBromomethane
09/01/23 18:320.5000.180<0.180µg/Ln-Butylbenzene
09/01/23 18:320.5000.200<0.200µg/Lsec-Butyl benzene
09/01/23 18:322.000.920<0.920µg/Ltert-Butyl benzene
09/01/23 18:320.5000.180<0.180µg/LCarbon Tetrachloride
09/01/23 18:320.5000.190<0.190µg/LChlorobenzene
09/01/23 18:320.5000.190<0.190µg/LChlorodibromomethane
09/01/23 18:321.000.430<0.430µg/LChloroethane
09/01/23 18:320.5000.220<0.220µg/LChloroform
09/01/23 18:320.5000.220<0.220µg/LChloromethane
09/01/23 18:320.5000.200<0.200µg/L2-Chlorotoluene
09/01/23 18:320.5000.200<0.200µg/L4-Chlorotoluene
09/01/23 18:320.5000.500<0.500µg/LDi-Isopropyl Ether (DIPE)
09/01/23 18:322.001.10<1.10µg/L1,2-Dibromo-3-Chloropropane
09/01/23 18:320.5000.230<0.230µg/LDibromomethane
09/01/23 18:320.5000.220<0.220µg/L1,2-Dichlorobenzene
09/01/23 18:320.5000.190<0.190µg/L1,3-Dichlorobenzene
09/01/23 18:320.5000.210<0.210µg/L1,4-Dichlorobenzene
09/01/23 18:325.001.20<1.20µg/LDichlorodifluoromethane
09/01/23 18:320.5000.240<0.240µg/L1,1-Dichloroethane
09/01/23 18:320.5000.150<0.150µg/L1,2-Dichloroethane
Page 8 of 16Date:09/08/2023 12:12 PM
Page 64 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37437QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37436
Associated Lab Samples: 93503, 93505, 93506, 93508, 93509, 93510
LRB-V37436 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
09/01/23 18:320.5000.150<0.150µg/L1,1-Dichloroethene
09/01/23 18:320.5000.200<0.200µg/Lcis-1,2-Dichloroethene
09/01/23 18:320.5000.180<0.180µg/Ltrans-1,2-Dichloroethene
09/01/23 18:320.5000.190<0.190µg/L1,2-Dichloropropane
09/01/23 18:320.5000.130<0.130µg/L1,3-Dichloropropane
09/01/23 18:322.000.210<0.210µg/L2,2-Dichloropropane
09/01/23 18:320.5000.200<0.200µg/L1,1-Dichloropropene
09/01/23 18:320.5000.210<0.210µg/Lcis-1,3-Dichloropropene
09/01/23 18:320.5000.150<0.150µg/Ltrans-1,3-Dichloropropene
09/01/23 18:3220042.0<42.0µg/LEthanol
09/01/23 18:320.5000.170<0.170µg/LEthylbenzene
09/01/23 18:323.000.350<0.350µg/LHexachlorobutadiene
09/01/23 18:321.000.380<0.380µg/L2-Hexanone
09/01/23 18:320.5000.180<0.180µg/LIsopropylbenzene
09/01/23 18:320.5000.089<0.089µg/L4-Isopropyl toluene
09/01/23 18:325.000.710<0.710µg/LMethyl Ethyl Ketone (MEK)
09/01/23 18:321.000.140<0.140µg/LMethyl tert-butyl ether (MTBE)
09/01/23 18:321.000.078<0.078µg/L4-Methyl-2-Pentanone
09/01/23 18:322.000.330<0.330µg/LMethylene Chloride
09/01/23 18:321.000.470<0.470µg/LNaphthalene
09/01/23 18:320.5000.190<0.190µg/Ln-Propylbenzene
09/01/23 18:320.5000.220<0.220µg/LStyrene
09/01/23 18:3210.01.60<1.60µg/Ltert-Butyl Alcohol (TBA)
09/01/23 18:3210.00.350<0.350µg/Ltert-Butyl formate (TBF)
09/01/23 18:3210.01.90<1.90µg/Ltert-Amyl Alcohol (TAA)
09/01/23 18:3210.00.280<0.280µg/Ltert-Amyl Methyl Ether (TAME)
09/01/23 18:320.5000.160<0.160µg/L1,1,1,2-Tetrachloroethane
Page 9 of 16Date:09/08/2023 12:12 PM
Page 65 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37437QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37436
Associated Lab Samples: 93503, 93505, 93506, 93508, 93509, 93510
LRB-V37436 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
09/01/23 18:320.5000.160<0.160µg/L1,1,2,2-Tetrachloroethane
09/01/23 18:320.5000.220<0.220µg/LTetrachloroethene
09/01/23 18:320.5000.220<0.220µg/LToluene
09/01/23 18:320.5000.380<0.380µg/L1,2,3-Trichlorobenzene
09/01/23 18:320.5000.310<0.310µg/L1,2,4-Trichlorobenzene
09/01/23 18:320.5000.160<0.160µg/L1,1,1-Trichloroethane
09/01/23 18:320.5000.096<0.096µg/L1,1,2-Trichloroethane
09/01/23 18:320.5000.180<0.180µg/LTrichloroethene
09/01/23 18:320.5000.180<0.180µg/LTrichlorofluoromethane
09/01/23 18:320.5000.270<0.270µg/L1,2,3-Trichloropropane
09/01/23 18:320.5000.190<0.190µg/L1,2,4-Trimethylbenzene
09/01/23 18:320.5000.180<0.180µg/L1,3,5-Trimethylbenzene
09/01/23 18:325.001.00<1.00µg/LVinyl Acetate
09/01/23 18:320.5000.170<0.170µg/LVinyl Chloride
09/01/23 18:320.5000.210<0.210µg/Lo-Xylene
09/01/23 18:321.000.420<0.420µg/Lm,p-Xylene
09/01/23 18:3210.01.00<1.00µg/L3,3-Dimethyl-1-butanol
09/01/23 18:324-Bromofluorobenzene (S)94.8 70-130
09/01/23 18:32Dibromofluoromethane (S)100 70-130
09/01/23 18:321,2-Dichloroethane - d4 (S)88.4 70-130
09/01/23 18:32Toluene-d8 (S)99.2 70-130
LCS-V37436 LCSD-V37436Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
32.4 81.088.535.440.0µg/LAcetone 40-160 8.8 20.0
Page 10 of 16Date:09/08/2023 12:12 PM
Page 66 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37437QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37436
LCS-V37436 LCSD-V37436Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
20.3 10210721.320.0µg/LBenzene 70-130 4.8 20.0
18.4 92.098.019.620.0µg/LBromobenzene 70-130 6.3 20.0
20.5 10311322.620.0µg/LBromochloromethane 70-130 9.7 20.0
18.4 92.098.019.620.0µg/LBromodichloromethane 70-130 6.3 20.0
17.5 87.592.018.420.0µg/LBromoform 70-130 5.0 20.0
21.4 10711222.420.0µg/LBromomethane 60-140 4.5 20.0
19.3 96.510521.020.0µg/Ln-Butylbenzene 70-130 8.4 20.0
19.0 95.010120.220.0µg/Lsec-Butyl benzene 70-130 6.1 20.0
18.8 94.099.519.920.0µg/Ltert-Butyl benzene 70-130 5.6 20.0
19.2 96.010320.520.0µg/LCarbon Tetrachloride 70-130 6.5 20.0
19.8 99.010520.920.0µg/LChlorobenzene 70-130 5.4 20.0
20.1 10198.019.620.0µg/LChlorodibromomethane 70-130 2.5 20.0
18.9 94.596.019.220.0µg/LChloroethane 60-140 1.5 20.0
19.3 96.510721.420.0µg/LChloroform 70-130 10.3 20.0
16.9 84.589.017.820.0µg/LChloromethane 60-140 5.1 20.0
18.7 93.598.019.620.0µg/L2-Chlorotoluene 70-130 4.6 20.0
18.6 93.096.519.320.0µg/L4-Chlorotoluene 70-130 3.6 20.0
19.8 99.010621.120.0µg/LDi-Isopropyl Ether (DIPE)70-130 6.3 20.0
18.8 94.097.019.420.0µg/L1,2-Dibromo-3-Chloropropane 70-130 3.1 20.0
17.6 88.094.018.820.0µg/LDibromomethane 70-130 6.5 20.0
19.3 96.510621.120.0µg/L1,2-Dichlorobenzene 70-130 8.9 20.0
20.1 10110521.020.0µg/L1,3-Dichlorobenzene 70-130 4.3 20.0
19.5 97.510220.420.0µg/L1,4-Dichlorobenzene 70-130 4.5 20.0
15.8 79.084.516.920.0µg/LDichlorodifluoromethane 60-140 6.7 20.0
19.4 97.010320.520.0µg/L1,1-Dichloroethane 70-130 5.5 20.0
16.9 84.587.017.420.0µg/L1,2-Dichloroethane 70-130 2.9 20.0
Page 11 of 16Date:09/08/2023 12:12 PM
Page 67 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37437QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37436
LCS-V37436 LCSD-V37436Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
19.0 95.010220.420.0µg/L1,1-Dichloroethene 70-130 7.1 20.0
19.1 95.510120.220.0µg/Lcis-1,2-Dichloroethene 70-130 5.5 20.0
18.7 93.510120.220.0µg/Ltrans-1,2-Dichloroethene 70-130 7.7 20.0
19.9 99.510521.020.0µg/L1,2-Dichloropropane 70-130 5.3 20.0
19.4 97.010220.320.0µg/L1,3-Dichloropropane 70-130 4.5 20.0
19.7 98.510420.720.0µg/L2,2-Dichloropropane 70-130 4.9 20.0
21.1 10611222.420.0µg/L1,1-Dichloropropene 70-130 5.9 20.0
18.9 94.598.519.720.0µg/Lcis-1,3-Dichloropropene 70-130 4.1 20.0
18.1 90.596.019.220.0µg/Ltrans-1,3-Dichloropropene 70-130 5.8 20.0
477 95.485.2426500µg/LEthanol 60-140 11.2 20.0
18.9 94.597.019.420.0µg/LEthylbenzene 70-130 2.6 20.0
18.7 93.510220.420.0µg/LHexachlorobutadiene 70-130 8.6 20.0
18.3 91.594.518.920.0µg/L2-Hexanone 60-140 3.2 20.0
19.4 97.010320.620.0µg/LIsopropylbenzene 70-130 6.0 20.0
19.6 98.010521.020.0µg/L4-Isopropyl toluene 70-130 6.8 20.0
18.2 91.083.016.620.0µg/LMethyl Ethyl Ketone (MEK)60-140 9.1 20.0
20.1 10110521.020.0µg/LMethyl tert-butyl ether (MTBE)70-130 4.3 20.0
17.2 86.094.018.820.0µg/L4-Methyl-2-Pentanone 60-140 8.8 20.0
19.0 95.098.019.620.0µg/LMethylene Chloride 70-130 3.1 20.0
17.5 87.590.018.020.0µg/LNaphthalene 70-130 2.8 20.0
18.8 94.099.519.920.0µg/Ln-Propylbenzene 70-130 5.6 20.0
20.5 10310821.520.0µg/LStyrene 70-130 4.7 20.0
54.7 13713152.340.0µg/Ltert-Butyl Alcohol (TBA)40-140 4.4 20.0
40.0 10010541.940.0µg/Ltert-Butyl formate (TBF)40-140 4.6 20.0
21.7 10971.514.320.0µg/Ltert-Amyl Alcohol (TAA)40-140 41.1*20.0
40.2 10110642.340.0µg/Ltert-Amyl Methyl Ether (TAME)40-140 5.0 20.0
Page 12 of 16* QC Fail Date:09/08/2023 12:12 PM
Page 68 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37437QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37436
LCS-V37436 LCSD-V37436Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
20.6 10310420.820.0µg/L1,1,1,2-Tetrachloroethane 70-130 0.9 20.0
19.9 99.510520.920.0µg/L1,1,2,2-Tetrachloroethane 70-130 4.9 20.0
19.8 99.010320.520.0µg/LTetrachloroethene 70-130 3.4 20.0
18.7 93.510120.220.0µg/LToluene 70-130 7.7 20.0
17.5 87.595.519.120.0µg/L1,2,3-Trichlorobenzene 70-130 8.7 20.0
18.3 91.597.019.420.0µg/L1,2,4-Trichlorobenzene 70-130 5.8 20.0
19.1 95.510420.720.0µg/L1,1,1-Trichloroethane 70-130 8.0 20.0
19.4 97.010220.420.0µg/L1,1,2-Trichloroethane 70-130 5.0 20.0
19.7 98.510420.820.0µg/LTrichloroethene 70-130 5.4 20.0
19.6 98.010721.420.0µg/LTrichlorofluoromethane 60-140 8.7 20.0
18.6 93.097.519.520.0µg/L1,2,3-Trichloropropane 70-130 4.7 20.0
19.4 97.010220.420.0µg/L1,2,4-Trimethylbenzene 70-130 5.0 20.0
19.2 96.010120.220.0µg/L1,3,5-Trimethylbenzene 70-130 5.0 20.0
19.0 95.010220.320.0µg/LVinyl Acetate 60-140 6.6 20.0
19.7 98.510420.720.0µg/LVinyl Chloride 60-140 4.9 20.0
19.4 97.099.019.820.0µg/Lo-Xylene 70-130 2.0 20.0
38.6 96.510240.840.0µg/Lm,p-Xylene 70-130 5.5 20.0
14.5 72.576.515.320.0µg/L3,3-Dimethyl-1-butanol 70-130 5.3 20.0
91.292.04-Bromofluorobenzene (S)70-130
99.0102Dibromofluoromethane (S)70-130
89.891.01,2-Dichloroethane - d4 (S)70-130
10098.6Toluene-d8 (S)70-130
Page 13 of 16Date:09/08/2023 12:12 PM
Page 69 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Volatile Organic Compounds - GC/MS
6200B
V37553QC Analytical Batch(es):
Analysis Method:
Analysis Description:
6200 PT
QC Prep:V37551
Associated Lab Samples: 93505
LRB-V37551 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
09/06/23 16:030.5000.220<0.220µg/LToluene
09/06/23 16:034-Bromofluorobenzene (S)97.4 70-130
09/06/23 16:03Dibromofluoromethane (S)103 70-130
09/06/23 16:031,2-Dichloroethane - d4 (S)92.4 70-130
09/06/23 16:03Toluene-d8 (S)101 70-130
LCS-V37551 LCSD-V37551Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
19.5 97.596.519.320.0µg/LToluene 70-130 1.0 20.0
92.093.84-Bromofluorobenzene (S)70-130
103102Dibromofluoromethane (S)70-130
91.090.81,2-Dichloroethane - d4 (S)70-130
10099.8Toluene-d8 (S)70-130
Page 14 of 16Date:09/08/2023 12:12 PM
Page 70 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
EDB and DBCP by Microextraction GC/ECD
EPA-504.1
V37326QC Analytical Batch(es):
Analysis Method:
Analysis Description:
EPA-504.1(PREP)
QC Prep:V37272
Associated Lab Samples: 93507, 93508, 93509
LRB-V37272 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLBlank
ResultUnits
08/31/23 10:360.0200< 0.0200µg/L1,2-Dibromoethane
LCS-V37272 LCSD-V37272Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
0.276 11099.60.2490.250µg/L1,2-Dibromoethane 70-130 10.2 20.0
V 93508-DUP-V37272Duplicate
Max RPD
Parameter
AnalyzedRPDDUP
Result
Result
Units
20.0 08/31/23 14:000.0< 0.0207< 0.0207µg/L1,2-Dibromoethane
V 93507-MS-V37272Matrix Spike
MS Result
Parameter
Max
RPD
MS
%Rec
MSD
Result
MSD
Spike
Conc.
MS Spike
Conc.ResultUnits
%Rec
Limits
0.254 97.60.260< 0.0208µg/L1,2-Dibromoethane 70-130
Page 15 of 16Date:09/08/2023 12:12 PM
Page 71 of 74
Quality Control Data
23-240-0002Report No:
Project Description:
Client ID:Geological Resources, Inc.
Rushco 4 (Former)
QC Prep Batch Method:
Massachusetts VPH
MADEP-VPH
V37165QC Analytical Batch(es):
Analysis Method:
Analysis Description:
MAVPH (Prep)
QC Prep:V37164
Associated Lab Samples: 93507, 93508, 93509
LRB-V37164 Matrix: AQULab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
08/28/23 18:0650.011.5<11.5µg/LAliphatic C5-C8
08/28/23 18:0650.025.8<25.8µg/LAliphatic C9-C12
08/28/23 18:0650.04.02<4.02µg/LAromatic C9-C10
08/28/23 18:062,5-Dibromotoluene (FID) (S)86.4 70-130
08/28/23 18:062,5-Dibromotoluene (PID) (S)87.5 70-130
LCS-V37164 LCSD-V37164Laboratory Control Sample & LCSD
LCSD
ResultParameter Max
RPD
LCSD
% Rec
LCS
%Rec
LCS
Result
Spike
Conc.Units
% Rec
Limits RPD
298 99.399.3298300µg/LAliphatic C5-C8 70-130 0.0 50.0
339 113113338300µg/LAliphatic C9-C12 70-130 0.2 50.0
110 110111111100µg/LAromatic C9-C10 70-130 0.9 50.0
1091012,5-Dibromotoluene (FID) (S)70-130
97.393.02,5-Dibromotoluene (PID) (S)70-130
Page 16 of 16Date:09/08/2023 12:12 PM
Page 72 of 74
Fed Ex
UPS
US Postal
Client
Lab
Courier
Other :
Shipment Receipt Form
Customer Number:
Customer Name:
Report Number:23-240-0002
Geological Resources, Inc.
00087
Shipping Method
Shipping container/cooler uncompromised?
Thermometer ID:IRT15 0.4C
Chain of Custody (COC) present?Yes No
Yes No Not Present
Yes No Not Present
Yes No
COC agrees with sample label(s)? Yes No
COC properly completed
Samples in proper containers?
Sample containers intact?
Sufficient sample volume for indicated test(s)?
All samples received within holding time?
Cooler temperature in compliance?
Yes No
Yes No
Yes No
Yes No
Yes No
Yes NoCooler/Samples arrived at the laboratory on ice.
Samples were considered acceptable as cooling
process had begun.
Yes No
Yes No N/A
Yes No N/A
Yes No N/ASoil VOA method 5035 – compliance criteria met
Water - Sample containers properly preserved
Water - VOA vials free of headspace Yes No N/A
Trip Blanks received with VOAs
Low concentration EnCore samplers (48 hr)
High concentration pre-weighed (methanol -14 d) Low conc pre-weighed vials (Sod Bis -14 d)
High concentration container (48 hr)
Custody seals intact on shipping container/cooler?
Custody seals intact on sample bottles?
Number of coolers/boxes received
Yes No
1
TW-1 is for 6200 + Oxys only.
Signature:Angelo Norvell Date & Time:08/28/2023 09:28:41
Special precautions or instructions included?
Comments:
Page 73 of 74
Pa
g
e
7
4
o
f
7
4
Appendix F
Contaminant Mass Calculations
Area ID Well ID Area
(ft²)
Average Well
Depth
(ft.)
Average
Depth to
Water
(ft.)
Water Column
Height
(ft)
Volume
(ft³)
Volume
(L)
Effective
Porosity
Effective
Volume
(L)
MW-1
MW-4
MW-3
MW-6
MW-2
MW-5
Area Date Well Benzene
(μ/L)
Toluene
(μ/L)
Ethylbenzene
(μ/L)
Xylenes
(μ/L)
MTBE
(μ/L)
Naphthalene
(μ/L)
Total
(μ/L)
DTW
(ft.)
Average Water
Column Height
(ft.)
Total Average
Mass
(g)
Percent Red.To Date Red.
MW-1 13000.00 30800.00 3220.00 16500.00 11300.00 1150.00 75970.00 22.98
MW-4 22100.00 46900.00 3180.00 18600.00 15400.00 892.00 107072.00 22.59
Avg.17550.00 38850.00 3200.00 17550.00 13350.00 1021.00 91521.00 22.79
MW-3 1340.00 13400.00 4170.00 17800.00 16.50 1130.00 37856.50 23.01
MW-6 4530.00 27400.00 3900.00 17200.00 0.00 1080.00 54110.00 23.48
Avg.2935.00 20400.00 4035.00 17500.00 8.25 1105.00 45983.25 23.25
MW-2 161.00 66.00 43.90 44.20 713.00 0.00 1028.10 23.34
MW-5 760.00 1150.00 2560.00 10300.00 7580.00 1310.00 23660.00 25.38
Avg.460.50 608.00 1301.95 5172.10 4146.50 655.00 12344.05 24.36
Date
Average Water
Column Height
(ft.)
08/24/23 7.37
Notes:
• FP: Free Product
• Area of the contaminant plume is calculated from Figure #10
• Height of the water column is calculated by subtracting the average depth to water from the average well depth of the referenced monitoring wells
• Volume of the contaminant plume is calculated by multiplying the area of the plume by the average height of the water column during each sampling event
• Effective porosity is assumed based on the sub-surface soil profile obtained from well construction records and soil boring logs
• Total mass was calculated by multiplying the total contaminant concentrations for the sampling event with effective volume
• Contaminant mass cannot be calculated in wells containing FP; therefore, the total contaminant mass is based on the known concentrations in the area for each sampling event.
APPENDIX F
PERCENTAGE REDUCTIONS
RUSHCO #4 (INCIDENT NO. 48124)
Baseline Event
3,382 ------
Total Contaminant Mass
(g)
Percent Reduction Compared
to Previous Event Percent Reduction To Date
1
147,824
64,554
58,429
0.20
0.20
0.20
739,120
322,768
292,146
26,102
11,398
10,31732.50
4,627.98
1,688.66
1,062.52
5.64
6.75
9.71
24.36
23.25
22.79
Area 3
Area 2
Area 1
30.00
30.00
3
2
1,824.75
---
---
---
---
2,970.58
5,350.26
------5.64
6.76
9.72
08/24/23
08/24/23
08/24/23
Appendix G
Notification of Local Officials
3502 Hayes Road • Monroe, North Carolina 28110
113 West Firetower Road, Suite G • Winterville, North Carolina 28590
Phone (704) 845-4010 • (888) 870-4133 • Fax (704) 845-4012
September 15, 2023
CERTIFIED MAIL
Ms. Alyssa Harris
Rowan County Health Director
1811 East Innes Street
Salisbury, NC 28146
RE: Comprehensive Site Assessment – Public Notice
Former Rushco Food Store #4
1901 West Innes Street
Salisbury, North Carolina
Rowan County
Incident Number: 48124
GRI Project Number: 5721
Dear Ms. Harris:
In October 2021, a petroleum release was reported at the above referenced property. In conjunction with
the North Carolina Department of Environmental Quality (NCDEQ) guidelines, soil and ground water
assessment activities were conducted at the site. The assessment activities included a Phase I Limited Site
Assessment (LSA), an Additional Risk Assessment (ARA), and a Comprehensive Site Assessment (CSA)
on the subject property.
Please find enclosed a copy of the executive summary and pertinent figures and tables associated with the
CSA Report for the above referenced site in accordance with the public notice requirements listed 15A
NCAC 2L .0114 of the Guidelines for Assessment and Corrective Action published by the UST Section
of NCDEQ.
Please do not hesitate to contact the undersigned at (704) 845-4010 if you have any questions or
comments.
Sincerely,
Samuel McKay III, P.G.
Project Manager
enclosure
3502 Hayes Road • Monroe, North Carolina 28110
113 West Firetower Road, Suite G • Winterville, North Carolina 28590
Phone (704) 845-4010 • (888) 870-4133 • Fax (704) 845-4012
September 15, 2023
CERTIFIED MAIL
Mr. Jim Greene Jr.
Salisbury City Manager
132 North Main Street
Salisbury, NC 28144
RE: Comprehensive Site Assessment – Public Notice
Former Rushco Food Store #4
1901 West Innes Street
Salisbury, North Carolina
Rowan County
Incident Number: 48124
GRI Project Number: 5721
Dear Mr. Greene:
In October 2021, a petroleum release was reported at the above referenced property. In conjunction with
the North Carolina Department of Environmental Quality (NCDEQ) guidelines, soil and ground water
assessment activities were conducted at the site. The assessment activities included a Phase I Limited Site
Assessment (LSA), an Additional Risk Assessment (ARA), and a Comprehensive Site Assessment (CSA)
on the subject property.
Please find enclosed a copy of the executive summary and pertinent figures and tables associated with the
CSA Report for the above referenced site in accordance with the public notice requirements listed 15A
NCAC 2L .0114 of the Guidelines for Assessment and Corrective Action published by the UST Section
of NCDEQ.
Please do not hesitate to contact the undersigned at (704) 845-4010 if you have any questions or
comments.
Sincerely,
Samuel McKay III, P.G.
Project Manager
enclosure
3502 Hayes Road • Monroe, North Carolina 28110
113 West Firetower Road, Suite G • Winterville, North Carolina 28590
Phone (704) 845-4010 • (888) 870-4133 • Fax (704) 845-4012
September 15, 2023
CERTIFIED MAIL
Mayor Karen Alexander
Mayor of Salisbury
Post Office Box 479
Salisbury, NC 28145
RE: Comprehensive Site Assessment – Public Notice
Former Rushco Food Store #4
1901 West Innes Street
Salisbury, North Carolina
Rowan County
Incident Number: 48124
GRI Project Number: 5721
Dear Mayor Alexander:
In October 2021, a petroleum release was reported at the above referenced property. In conjunction with
the North Carolina Department of Environmental Quality (NCDEQ) guidelines, soil and ground water
assessment activities were conducted at the site. The assessment activities included a Phase I Limited Site
Assessment (LSA), an Additional Risk Assessment (ARA), and a Comprehensive Site Assessment (CSA)
on the subject property.
.
Please find enclosed a copy of the executive summary and pertinent figures and tables associated with the
CSA Report for the above referenced site in accordance with the public notice requirements listed 15A
NCAC 2L .0114 of the Guidelines for Assessment and Corrective Action published by the UST Section
of NCDEQ.
Please do not hesitate to contact the undersigned at (704) 845-4010 if you have any questions or
comments.
Sincerely,
Samuel McKay III, P.G.
Project Manager
enclosure