MO-29522_48657_CA_IAR_20220830_Initial Abatement Action Report

Cedar Rock
ENVIRONMENTAL
August 30, 2022
Ms. Trudy Beverly
NCDEQ
Division of Waste Management - UST Section
610 East Center Avenue
Mooresville, North Carolina 28115
CEDAR ROCK ENVIRONMENTAL, P.C.
107 Pioneer Trail
Graham, NC 27253
[phone]
Reference: Initial Abatement Action Report for the Rental and Home Solutions Property
8610 Douglas Drive, Charlotte, Mecklenburg County
Incident Number: Pending
Cedar Rock Project Number: 343522590
Dear Ms. Beverly:
Please accept this Initial Abatement Action Report for a release of fuel oil from one non-commercial
underground storage tank (UST) formerly located at the above referenced property. This report satisfies
the requirements specified in the Underground Storage Tank Section Guidelines for Site Checks, Tank
Closure, and Initial Response and Abatement, Change 11 (May 17, 2021).
One UST, used for storing home heating oil, was removed from the subject property on August 23, 2022.
A total of 32.01 tons of impacted soil were excavated and transported to a permitted facility for
bioremediation as an initial abatement measure. The laboratory results for five soil samples collected from
the limits of the excavation showed that no petroleum residuals remain in the unexcavated soils.
If you have any questions or need additional information, please give me a call.
Sincerely,
pr_6�"� 1___'
Robert A. Payne,)L.G.
Enclosure
cc: Mr. Johnny Sayasith — Property Owner

Cedar Rock
ENVIRONMENTAL
August 30, 2022
Mr. Johnny Sayasith
928 Rocky River Road West
Charlotte, NC 28213
Reference: Initial Abatement Action Report
Dear Mr. Sayasith:
CEDAR ROCK ENVIRONMENTAL, P.C.
107 Pioneer Trail
Graham, NC 27253
[phone]
Cedar Rock Environmental, P.C. (Cedar Rock) is pleased to submit this Initial Abatement Action Report
to satisfy the requirements specified in the Underground Storage Tank Section Guidelines for Site Checks,
Tank Closure, and Initial Response and Abatement, Change 11 (May 17, 2021) for a release of fuel oil from
the former underground heating oil system located at the 8610 Douglas Drive property in Charlotte, North
Carolina. This report should be maintained for your records. A copy of this report has been sent to the
North Carolina Department of Environmental Quality (NCDEQ), Division of Waste Management (DWM),
UST Section in Mooresville.
Enclosed is an invoice for this work effort. If you have any questions, please feel free to contact me at 336-
376-0394.
Sincerely,
RobeAne, L.G.
President

INITIAL ABATEMENT
ACTION REPORT
RENTAL AND HOME SOLUTIONS
PROPERTY
8610 DOUGLAS DRIVE
CHARLOTTE, MECKLENBURG COUNTY
Date Release Discovered: April 29, 2022
Source: One 560-Gallon Heating Oil UST
Incident No.: Pending
Prepared by:
Cedar Rock Environmental, P. C.
107 Pioneer Trail, Graham, North Carolina
August 30, 2022
CRE Project #343522590

INITIAL ABATEMENT ACTION REPORT
A. Site Information
1. Project name: Rental and Home Solutions Property
2. Facility ID #: N/A (residential)
3. Site Facility address, county, and telephone no.: 8610 Douglas Drive, Charlotte, NC 28217,
Mecklenburg County.
4. Latitude and longitude of release: 35.180231 °N / 80.950337 °W (from Google Earth).
B. Release Information
1. Incident number: Pending.
2. Date release discovered: April 29, 2022.
3. Estimated quantity of release: Unknown.
4. Cause of release: Corrosion of UST.
5. Source of release: One 560-gallon heating oil UST.
C. Ownership Information
1. Name, address, and telephone number of current UST owner: Rental and Home Solutions c/o
Johnny Sayasith, 928 Rocky River Road West, Charlotte, NC 28213. Phone: [phone]
2. Name and address of current property owner: Same as above.
D. Consultant/contractors
1. Primary consultant: Cedar Rock Environmental, P.C.
107 Pioneer Trail, Graham, NC 27253
Robert A. Payne, L.G. [phone]
2. Excavation: Terra Nova Solutions
901 East Springfield Road,
High Point, NC 27263 [phone]
3. Soil Disposal: AES of NC, LLC
P.O. Box 310, Sanford, NC 27331 [phone]
4. Laboratory: Pace Analytical Services, LLC
North Carolina Field Services Certification #5342
1377 South Park Drive, Kernersville, NC 27284 [phone]
E. Report Certification
I, Robert A. Pae, a Licensed Geologist for
Cedar Rock Environmental, P.C., do certify that
the information contained in this report is correct
and accurate to the best of my knowledge.
License #: 970
(Signature & Seal)
Cedar Rock Environmental, P.C. is licensed to practice geology in North Carolina. The
number of the corporation is C-324 .
August 30, 2022
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Title Page

TABLE OF CONTENTS
Section Pam
1.0 SITE HISTORY AND CHARACTERIZATION ............................... 1
2.0 INITIAL RESPONSE AND ABATEMENT ACTIVITIES ....................... 1
3.0 EXCAVATION OF CONTAMINATED SOIL ................................ 1
3.1 Field Activities...................................................... 1
3.2 Soils Investigation.................................................... 2
3.3 Discussion of Results .................................................. 2
4.0 CONCLUSIONS AND RECOMMENDATIONS ............................... 2
5.0 REFERENCES.......................................................... 3
Fifzures
1 Site Location Map
2 Site Map
3 Sample Locations and Results
Table
1 UST Owner and Operator Information
2 UST System Information
3 Summary of Soil Sampling Results
Appendices
A Photographic Documentation
B Disposal Manifests
C Excavation Log
D Sampling & Decontamination Procedures
E Laboratory Report & Chain -of -Custody
i

1.0 SITE HISTORY AND CHARACTERIZATION
The project site is a residential property located at 8610 Douglas Drive in Charlotte, North Carolina
(see Figure 1). One 560-gallon underground storage tank (UST), identified as T1, was located as
shown in Figure 2. According to the Mecklenburg County tax office records, the building was
constructed in 1961. Table 1 lists pertinent storage tank system ownership information. Table 2
lists specific UST information for T1. The subject site is surrounded by residential properties.
There is an active onsite water supply well located as shown in Figure 2. City water is available
to properties in the area.
2.0 INITIAL RESPONSE AND ABATEMENT ACTIVITIES
Tank removal activities were performed on August 23, 2022, under the supervision of Cedar Rock
Environmental (Cedar Rock). Prior to removing T1 from the ground, approximately 356 gallons
of water and fuel oil were removed from the tank by Terra Nova Solutions of High Point, North
Carolina. Upon removal from the ground, the UST was found to be corroded, and the underlying
soils were observed to have been impacted by leakage (strong petroleum odor and soil
discoloration).
Initial abatement activities consisted of excavating 32.01 tons of obviously contaminated soil from
the source area of the release. Soil removal continued to a maximum depth of 9.5 feet. The lateral
dimensions of the excavation pit measured about 10.5 feet by 6.5 feet at the pit floor. The
excavated contaminated soil was transported to a permitted disposal facility located in
Thomasville, North Carolina for bioremediation.
No free product was encountered during the initial abatement activities. There are no other
subsurface structures on the subject site where free product or vapors could accumulate, or that
would provide a migration pathway for the release. The possibility of an explosion or the threat
to public health and safety or to the environment from the accumulation of vapors does not appear
to be of concern at this time. Therefore, the release is unlikely to be a significant fire/safety/health
hazard.
The 24-Hour Release Report and UST Leak Reporting Form (UST-61) was submitted to the North
Carolina Department of Environmental Quality (NCDEQ), Division of Waste Management
(DWM), UST Section in Mooresville on August 22, 2022.
3.0 EXCAVATION OF CONTAMINATED SOIL
3.1 Field Activities
Tank closure activities were performed on August 23, 2022 (see photographs in Appendix A).
Petroleum -impacted soils were encountered in the source area at a depth of about 5.0 feet below
land surface (bls). As impacted soil was removed from the source area, the soils were
periodically inspected by a North Carolina licensed geologist for evidence of petroleum
residuals (staining and odors). Soil removal continued to a maximum depth of 9.5 feet. The
1

lateral dimensions of the excavation pit measured about 10.5 feet by 6.5 feet at the pit floor
(see Figure 3). Neither bedrock nor groundwater were encountered during excavation
activities.
A total of 32.01 tons of contaminated soil were transported to a permitted disposal facility
located in Sanford, North Carolina for bioremediation. The subject UST was disposed of by
Terra Nova Solutions at the D. H. Griffin facility in High Point, North Carolina. Copies of the
fluids, UST and soils disposal manifests are included in Appendix B.
3.2 Soils Investigation
According to the Geologic Map of North Carolina (1985), the subject site is underlain by
granitic rock. The native soils in the source area of the release consisted of a reddish -orange
sandy SILT. A copy of the excavation log for the excavation is included in Appendix C.
On August 23, 2022, Cedar Rock collected six soil samples to document the effectiveness of
soil excavation. One soil sample, CR-1, was collected from one foot beneath the eastern end
of the former location of T1. Five soil samples, CR-2 through CR-6, were collected from the
limits of the excavation. Sample locations are shown in Figure 3. The soil samples were
collected according to the sampling procedures included in Appendix D. Soil samples CR-1
through CR-6 were submitted to the laboratory to be analyzed for Total Petroleum
Hydrocarbons (TPH) by EPA Methods 3550 and 5030.
TPH were quantified in soil sample CR-1 at a concentration of 9,320 parts per million (ppm)
by EPA Method 3550, and at a concentration of 11.7 ppm by EPA Method 5030. No TPH
were quantified in soil samples CR-2 through CR-6 by either of the methods. Soil sampling
activities and results are summarized in Table 3. A copy of the laboratory report and chain -
of -custody is included in Appendix E.
3.3 Discussion of Results
Figure 3 shows a plan view of the source area, limits of the excavation, and soil sample
locations in relation to the former location of the UST.
Petroleum -impacted soils were encountered in the source area at a depth of about 5.0 feet bls.
Soil removal continued to a maximum depth of 9.5 feet. The lateral dimensions of the
excavation pit measured about 10.5 feet by 6.5 feet at the pit floor.
Five soil samples were collected from the limits of the excavation where contamination was
most likely to remain. As shown in Table 3, no petroleum constituents were quantified in these
soil samples.
4.0 CONCLUSIONS AND RECOMMENDATIONS
One UST, used for storing home heating oil, was removed from the subject property on August
23, 2022. A total of 32.01 tons of impacted soil were excavated and transported to a permitted
2

facility for bioremediation as an initial abatement measure. The laboratory results for five soil
samples collected from the limits of the excavation showed that no petroleum residuals remain in
the unexcavated soils. Cedar Rock recommends that the DWM should issue a "Notice of No
Further Action" (NFA) letter to close out the release incident.
5.0 REFERENCES
24-Hour Release Report and UST LeakReporting Form (UST-61); submitted to the North Carolina
Department of Environmental Quality, Division of Waste Management, UST Section,
Mooresville Regional Office on August 22, 2022.
Underground Storage Tank Section Guidelines for Site Checks, Tank Closure, and Initial
Response and Abatement, Change 11; published by the North Carolina Department of
Environmental Quality, Division of Waste Management, UST Section, May 17, 2021.
Geologic Map of North Carolina; published by the North Carolina Department of Natural
Resources and Community Development, Division of Land Resources, 1985.
3

FIGURES

Data use subject to license. *TN Scale 1 : 12,000
© DeLorme. Topo North AmericaTM 10. MN (8.1^w) ^I o 2W 4W 6W goo 1000
m
0 100 2IX1 300 400 500
www.delorme.com 1" = 1.000.0 ft Data Zoom 14-3

I
I
I
James Maynor
Property
I
I
I
I
I
I
I
I
Virginia McGinn
Property
Douglas Drive
T1
Water
® supply
well
I
0 20 40 80 r----- i
T1 = 560-Gallon UST
1 inch = 40 feet - : Property Lines
PROJECT: Rental and Home Solutions Property CEDAR ROCK
INCIDENT#: Pending ENVIRONMENTAL, P. C. SITE MAP
LOCATION: 8610 Douglas Drive
Charlotte, Mecklenburg Co. FILENAME: 3435-Fig2.tcw
CRE PROJECT NUMBER: 343522590 VERSION DATE: 8/30/22 FIGURE 2

SOIL SAMPLE ANALYTICAL SUMMARY
Sample ID
Depth (ft.)
TPH 5030 (ppm)
TPH 3550 (ppm)
CR-1
6.0
11.7
9,320
CR-2
8.5
BQL
BQL
CR-3
8.5
BQL
BQL
CR-4
9.5
BQL
BQL
CR-5
8.5
BQL
BQL
CR-6
9.5
BQL
BQL
5 r2 l
2iil 13
Water
®supply
well
r------I
: T1 = 560-Gallon UST
----
0 10 20 40 - - : Limits of Excavation
1 inch = 20 feet • Sample Locations (CR-x)
PROJECT: Rental and Home Solutions Property CEDAR ROCK SAMPLE
INCIDENT#: Pending ENVIRONMENTAL, P. C. LOCATIONS
LOCATION: 8610 Douglas Drive
Charlotte, Mecklenburg Co. FILENAME: 3435-Fig3.tcw AND RESULTS
CRE PROJECT NUMBER: 343522590 VERSION DATE: 8/30/22 FIGURE 3

TABLES

TABLE I
UST OWNER AND OPERATOR INFORMATION
Rental and Home Solutions Property
8610 Douglas Drive, Charlotte, Mecklenburg County
UST ID Number
T1
Facility ID Number
N/A (residential)
Name of Owner/Operator
Dates of Ownership
Rental and Home Solutions c/o Johnny
Sayasith
? — present
Street Address
928 Rocky River Road West
City
State
Zip
Telephone Number
Charlotte
NC
28213
[phone]

TABLE 2
UST SYSTEM INFORMATION
Rental and Home Solutions Property
8610 Douglas Drive, Charlotte, Mecklenburg County
Tank
Description
Was a release
UST ID
Current/Last
Previous
Capacity
Construction
Dimensions
of Assoc.
Date Tank
Status of
associated
Number
Contents
Contents
(in gallons)
Details
(in feet)
Piping/Pumps
Installed
UST/AST
with the
system?
Tl (UST)
#2 Fuel Oil
#2 Fuel Oil
560
Steel
3.33 x 7.67
Copper
Unknown
Removed
Yes,
tubing to &
on
discovered on
from
8/23/2022.
4/29/2022.
foundation
wall.

TABLE 3
SUMMARY OF SOIL SAMPLING RESULTS
Rental and Home Solutions Property
8610 Douglas Drive, Charlotte, Mecklenburg County
Parameter
TPH Action
CR-1
CR-2
CR-3
CR-4
CR-5
CR-6
(Analytical Method)
Limit
Total Petroleum Hydrocarbons
100
9,320
BQL
BQL
BQL
BQL
BQL
(EPA Method 3550)
Total Petroleum Hydrocarbons
50
11.7
BQL
BQL
BQL
BQL
BQL
(EPA Method 5030)
Sample Collection Procedure
Hand Grab
Hand Grab
Hand Grab
Hand Grab
Hand Grab
Hand Grab
Sample Location
Below
eastern end
North wall of
East wall of
South wall
West wall of
Center of pit
of Tl .
pit.
pit.
of pit.
pit.
floor.
Sample Depth (ft. bls)
6.0
8.5
8.5
9.5
8.5
9.5
Date of Sample Collection
8/23/22
8/23/22
8/23/22
8/23/22
8/23/22
8/23/22
Incident Phase
UST Closure
UST Closure
UST Closure
UST Closure
UST Closure
UST Closure
Results and TPH Action Limit in parts per million (ppm).
bls = below land surface
N/A = Not Applicable
Results for in bold and shaded exceeded the TPH Action Limits.

APPENDIX A
Photographic Documentation

4i

APPENDIX B
Disposal Manifests

MATERIAL � Manifest Document No.
bra �°
MANIFEST Page of '
rrt.uoru W.r 6 I0d.,W.1 S.,Wc 1
EMERGENCY PHONE NO. POST OFFICE BOX 357 TEL [phone] ZebNo.
[phone] HIGH POINT, NC 27261 FAX [phone] C
GENERATOR INFORMATION
Name Home _ / Jeexhl
SOiU�'� US EPA ID No.
Street AM�'26 /�� �� Mailing Address Phone tda. 336 6 ,Ar; sZ73
Contact 90 /a
DESCRIPTION OF MATERIALS
USDQT Proper Shipping Name
HMI (Complete All Items for Hazardous Materials)
Hazard
Class or Div
UN / NA
ID No.
Packing
Group
Containers
Qty. Type
Total
Quantity
Unit
Wt./Vol.
a.
��� d Ide ourr'
XV
Pt/ an
b.
C.
ADDITIONAL
INFORMATION
ERG No.
Zebra Profile Code
Facility Use
a.
fry [ ii
b.
C.
GENERATOR'S CERTIFICATION
This is to certify that the above -described materials are properly classified, described, packaged, marked and labeled, and are in
proper condition for transportation according to the applicable regulations of the Department of Transportation. I further certify that
none of the materials described above are a hazardous waste as defined by EPA 40 CFR Part 261 or any applicable state law, and
unless specifically identified above, the materials contain less than 1, 000 ppm total halogens and do not contain quantifiable levels
(2 ppm) of PCBs as defined by EPA 40 CFR Parts 279 and 761.
e'lf V.
2-?12 z
TRANSPORTER
INFORMATION
Transporter Zebra Environmental & Industrial Services Inc
I hereby acknowledge receipt of the a ve-described materials for transport
from the gone site listed ab e.
Address
901 East Springfield Road
r.
High Point, NC 27263
Signature 5 ipment ate
I hereby a knowledge receipt of t above -described materials were received
from the generatorslte and were ansported to the facility listed below.
Transporter or NCO991302669
i
EPA ID No.
Z
Phone [phone]
Signature f Delivery Date
FACILITY INFORMATION
Facility Zebra Environmental & Industrial Services, Inc.
I hereby acknowledge receipt of the materials covered by this manifest
except for any discrepancy noted below.
4/�Pam; "7 �---
Address
901 East Springfield Road
High Point, NC 27263
Signatur lReceipt Date
DI c e les outin Codes 1 HandingMethods
Facility or NCO991302669
EPA ID Ala.
a'
Phone
(336)1$41-5276
b.
Contact Bill Hunter
C.
0
ORIGINAL - Facility Retain COPY 2 - Return to Generator COPY 3 - Transporter Retain COPY 4 - Generator Retain

'zebra
ENVIRONMENTAL &
INDUSTRIAL SERVICES
A Terro Nova Company
901 East Springfield Road High Point, NC 27263 Phone: [phone] Fax: [phone]
Tank Disposal Manifest
Ta,qk Owner/Autho iz I
ttoe'
6-76 IU a"A
and Mailing address
Tank Owner/Authorized Representative: Contact: )e 0/0 1%11-folf
Phone: .3. 2
Description of Tanks:
Tank No. Capacity Previous Contents
s�
Comments
Tank Owner/Authorized Representative Certification: The undersigned certifies that the above
listed storage tanks have been removed from the premises of the tank owner.
Signature
Printed Name
Month/Day/Year
Transporter: The under signed certifies that the above listed storage tanks have been transported to
Zebra Environmental & industrial Services Inc, 901 East Springfield Road High Point, NC 27263
Signature LJ Printed Name ' /"Month/Day/Year
Disposal Certification: The undersigned certifies that the above -named storage tank(s) have been
accepted by the metal recycling facility.
Recycling Facility:
Signature Printed Name Month/Day/Year

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APPENDIX C
Excavation Log

EXCAVATION LOG
PROJECT NUMBER: 343522590
PROJECT: Rental and Home Solutions Property
LOC.: 8610 Douglas Drive, Charlotte
COUNTY: Mecklenburg
DATE STARTED: 8/23/2022
DATE COMPLETED: 8/23/2022
CONTRACTOR: Zebra Environmental, Inc.
BACKFILL: brown silt
DIA. x
TANK # GALS. LENGTH (ft.)
T1 560 3.33 x 7.67
CONTENTS
BOTTOM
(ft.)
5.0
FREE PRODUCT ENCOUNTERED? No
DEPTH TO BEDROCK: n/a GROUNDWATER: n/a
FINAL DIMENSIONS OF EXC.: 6.5' (W) x 10.5' (L) x 9.5' (D)
VOL. REMOVED & DISPOSED: 32.01 tons
SAMPLE
DEPTH IN
FEET
LOCATION
(wall,
SAMPLE NO.
AND TYPE
USGS
SYMBOL
DESCRIPTION OF MATERIAL
REMARKS
floor, etc.)
—
0 - 5.0': backfill
1
2
3
4
5
..... ..............
5.0 - 95: reddish -orange sandy SILT
CR-1
6
7
8
CR-2,3&5
9
CR-4&6
10
_ _ _ _ _ _ _ _ _ _
Excavation terminated at 9.5 feet (pit center)
11
12
13
14
15
16
17
18
19
CEDAR ROCK ENVIRONMENTAL, P. C.

APPENDIX D
Sampling & Decontamination Procedures

CEDAR ROCK ENVIRONMENTAL, P.C.
EQUIPMENT DECONTAMINATION PROCEDURES
Every effort will be made to prevent cross -contamination of soil and groundwater samples before,
during, and after sample collection. It is company policy that drillers contracted by Cedar Rock
decontaminate their drilling and sampling equipment with steam prior to, and after, each use and/or
each boring. The following procedures apply to the decontamination of field equipment used by
Cedar Rock employees.
Soil Sampling Equipment
Stainless steel hand augers, spoons, and knives will be cleaned prior to, and after, each use and/or
each boring. If hand auger advancement of a borehole through contaminated soil is obvious or
suspected, a clean auger bucket will be used to retrieve the sample portion. A fresh pair of
disposable vinyl gloves will be worn while handling the sample container.
Sampling equipment will be decontaminated by washing with phosphate -free soapy water; rinsing
in tap water followed by an isopropyl alcohol rinse; and a final "triple" rinse with distilled water.
The equipment will then be allowed to air dry. Clean sampling spoons and knives will be stored
in a fresh ziplock bag.
If available, steam may be used instead of the above procedure.
Groundwater Sampling quipment
Use of groundwater level measuring devices will proceed from the wells known to be the least
contaminated to those known to be more contaminated. If it is not known how contaminated the
wells are, measurements will be taken on the up gradient wells prior to the down gradient wells.
A fresh pair of disposable vinyl gloves will be worn at each well during water level and sample
collection.
Water level measuring and well sampling (i.e., pumps and lines) devices will be decontaminated
between wells by washing the wetted portion of the device as described above.
Each well will be sampled with a new disposable or decontaminated, dedicated bailer during each
sampling event. New nylon or cotton string will be used during each sampling event on each
bailer. If the bailer contains a significant quantity of silt or sand after purging the well of stagnant
water, the bailer may be flushed with distilled water. The bailer will never come into contact with
anything other than a gloved hand or the inside of the well casing. While allowing the well to
recover, the bailer will be hung inside the well at the top of the casing. The string will be coiled
and placed in a ziplock bag or vinyl glove such that it does not come into contact with other objects.
Groundwater sample containers will be wiped dry and stored in individual ziplock bags.

CEDAR ROCK ENVIRONMENTAL, P.C.
SOIL SAMPLING PROCEDURES
(Collection and Handling)
Soil sampling will be performed by, or under, the direct supervision of a North Carolina licensed
geologist. Care will be taken to minimize the loss of contaminants from the sample during sample
collection, storage, and transport through disturbance of the internal structure of the soil and
exposure to heat, sunlight, and air. Decontamination and handling procedures will be used that
minimize the chance of cross -contamination of the samples during and after sample collection.
All tools used to retrieve, divide, and collect the sample portion (e.g., hand augers, split -barrel
sampler, stainless steel spoons, etc.) will be decontaminated prior to and after each use (between
samples). See Decontamination Procedures.
Vinyl disposable gloves will be worn during sample collection. Gloves will be changed as
necessary after handling the sampling equipment (i.e., after breaking open split -barrels) to avoid
cross -contamination. Contact between the gloved hand and the soil will be minimized by dividing
and collecting the sample portion using a stainless steel spoon or knife.
The sample portion will be collected from the core of the soil at the end of the sampling device
where the deepest retrieved soil is represented (e.g., hand auger teeth). If the sample is being
retrieved using the backhoe bucket, the sample portion will be collected from the consolidated
material located directly behind one of the bucket teeth. A separate sampling implement will be
used to scrape away foreign material if present and/or the soil which came into contact with the
sample retrieving device in order to expose the core of the sample portion to be collected.
Immediately upon removal from the ground, the sample will be placed in a laboratory -provided,
decontaminated container. The sample container will be precooled, if possible, to minimize loss
of volatiles. The sample portion will be disturbed as little as possible during placement into the
container. The container will be filled leaving no head -space and immediately capped and sealed.
Immediately upon collection, the exterior of the sample container will be wiped free of soil, if
necessary, and placed in a ziplock bag to minimize cross -contamination. The sample will
immediately be placed in a cooler of ice for storage and transport to the analytical laboratory.
The sample will be labeled with sample identification number, project number, date and time of
collection, and analyses to be conducted. The sample will be transported as soon as practical to a
North Carolina certified laboratory under chain -of -custody.

APPENDIX E
Laboratory Report & Chain -of -Custody

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
August 30, 2022
Robert Payne
Cedar Rock Environmental
107 Pioneer Trail
Graham, NC 27253
RE: Project: RENTAL AND HOME SOLUTIONS PROP
Pace Project No.: 92622229
Dear Robert Payne:
Enclosed are the analytical results for sample(s) received by the laboratory on August 24, 2022. The results relate only to
the samples included in this report. Results reported herein conform to the applicable TNI/NELAC Standards and the
laboratory's Quality Manual, where applicable, unless otherwise noted in the body of the report.
The test results provided in this final report were generated by each of the following laboratories within the Pace Network:
• Pace Analytical Services - Charlotte
If you have any questions concerning this report, please feel free to contact me.
Sincerely,
Stephanie Knott
[e-mail]
704-977-0981
Project Manager
Enclosures
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Page 1 of 15

lacmnalyfica('
www,pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
Project: RENTALAND HOME SOLUTIONS PROP
Pace Project No.: 92622229
Pace Analytical Services Charlotte
South Carolina Laboratory ID: 99006
9800 Kincey Ave. Ste 100, Huntersville, NC 28078
North Carolina Drinking Water Certification #: 37706
North Carolina Field Services Certification #: 5342
North Carolina Wastewater Certification #: 12
South Carolina Laboratory ID: 99006
CERTIFICATIONS
South Carolina Certification #: 99006001
South Carolina Drinking Water Cert. #: 99006003
Florida/NELAP Certification #: E87627
Kentucky UST Certification #: 84
Louisiana DoH Drinking Water #: LA029
Virginia/VELAP Certification #: 460221
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC. Page 2 of 15

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
SAMPLE SUMMARY
Project: RENTAL AND HOME SOLUTIONS PROP
Pace Project No.: 92622229
Lab ID
Sample ID
Matrix
Date Collected
Date Received
92622229001
CR-1
Solid
08/23/22 09:20
08/24/22 09:30
92622229002
CR-2
Solid
08/23/22 10:46
08/24/22 09:30
92622229003
CR-3
Solid
08/23/22 11:15
08/24/22 09:30
92622229004
CR-4
Solid
08/23/22 11:00
08/24/22 09:30
92622229005
CR-5
Solid
08/23/22 10:25
08/24/22 09:30
92622229006
CR-6
Solid
08/23/22 11:05
08/24/22 09:30
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Page 3 of 15

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
SAMPLE ANALYTE COUNT
Project:
Pace Project No.:
RENTAL AND HOME SOLUTIONS PROP
92622229
Analytes
Lab ID
Sample ID
Method
Analysts
Reported
Laboratory
92622229001
CR-1
EPA 8015C
HH
2
PASI-C
EPA 8015C
TEG
2
PASI-C
SW-846
KDF
1
PASI-C
92622229002
CR-2
EPA 8015C
HH
2
PASI-C
EPA 8015C
TEG
2
PASI-C
SW-846
KDF
1
PASI-C
92622229003
CR-3
EPA 8015C
HH
2
PASI-C
EPA 8015C
TEG
2
PASI-C
SW-846
KDF
1
PASI-C
92622229004
CR-4
EPA 8015C
HH
2
PASI-C
EPA 8015C
TEG
2
PASI-C
SW-846
KDF
1
PASI-C
92622229005
CR-5
EPA 8015C
HH
2
PASI-C
EPA 8015C
TEG
2
PASI-C
SW-846
KDF
1
PASI-C
92622229006
CR-6
EPA 8015C
HH
2
PASI-C
EPA 8015C
TEG
2
PASI-C
SW-846
KDF
1
PASI-C
PASI-C = Pace Analytical
Services - Charlotte
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC. Page 4 of 15

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
ANALYTICAL RESULTS
Project: RENTAL AND HOME SOLUTIONS PROP
Pace Project No.: 92622229
Sample: CR-1 Lab ID: 92622229001 Collected: 08/23/22 09:20 Received: 08/24/22 09:30 Matrix: Solid
Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions.
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual
8015 GCS THC-Diesel
Analytical Method: EPA 8015C Preparation Method: EPA 3546
Pace Analytical Services - Charlotte
Diesel Range Organics(C10-C28)
9320 mg/kg 249 40 08/27/22 16:59
08/30/22 10:35 M1
Surrogates
n-Pentacosane (S)
0 % 10-130 40 08/27/22 16:59
08/30/22 10:35 629-99-2 S4
Gasoline Range Organics
Analytical Method: EPA 8015C Preparation Method: EPA 5030B
Pace Analytical Services - Charlotte
Gas Range Organics (C6-C10)
11.7 mg/kg 9.1 1 08/25/22 12:31
08/25/22 19:33
Surrogates
4-Bromofluorobenzene (S)
112 % 66-130 1 08/25/22 12:31
08/25/22 19:33 460-00-4
Percent Moisture
Analytical Method: SW-846
Pace Analytical Services - Charlotte
Percent Moisture
21.1 % 0.10 1
08/25/22 16:57 N2
Sample: CR-2
Lab ID: 92622229002 Collected: 08/23/22 10:46 Received: 08/24/22 09:30 Matrix: Solid
Results reported on a "dry weight"
basis and are adjusted for percent moisture, sample size and any dilutions.
Parameters
Results Units Report Limit DF Prepared
Analyzed CAS No. Qual
8015 GCS THC-Diesel
Analytical Method: EPA 8015C Preparation Method: EPA 3546
Pace Analytical Services - Charlotte
Diesel Range Organics(C10-C28)
ND mg/kg 6.0 1 08/27/22 16:59
08/30/22 10:35
Surrogates
n-Pentacosane (S)
72 % 10-130 1 08/27/22 16:59
08/30/22 10:35 629-99-2
Gasoline Range Organics
Analytical Method: EPA 8015C Preparation Method: EPA 5030E
Pace Analytical Services - Charlotte
Gas Range Organics (C6-C10)
ND mg/kg 8.7 1 08/25/22 12:31
08/25/22 20:24
Surrogates
4-Bromofluorobenzene (S)
101 % 66-130 1 08/25/22 12:31
08/25/22 20:24 460-00-4
Percent Moisture
Analytical Method: SW-846
Pace Analytical Services - Charlotte
Percent Moisture
18.4 % 0.10 1
08/25/22 16:57 N2
Sample: CR-3
Lab ID: 92622229003 Collected: 08/23/22 11:15 Received: 08/24/22 09:30 Matrix: Solid
Results reported on a "dry weight"
basis and are adjusted for percent moisture, sample size and any dilutions.
Parameters
Results Units Report Limit DF Prepared
Analyzed CAS No. Qual
8015 GCS THC-Diesel Analytical Method: EPA 8015C Preparation Method: EPA 3546
Pace Analytical Services - Charlotte
Diesel Range Organics(C10-C28) ND mg/kg 6.1 1 08/27/22 16:59 08/29/22 13:11
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
Date: 08/30/2022 02:01 PM without the written consent of Pace Analytical Services, LLC.
Page 5 of 15

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
ANALYTICAL RESULTS
Project: RENTAL AND HOME SOLUTIONS PROP
Pace Project No.: 92622229
Sample: CR-3 Lab ID: 92622229003 Collected: 08/23/22 11:15 Received: 08/24/22 09:30 Matrix: Solid
Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions.
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual
8015 GCS THC-Diesel
Surrogates
n-Pentacosane (S)
Gasoline Range Organics
Gas Range Organics (C6-C10)
Surrogates
4-Bromofluorobenzene (S)
Percent Moisture
Percent Moisture
Analytical Method: EPA 8015C Preparation Method: EPA 3546
Pace Analytical Services - Charlotte
76 %
10-130
1 08/27/22 16:59
08/29/2213:11 629-99-2
Analytical Method: EPA 8015C Preparation Method: EPA 5030B
Pace Analytical Services - Charlotte
ND mg/kg
8.6
1 08/25/22 12:31
08/25/2216:58
95 %
66-130
1 08/25/22 12:31
08/25/2216:58 460-00-4
Analytical Method: SW-846
Pace Analytical Services - Charlotte
17.9 %
0.10
1
08/25/2216:57
►fa
Sample: CR-4 Lab ID: 92622229004 Collected: 08/23/22 11:00 Received: 08/24/22 09:30 Matrix: Solid
Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions.
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual
8015 GCS THC-Diesel
Analytical Method: EPA 8015C Preparation Method: EPA 3546
Pace Analytical Services - Charlotte
Diesel Range Organics(C10-C28)
ND mg/kg 6.2 1 08/27/22 16:59
08/29/22 13:28
Surrogates
n-Pentacosane (S)
68 % 10-130 1 08/27/22 16:59
08/29/22 13:28 629-99-2
Gasoline Range Organics
Analytical Method: EPA 8015C Preparation Method: EPA 5030E
Pace Analytical Services - Charlotte
Gas Range Organics (C6-C10)
ND mg/kg 8.9 1 08/25/22 12:31
08/25/22 18:41
Surrogates
4-Bromofluorobenzene (S)
98 % 66-130 1 08/25/22 12:31
08/25/22 18:41 460-00-4
Percent Moisture
Analytical Method: SW-846
Pace Analytical Services - Charlotte
Percent Moisture
19.5 % 0.10 1
08/25/22 16:57
N2
Sample: CR-5 Lab ID: 92622229005 Collected: 08/23/22 10:25 Received: 08/24/22 09:30 Matrix: Solid
Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions.
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qua[
8015 GCS THC-Diesel Analytical Method: EPA 8015C Preparation Method: EPA 3546
Pace Analytical Services - Charlotte
Diesel Range Organics(C10-C28) ND mg/kg 6.2 1 08/27/22 16:59 08/29/22 13:28
Date: 08/30/2022 02:01 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
Page 6 of 15

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
ANALYTICAL RESULTS
Project: RENTAL AND HOME SOLUTIONS PROP
Pace Project No.: 92622229
Sample: CR-5 Lab ID: 92622229005 Collected: 08/23/22 10:25 Received: 08/24/22 09:30 Matrix: Solid
Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions.
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual
8015 GCS THC-Diesel
Surrogates
n-Pentacosane(S)
Gasoline Range Organics
Gas Range Organics (C6-C10)
Surrogates
4-Bromofluorobenzene (S)
Percent Moisture
Percent Moisture
Analytical Method: EPA 8015C Preparation Method: EPA 3546
Pace Analytical Services - Charlotte
68 %
10-130
1 08/27/22 16:59
08/29/2213:28 629-99-2
Analytical Method: EPA 8015C Preparation Method: EPA 5030B
Pace Analytical Services - Charlotte
ND mg/kg
8.8
1 08/25/22 12:31
08/25/22 21:16
98 %
66-130
1 08/25/22 12:31
08/25/22 21:16 460-00-4
Analytical Method: SW-846
Pace Analytical Services - Charlotte
18.6 %
0.10
1
08/25/2216:57
►iel
Sample: CR-6 Lab ID: 92622229006 Collected: 08/23/22 11:05 Received: 08/24/22 09:30 Matrix: Solid
Results reported on a "dry weight" basis and are adjusted for percent moisture, sample size and any dilutions.
Parameters Results Units Report Limit DF Prepared Analyzed CAS No. Qual
8015 GCS THC-Diesel
Analytical Method: EPA 8015C Preparation Method: EPA 3546
Pace Analytical Services - Charlotte
Diesel Range Organics(C10-C28)
ND mg/kg 6.2 1 08/27/22 16:59
08/29/22 13:46
Surrogates
n-Pentacosane (S)
144 % 10-130 1 08/27/22 16:59
08/29/22 13:46 629-99-2
Gasoline Range Organics
Analytical Method: EPA 8015C Preparation Method: EPA 5030E
Pace Analytical Services - Charlotte
Gas Range Organics (C6-C10)
ND mg/kg 8.9 1 08/25/22 12:31
08/25/22 22:07
Surrogates
4-Bromofluorobenzene (S)
99 % 66-130 1 08/25/22 12:31
08/25/22 22:07 460-00-4
Percent Moisture
Analytical Method: SW-846
Pace Analytical Services - Charlotte
Percent Moisture
19.5 % 0.10 1
08/25/22 16:57
Date: 08/30/2022 02:01 PM
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
without the written consent of Pace Analytical Services, LLC.
S3
N2
Page 7 of 15

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
QUALITY CONTROL DATA
Project: RENTAL AND HOME SOLUTIONS
PROP
Pace Project No.: 92622229
QC Batch: 719579
Analysis Method: EPA 8015C
QC Batch Method: EPA 5030E
Analysis Description: Gasoline Range Organics
Laboratory: Pace Analytical Services - Charlotte
Associated Lab Samples: 92622229001, 92622229002, 92622229003, 92622229004, 92622229005, 92622229006
METHOD BLANK: 3750271
Matrix: Solid
Associated Lab Samples: 92622229001, 92622229002, 92622229003, 92622229004, 92622229005, 92622229006
Blank Reporting
Parameter
Units
Result Limit Analyzed Qualifiers
Gas Range Organics (C6-C10)
mg/kg
ND 6.0 08/25/22 16:32
4-Bromofluorobenzene (S)
%
97 66-130 08/25/22 16:32
LABORATORY CONTROL SAMPLE:
3750272
Spike LCS LCS % Rec
Parameter
Units
Conc. Result % Rec Limits Qualifiers
Gas Range Organics (C6-C10)
mg/kg
50.2 52.1 104 70-130
4-Bromofluorobenzene (S)
%
97 66-130
MATRIX SPIKE SAMPLE:
3750274
92622229004 Spike MS MS
% Rec
Parameter
Units
Result Conc. Result % Rec
Limits Qualifiers
Gas Range Organics (C6-C10)
mg/kg
ND 74.2 88.2 118
65-146
4-Bromofluorobenzene (S)
%
101
66-130
SAMPLE DUPLICATE: 3750273
92622229003 Dup Max
Parameter
Units
Result Result RPD RPD
Qualifiers
Gas Range Organics (C6-C10)
mg/kg
ND ND 30
4-Bromofluorobenzene (S)
%
95 98
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
Date: 08/30/2022 02:01 PM without the written consent of Pace Analytical Services, LLC.
Page 8 of 15

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
QUALITY CONTROL DATA
Project: RENTAL AND HOME SOLUTIONS
PROP
Pace Project No.: 92622229
QC Batch: 719991
Analysis Method: EPA 8015C
QC Batch Method: EPA 3546
Analysis Description: 8015 Solid GCSV
Laboratory: Pace Analytical Services - Charlotte
Associated Lab Samples: 92622229001, 92622229002, 92622229003, 92622229004, 92622229005, 92622229006
METHOD BLANK: 3752322
Matrix: Solid
Associated Lab Samples: 92622229001, 92622229002, 92622229003, 92622229004, 92622229005, 92622229006
Blank Reporting
Parameter
Units
Result Limit Analyzed Qualifiers
Diesel Range Organics(C10-C28)
mg/kg
ND 5.0 08/29/22 11:43
n-Pentacosane (S)
%
70 10-130 08/29/22 11:43
LABORATORY CONTROL SAMPLE:
3752323
Spike LCS LCS % Rec
Parameter
Units
Conc. Result % Rec Limits Qualifiers
Diesel Range Organics(C10-C28)
mg/kg
66.9 44.0 66 44-130
n-Pentacosane (S)
%
59 10-130
MATRIX SPIKE SAMPLE:
3752324
92622229001 Spike MS MS
% Rec
Parameter
Units
Result Conc. Result % Rec
Limits Qualifiers
Diesel Range Organics(C10-C28)
mg/kg
9320 83.4 11400 2540
10-130 M1
n-Pentacosane(S)
%
391
10-130 SO
SAMPLE DUPLICATE: 3752325
92622229002 Dup Max
Parameter
Units
Result Result RPD RPD
Qualifiers
Diesel Range Organics(C10-C28)
mg/kg
ND ND 30
n-Pentacosane (S)
%
72 78
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
Date: 08/30/2022 02:01 PM without the written consent of Pace Analytical Services, LLC.
Page 9 of 15

Pace Analytical Services, LLC
leac,yficalAnal1377 South Park Drive
Kernersville, NC 27284
www.pacelabs.com [phone]
QUALITY CONTROL DATA
Project: RENTAL AND HOME SOLUTIONS PROP
Pace Project No.: 92622229
QC Batch: 719706 Analysis Method: SW-846
QC Batch Method: SW-846 Analysis Description: Dry Weight/Percent Moisture
Laboratory: Pace Analytical Services - Charlotte
Associated Lab Samples: 92622229001, 92622229002, 92622229003, 92622229004, 92622229005, 92622229006
SAMPLE DUPLICATE: 3751056
92622229001 Dup Max
Parameter Units Result Result RPD RPD Qualifiers
Percent Moisture % 21.1 21.1 0 25 N2
SAMPLE DUPLICATE: 3751057
92621898002 Dup Max
Parameter Units Result Result RPD RPD Qualifiers
Percent Moisture % 29.7 17.9 49 25 D6,N2
Results presented on this page are in the units indicated by the "Units" column except where an alternate unit is presented to the right of the result.
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
Date: 08/30/2022 02:01 PM without the written consent of Pace Analytical Services, LLC.
Page 10 of 15

Pace Analytical Services, LLC
leac,yficalAnal1377 South Park Drive
Kernersville, NC 27284
www.pacelabs.com [phone]
QUALIFIERS
Project: RENTAL AND HOME SOLUTIONS PROP
Pace Project No.: 92622229
DEFINITIONS
DF - Dilution Factor, if reported, represents the factor applied to the reported data due to dilution of the sample aliquot.
ND - Not Detected at or above adjusted reporting limit.
TNTC - Too Numerous To Count
J - Estimated concentration above the adjusted method detection limit and below the adjusted reporting limit.
MDL -Adjusted Method Detection Limit.
PQL - Practical Quantitation Limit.
RL - Reporting Limit - The lowest concentration value that meets project requirements for quantitative data with known precision and
bias for a specific analyte in a specific matrix.
S - Surrogate
1,2-Diphenylhydrazine decomposes to and cannot be separated from Azobenzene using Method 8270. The result for each analyte is
a combined concentration.
Consistent with EPA guidelines, unrounded data are displayed and have been used to calculate % recovery and RPD values.
LCS(D) - Laboratory Control Sample (Duplicate)
MS(D) - Matrix Spike (Duplicate)
DUP - Sample Duplicate
RPD - Relative Percent Difference
NC - Not Calculable.
SG - Silica Gel - Clean -Up
U - Indicates the compound was analyzed for, but not detected.
Acid preservation may not be appropriate for 2 Chloroethylvinyl ether.
A separate vial preserved to a pH of 4-5 is recommended in SW846 Chapter 4 for the analysis of Acrolein and Acrylonitrile by EPA
Method 8260.
N-Nitrosodiphenylamine decomposes and cannot be separated from Diphenylamine using Method 8270. The result reported for
each analyte is a combined concentration.
Reported results are not rounded until the final step prior to reporting. Therefore, calculated parameters that are typically reported as
"Total" may vary slightly from the sum of the reported component parameters.
Pace Analytical is TNI accredited. Contact your Pace PM for the current list of accredited analytes.
TN -The NELAC Institute.
ANALYTE QUALIFIERS
D6 The precision between the sample and sample duplicate exceeded laboratory control limits.
M1 Matrix spike recovery exceeded QC limits. Batch accepted based on laboratory control sample (LCS) recovery.
N2 The lab does not hold NELAC/TNI accreditation for this parameter but other accreditations/certifications may apply. A
complete list of accreditations/certifications is available upon request.
SO Surrogate recovery outside laboratory control limits.
S3 Surrogate recovery exceeded laboratory control limits. Analyte presence below reporting limits in associated sample.
S4 Surrogate recovery not evaluated against control limits due to sample dilution.
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
Date: 08/30/2022 02:01 PM without the written consent of Pace Analytical Services, LLC. Page 11 of 15

leAnalyiical
www.pacelabs.com
Pace Analytical Services, LLC
1377 South Park Drive
Kernersville, NC 27284
[phone]
QUALITY CONTROL DATA CROSS REFERENCE TABLE
Project:
Pace Project No.:
RENTAL AND HOME SOLUTIONS PROP
92622229
Analytical
Lab ID
Sample ID
QC Batch Method
QC Batch
Analytical Method
Batch
92622229001
CR-1
EPA 3546
719991
EPA 8015C
720083
92622229002
CR-2
EPA 3546
719991
EPA 8015C
720083
92622229003
CR-3
EPA 3546
719991
EPA 8015C
720083
92622229004
CR-4
EPA 3546
719991
EPA 8015C
720083
92622229005
CR-5
EPA 3546
719991
EPA 8015C
720083
92622229006
CR-6
EPA 3546
719991
EPA 8015C
720083
92622229001
CR-1
EPA 5030B
719579
EPA 8015C
719647
92622229002
CR-2
EPA 5030B
719579
EPA 8015C
719647
92622229003
CR-3
EPA 5030B
719579
EPA 8015C
719647
92622229004
CR-4
EPA 5030B
719579
EPA 8015C
719647
92622229005
CR-5
EPA 5030B
719579
EPA 8015C
719647
92622229006
CR-6
EPA 5030B
719579
EPA 8015C
719647
92622229001
CR-1
SW-846
719706
92622229002
CR-2
SW-846
719706
92622229003
CR-3
SW-846
719706
92622229004
CR-4
SW-846
719706
92622229005
CR-5
SW-846
719706
92622229006
CR-6
SW-846
719706
REPORT OF LABORATORY ANALYSIS
This report shall not be reproduced, except in full,
Date: 08/30/2022 02:01 PM without the written consent of Pace Analytical Services, LLC. Page 12 of 15

��m mjw. GEYY vFxnli-nuts I vuoa vU t sample i oncimon uporl rcecelpt
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Effective Date: 05/121202205/12/2022
Laboratory receiving samples:
Ash evij a en reenwoo__ H.urtersville. RaleighLj Mechanicsville❑ Atlanta❑ Kernersvilleil-
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' _ Project #: W0# 9L'.622Z12�
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Thermometer:
❑ IR Gun ID:
Type of Ice: Ellwet ❑ Blue
Correction Factor:
Cooler Temp: Cl Add/Subtract ('Cj
Cooler Temp Corrected (°C):
USDA Regulated Soil (❑ N/A, water sample)
Did samples originate in a quarantine zone within the United States: CA, NY, or SC
(check maps)? I IYes FlNo
Chain of Custody Present?
Samples Arrived within Hold Time?
Short Hold Time Analysis (c72 hr.)?
Rush Turn Around Time Requested?
Sufficient Volume?
Correct Containers Used?
-Pace Containers Used?
Containers Intact?
Dissolved analysis: Samples Field Filtered?
Sample Labels Match COC?
-Includes Date/Time/ID/Analysis Matrix:
Headspace in VOA Vials (>S-6mm)?
Trip Blank Present?
Trip Blank Custody Seals Present?
COMMENTS/SAMPLE DISCREPANCY
CLIENT NOTIFICATION/RESOLUTION
Person contacted:
©Yes
❑No
❑N/A
1.
Yes
ONO
❑N/A
2.
❑Yes
No-
[]N/A
3.
❑]�Ye''s
No
❑N/A
4.
3Yes
❑No
❑N/A
S.
[:]No
[]N/A
6,
❑No
❑N/A
QYes ❑No ❑N/A 7.
❑Yes ❑No d/A 81
[�fes ❑No ❑N/A 9.
LjYes I -)No UN
J�A 1 10.
❑Yes ❑No /A 1 11.
Date(tnitials Person Examining
❑Yes ❑No ❑N/A
❑None
Temp should be above freezing to 6'C
❑samples out of temp criteria. Samples on ice, cooling process
has begun
Did samples originate from a foreign source (internationally,
including Hawaii and Puerto Rico)? ❑Yes ❑No
CommentslD€screoancv:
Lot ID of split containers:
Date/Time:
Project Manager SCURF Review: Date:
Protect Manager SRF ANu;pw-
Field Data Required? ❑Yes []No
Qualtrax ID: 69614 Page 1 of 2 Page 13 of 15

—u" J i-uvo3 vv t z)ampie uonaition upon Keceipt
ace
Effective Date: 05/12/202205/12/2022
*
within the acceptance range for preservation samples.
Exceptions: VOA, Coliform, TOC, Oil and Grease, DRO/80151waterl DOC, ttftg
**Bottom half of box is to list number of bottles_
***Check all unpreserved Nitrates for chlorine
L
PM: SIC Due Date: 08/31/22
CLIEN'r: KR—CedarRock
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pH Adjustment Log for Preserved Samples
receipt Date preservation adjusted Time preservation
adjusted
added
d
MVIt! „ d uiscrepdncy dlleCling Nortn Carolina compliance samples, a copy of this form will be sent to the North Carolina DENR Certification Of#ice (i.e.
Out of hold, incorrect preservative, out of temp, incorrect containers.
Qualtrax ICE; 69614 Page 2 of 2 Page 14 of 15

SAMPLES
SANI
LAB
C
LERS'
RATOR
LLECI
GNA
LITILI
ED BY: Damien Callaghan
RE- �r �
ED: Pace Analytical
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CIOtSY
REQUESTED ANALYSIS
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SAMPLE ILIATRIX
LAB i
NO.
DATE
TIME
COUP
GRAB
SALIPLE ID
23120
0920
X
CR-1
1
X
X
SOIL
8/23/20
1046
X
CR-2
1
X
X
SOIL C?GZ
8/23/20
1115
1
X
CR-3
1
X
X
SOIL c� i3
8/23/20
1100
X
CR-4
1
X
X
SOIL �'i
8123/20
1025
X
CR-5
1
X
X
SOIL
8/23/20
1105
X
CR-6
1
X
X
SOIL Q
R5.kN'Q f 'r.
G nY
M75
TWE
R=C=I`J=D 3Y :C 4'
R=_`.'f.R<T:
Via^-.^lG te•,- _rat_ru aL rzxFt t Samples on ICB.
-
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TIS.�/c)
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ft= g�. Y S�l�
J
rR,2L'ISf^-G
ECT.
ENT
CNN:
arlott
Rental acid
Home
Solutions Property1(37
Pioneer Trail
Ceder Rock Graham, NC 27253
Etlr�iranmerltal, P_C.cedarrockena [e-mail]
Attn: Robert Payne
t336) 376-4394
C
CUST
AWN CIF'T
DY RECOF,D
Pending
8610 Douglas
Dri
a
; Meckle
burg Co'
PRZJ_
T NJ'VEFR
34
522590

Beverly, Trudy
From: Beverly, Trudy
Sent: Wednesday, August 31, 2022 6:37 AM
To: Robert Payne
Subject: RE: [External] Initial Abatement Action (IAA) report for 8610 Douglas Drive, Charlotte
Received, thank you.
Trudy
Trudy Beverly, L.G.
Hydrogeologist, Division of Waste Management
North Carolina Department of Environmental Quality
w'rnme�n e�r UST Section, Mooresville Regional Office
704.235.2182 (Office)
Trudy. B everly(a,ncdenr. gov
Email correspondence to and from this address is subject to the
North Carolina Public Records Law and may be disclosed to third parties.
Office Mailing Address:
610 East Center Avenue, Suite 301
Mooresville, NC 28115
Branch's Underground Storage Tanks Website Address: https://deq.nc.gov/about/divisions/waste-management/ust
Branch's Above Ground Storage Tanks Website Address: https://deq.nc.gov/about/divisions/waste-mana2ement/ust/ast-proaram
INTERACTIVE MAPS WITH DWM SITES AND PERMITTED FACILITIES:
httns://deo.nc. eov/about/divisions/waste-manaeement/waste-manaeement-rules-data/waste-manaeement-ais-macs
File Review Procedures:
https://deq.nc. gov/about/divisions/waste-management/ust/file-review-procedures#mooresvilI e-regional-office
ONLINE ACCESS TO UST SECTION DOCUMENTS (Laserfiche):
htips://deq.nc.gov/about/divisions/waste-management/laserfiche
Document Submittal & UST File Names for Laserfiche Policies:
httys:Hfiles.nc.aov/nedea/Waste%2OMana2ement/DWMIUST/WhatsNew/Final-Electronic-Document-Submittal-Policy.odf
https:Hfiles.nc. gov/ncdeq/Waste%2OManagement/DWM/UST/Corrective%2OAction/UST%20file%20names%20for%2OLaserfiche.docx
From: Robert Payne <[e-mail]>
Sent: Tuesday, August 30, 2022 10:55 PM
To: Beverly, Trudy <[e-mail]>
Subject: [External] Initial Abatement Action (IAA) report for 8610 Douglas Drive, Charlotte
CAUTION: External email. Do not click links or open attachments unless you verify. Send all suspicious email as an attachment to
Report Spam.
Hello Trudy. Attached is Cedar Rock's IAA report. All soil contamination was successfully removed. Please issue an NFA
when you have the time. Thank you,
Robert A. Payne, L. G.
(cell) 336-684-2734
Jeremiah 9:23-24