11037_Double-Oaks_Northerly_Building 1012 Addl Sampling Report_rev

DOUBLE OAKS BROWNFIELDS PROPERTY
NORTHERLY TOWNHOMES
1986 Newland Avenue
Charlotte, North Carolina
Brownfields Project ID No. 11037-07-060
VIMS ADDITIONAL SAMPLING REPORT BUILDING 1012
H&H JOB NO. NVR-019
JUNE 11, 2024

2923 S Tryon Street, Suite 100
Charlotte, NC 28203
704 586 0007
harthickman.com Raleigh, NC 27607
919 847 4241
#C-1269 Engineering / #C-245 Geology
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VIMS Additional Sampling Report Building 1012
Double Oaks - Northerly Townhomes Charlotte, North Carolina Brownfields Project No. 11037-07-060 H&H Job No. NVR-019
Table of Contents 1.0 Introduction ..............................................................................................................................1
2.0 Sub-Slab Soil Gas Assessment Activities ...............................................................................4
2.1 Sub-Slab Soil Gas Sampling...................................................................................................4
2.2 Sub-Slab Soil Gas Sampling Results ......................................................................................5
2.3 Vapor Intrusion Evaluation ....................................................................................................7
3.0 Summary and Conclusions .....................................................................................................9

List of Tables

Table 1 Summary of Sub-Slab Soil Gas Analytical Data

List of Figures

Figure 1 Site Location Map
Figure 2 Site Plan

List of Appendices
Appendix A VIMS As-Built Drawings
Appendix B Field Forms and Field Data
Appendix C Laboratory Analytical Report
Appendix D PVC Primer and PVC Glue Material Safety Data Sheets
Appendix E DEQ Risk Calculator Summary Pages

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VIMS Additional Sampling Report Building 1012
Double Oaks - Northerly Townhomes Charlotte, North Carolina Brownfields Project No. 11037-07-060 H&H Job No. NVR-019
1.0 Introduction

Hart & Hickman, PC (H&H) has prepared this report to document additional sub-slab soil gas
sampling activities completed for Building 1012 at the Northerly Townhomes development at the
Double Oaks North Carolina Department of Environmental Quality (DEQ) Brownfields Property
(Brownfields Project No. 11037-07-060). The property is located at 1386 Newland Avenue in
Charlotte, Mecklenburg County, North Carolina (Site or subject Site). The Site consists of two
parcels of land (Parcel ID Nos.: 07707902 and 07707903) that total approximately 5.37 acres. The
larger parcel (Parcel No. 07707902) is approximately 5.26 acres in size and is part of a larger
Brownfields property (referred to as the Double Oaks Brownfields property), which is comprised
of multiple parcels of contiguous and noncontiguous parcels of land that total approximately 56
acres. The smaller parcel (Parcel No. 07707903) is approximately 0.11-acre and is not part of the
Double Oaks Brownfields property.

The Northerly Townhomes (also known as the Atando Northerly) development plan includes
construction of 17 buildings consisting of 96 for-sale townhome units by Ryan Homes, an NVR,
Inc. (NVR) company. The buildings include one 4-unit townhome building, eight 5-unit
townhome buildings, five 6-unit townhome buildings, and three 7-unit townhome buildings. This
report has been prepared for Atando Townhomes Building 1012 which includes a total of six
townhome units (Units 63 through 68) constructed in the south-eastern portion of the Site. The
units are also identified with a letter designation (Units A through F) in the as-builts drawings and
sample identifications. A Site location map is provided as Figure 1, and a Site Plan that identifies
Building 1012 is shown in Figure 2. A table listing the unit numbers, associated unit letter
identifications, monitoring point identifications (see Section 2.0), and unit addresses for Building
1012 is included below.

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Building 1012

H&H previously completed soil and soil gas sampling assessment activities for the Site in
December 2021, January 2022, and April 2023 to evaluate subsurface conditions for potential
impacts. Results of previous exterior soil gas assessment activities completed at the Site identified
chloroform, naphthalene, and bromodichloromethane in soil gas samples at concentrations above
their respective DEQ Division of Waste Management (DWM) Residential Soil Gas Screening
Levels (SGSLs). Further, the chlorinated solvents trichloroethylene (TCE) and
tetrachloroethylene (PCE) were detected in one location, VSP-5, in the northeast portion of the
property at concentrations above the laboratory method detection limits but below their respective
Residential SGSLs. PCE was also detected at low levels below its Residential SGSL in several
other samples. An Environmental Management Plan (EMP), dated May 17, 2022, describing Site
assessment activities conducted prior to May 2022 and was submitted to and approved by DEQ.

A Brownfields Agreement between Double Oaks Development, LLC and DEQ was recorded for
the Site on October 27, 2010, with an amendment to the Brownfields Agreement recorded on
December 15, 2016. Double Oaks Development has since sold a portion of the property to NVR
where the Site is located. Based on the Site information presented above and in accordance with
the requirements of the DEQ-approved EMP, plus additional discussions with DEQ, a VIMS will
be installed at Buildings 1002, 1004, and 1005 at the Site by NVR during construction of the
buildings, and a VIMS has been installed in Building 1012. In addition to the passive VIMS in
these buildings, the developer (NVR) will also install or has already installed a vapor barrier below
the slab of the 13 remaining buildings (1001, 1003, 1006 through 1011, and 1013 through 1017)
at the Site as a precautionary measure. H&H prepared the Vapor Intrusion Mitigation Plan
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(VIMP) and revisions to the VIMP based on DEQ comments describing the VIMS design for these
buildings. The VIMP – Revision 2 dated June 13, 2023, was approved by DEQ in a letter dated
June 30, 2023.
Building 1012 consists of six individually owned three-story townhomes. Each unit includes a
stairwell, garage, and living spaces located on the ground floor of the structure. The ground floor
for each townhome unit is approximately 640 square feet. The second and third floors of each unit
contain living spaces. Each of the units contains a flat roof with an attic space (i.e. roof heel) that
is approximately 3-feet thick between the ceiling of the top floor and the roof. The VIMS installed
within Building 1012 is a passive sub-slab depressurization system comprised of sub-slab vent
piping set within a stone base below the ground floor slabs, riser pipes that extend from the slab to
the building’s roof, and ventilators installed on the rooftop to promote air exhaust from the risers.
The installation of the passive VIMS in Building 1012 was described in the H&H VIMS
Installation Completion Report – Atando Townhomes Building 1012, dated October 21, 2023
(VIMS Installation Report). DEQ subsequently issued the Conditional Compliance
Review Building 1012 letter dated October 31, 2023 with the condition to perform an
additional sub-slab soil gas (sub-slab vapor) sampling event at Units B and D in Building
1012 due to elevated concentrations of several compounds generally associated with
off-gassing from building materials (see Section 2.0).
The additional sampling requested by DEQ was conducted in November 2023. However, the
November 2023 results indicated elevated concentrations of similar compounds compared to the
original sampling event. Therefore, upon further discussion with DEQ, Units B and D were
subsequently sampled again in April 2024. The sub-slab soil gas sampling from November 2023
and April 2024 are described in this report. In addition, data associated with the original sampling
event (September 2023) is included for reference. Additional details regarding the VIMS
installation are included in the VIMS Installation Report, and VIMS as-built drawings are also
included in Appendix A for ease of reference.
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2.0 Sub-Slab Soil Gas Assessment Activities

The sub-slab soil gas assessment activities were conducted in accordance with the DEQ-approved
VIMP and DEQ Division of Waste Management (DWM) Vapor Intrusion Guidance (Guidance)
dated March 2018.

2.1 Sub-Slab Soil Gas Sampling On September 6, 2023 and as documented in the VIMS Installation Report, H&H collected three
sub-slab soil gas samples from permanent monitoring points in Building 1012 prior to occupancy
of the building as part of the VIMS efficacy testing. The sampling was performed following VIMS
installation activities and approximately two weeks after installation of the stationary ventilators.
The sub-slab soil gas samples were collected from permanent monitoring point locations MP-
1012-B (sample ID SS-1012-B), MP-1012-D (sample ID SS-1012-D), and MP-1012-F (sample
ID SS-1012-F) as shown on Drawing VM-2 (Appendix A). One duplicate sub-slab soil gas sample
(SS-1012-DUP) was collected for quality assurance/quality control (QA/QC) purposes during the
event from the SS-1012-F parent location. The duplicate sample was collected utilizing a
laboratory supplied stainless-steel sampling “T” which allows for the simultaneous collection of
two sub-slab soil gas samples from a single location.

Based on the conditional compliance review letter (Section 1.0) and subsequent discussions with
DEQ, additional sub-slab soil gas sampling occurred on November 13, 2023 and again on April
30, 2024. The sub-slab soil gas samples were collected from permanent monitoring point locations
MP-1012-B (sample IDs: SSV-1012B and SS-1012-B) and MP-1012-D (sample IDs: SSV-1012D
and SS-1012-D), during the November 2023 and April 2024 sampling events, respectively. One
duplicate sub-slab soil gas sample (SS-1012-DUP) was collected for quality assurance/quality
control (QA/QC) purposes from the SS-1012-B parent location during the November 2023 and
April 2024 sampling events.

To collect the sub-slab soil gas samples, Teflon sample tubing was attached to a 2-inch expandable
well cap with a sampling port that was secured onto the 2-inch diameter PVC monitoring point.
The tubing was connected to an airflow regulator and laboratory-supplied batch-certified 1-liter
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stainless steel Summa canister. The air flow regulator was preset by the laboratory to collect a soil
gas sample at a flow rate of approximately 100 milliliters per minute.

Prior to sample collection, H&H conducted a leak test at each monitoring point by placing a shroud
around the monitoring point, expandable well cap, and sampling train including the Summa
canister. The air within the shroud was flooded with helium gas and concentrations were measured
with a calibrated helium detector. Helium concentrations within the shroud were maintained at
approximately 10 to 15%. A GilAir vacuum pump was connected to the sample tubing outside of
the shroud and used to purge a minimum of three volumes (monitoring point and sample train) of
soil gas into a Tedlar® bag at each sampling point. The helium gas detector was used to measure
helium concentrations within the Tedlar bag sample to confirm helium concentrations in the
sample were less than 10% of that measured within the shroud. Results of the helium leak checks
indicate that helium was not detected in the purge air above the threshold which indicates
unacceptable short-circuiting at the monitoring points or within the sampling train were not
present. Soil gas sampling field forms completed by sampling personnel in November 2023 and
April 2024 are included in Appendix B.

Following a successful leak check, the air flow regulators were opened to allow collection of the
sub-slab soil gas samples. Vacuum in the Summa canisters was monitored during the sampling
event to confirm adequate sample volume was collected at each monitoring point location. Upon
completion of sample collection, the air flow regulator was closed to the Summa canister. The
canisters were labeled with the sample identification, beginning and ending times, pressure
measurements, and the requested analysis. The canisters were then placed in laboratory supplied
shipping containers and delivered to Waypoint Analytical (Waypoint) under standard chain of
custody protocols for analysis of volatile organic compounds (VOCs) by Environmental Protection
Agency (EPA) Method TO-15.
2.2 Sub-Slab Soil Gas Sampling Results

The sub-slab soil gas sample analytical results are summarized in Table 1. The results were
compared to the DEQ DWM Residential Vapor Intrusion SGSLs dated July 2023 for the samples
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collected in 2023. The 2024 sample results were compared to the DEQ DWM Residential Vapor
Intrusion SGSLs dated February 2024. The laboratory analytical reports for the November 2023
and April 2024 sampling events with chain of custody records are provided in Appendix C. The
September 2023 analytical data was previously described in the VIMS Installation Report, but for
ease of reference, a summary of the September 2023 analytical results is included below and in
Table 1. For both the November 2023 and April 2024 sampling results, the laboratory results
indicated comparable compounds detected and comparable concentrations between the parent and
duplicate samples, thereby indicating good laboratory reproducibility for the results.

September 2023 Sample Results
The September 2023 sub-slab soil gas sample analytical results indicate that multiple compounds
were detected in each sample above the laboratory method detection limit (MDL), but below their
respective Residential SGSL. The chlorinated solvents TCE and PCE were not detected above the
laboratory MDLs in the samples collected in September 2023.

Acetone, 2-butanone (methyl ethyl ketone [MEK]), and tetrahydrofuran were detected at
concentrations that were orders of magnitude above the other compounds detected in each sample.
Acetone and 2-butanone were each detected at concentrations below the Residential SGSLs.
Tetrahydrofuran was detected above the Residential SGSL of 14,000 μg/m3 at a concentration of
35,200 μg/m3 in sample SS-1012-B. As stated earlier, due to the elevated concentrations of these
compounds and associated elevated laboratory MDLs for other compounds, DEQ requested
additional sampling for Units B and D after review of the VIMS Installation Report. Note, DEQ
did not request additional sampling for Unit F in Building 1012 which contained lower
concentrations of the abovementioned compounds.

November 2023 Sample Results
The November 2023 sub-slab soil gas sample analytical results indicate that tetrahydrofuran was
the only compound that exceeded its Residential SGSL in any of the samples. The concentrations
of tetrahydrofuran in the samples ranged from 50,000 E μg/m3 to 113,000 E μg/m3, which exceeded
the Residential SGSL of 14,000 μg/m3. This concentration contained the laboratory “E” qualifier,
which indicates the concentration exceeded the calibration range of the laboratory instrument.
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Multiple other compounds during the November 2023 sample event were detected in each sample
above the laboratory MDL, but below their respective Residential SGSL. Acetone, MEK, and
isopropanol were detected at concentrations higher than concentrations detected during the
September 2023 event. The chlorinated solvents TCE and PCE were not detected above the
laboratory MDLs in the samples collected in November 2023.

April 2024 Sample Results
The April 2024 sub-slab soil gas sample analytical results indicated that no compounds exceeded
Residential SGSLs, including the compound tetrahydrofuran where the concentration decreased
by approximately two orders of magnitude as compared to the November 2023 sampling results.
The chlorinated solvent PCE was detected at estimated low concentrations ranging from 1.02 J
μg/m3 to 1.26 J μg/m3, which are orders of magnitude below the Residential SGSL of 280 μg/m3.
The chlorinated compound TCE was not detected above the laboratory MDLs in the samples
collected in April 2024.

2.3 Vapor Intrusion Evaluation
The elevated compounds during the September 2023 and November 2023 sampling events were
generally comprised of acetone, MEK, and tetrahydrofuran. Acetone and MEK are two of the
main components in PVC primer, and tetrahydrofuran is one of the main components in PVC glue.
PVC primer and glue are common construction materials used throughout construction of the
townhome units, including on the sub-slab plumbing pipes. Therefore, these compound detections
are attributable to VOC off-gassing from the building materials. As expected, the concentrations
of these compounds significantly decreased during the April 2024 event as the VOCs from
building materials off-gassed overtime. Material safety data sheets for PVC glue and primer used
during construction are included as Appendix D.

The DEQ DWM Vapor Intrusion SGSLs are very conservative and based on a target carcinogenic
risk (TCR) for potential carcinogenic risks of 1 x 10-6 and a hazard quotient (HQ) of 0.2 for
potential non-carcinogenic risks. The DEQ and EPA acceptable risk level for potential
carcinogenic risks is a cumulative lifetime incremental cancer risk (LICR) of 1 x 10-4 or less and
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the acceptable level for non-carcinogenic risks is a cumulative hazard index (HI) of 1 or less. The
HI is the sum of HQs for each target analyte.

H&H utilized the DEQ Risk Calculator (dated July 2023 and February 2024) to confirm there are
no potential vapor intrusion risks at unacceptable levels. H&H modeled a worst-case scenario by
using the highest concentrations of any compound detected during each event below Building 1012
in a residential use scenario to conservatively evaluate potential vapor intrusion risks. The
calculated cumulative LICR and HI values are provided in Table 1, and a copy of the completed
DEQ Risk Calculator for the November 2023 and April 2024 sampling events is provided in
Appendix E.

As shown in Table 1, results of the worst-case risk calculations indicated a calculated cumulative
LICR of 5.5 x 10-8 and a HI value of 0.59 during the September 2023 sample event, which indicated
acceptable risk levels for residential use. The additional sampling event conducted in November
2023 indicated a calculated cumulative LICR of 2.9 x 10-5 and a HI value of 3.8, which indicates
an acceptable LICR, but an HI over the acceptable risk level. The second additional sampling
event conducted in April 2024 indicated a calculated cumulative LICR of 3.6 x 10-7 and a HI value
of 0.045. The calculated cumulative residential use LICR and HI values during this most recent
sampling event are well within the DEQ and EPA acceptable levels. These risk calculator results
confirm that compound concentrations detected below the slab do not pose vapor intrusion risks
at unacceptable levels within the townhome units at Building 1012, and the data provides
additional evidence that the previous elevated concentrations detected at Units B and D were
attributable to VOC off-gassing from building materials and these concentrations have decreased
overtime.

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3.0 Summary and Conclusions

Construction of Building 1012 of the Northerly Townhomes development has been completed at
the Double Oaks Brownfields property (Brownfields Project No. 11037-07-060) located in
Charlotte, North Carolina. Installation of the VIMS was reported under separate cover with the
original sub-slab soil gas sampling event conducted in September 2023. Based on DEQ comments
and conditional compliance approval letter, additional sub-slab soil gas sampling events for Units
B and D were conducted in November 2023 and April 2024.

The September 2023 and November 2023 sub-slab soil gas sampling events indicated there were
elevated concentrations of several compounds, including MEK and tetrahydrofuran, associated
with VOC off-gassing from building materials that contributed to elevated laboratory MDLs for
other compounds. In addition, the risk calculations for the November 2023 sampling event
indicated the hazard index exceeded the acceptable residential risk level. However, the April 2024
sub-slab soil gas sampling event indicated the concentrations below the slabs of Units B and D
had decreased with the April 2024 risk calculations indicating acceptable risk levels under a
residential use scenario. These risk calculator results confirm that compound concentrations
detected below the slab do not pose vapor intrusion risks at unacceptable levels within the
townhome units at Building 1012, and the data provides additional evidence that the previous
elevated concentrations detected at Units B and D were attributable to VOC off-gassing from
building materials.

Based on the analytical data, and the presence of the VIMS as detailed in the VIMS Installation
Report, no further sub-slab soil gas analytical sampling is recommended for Building 1012.
Further, the additional sampling described herein was conducted to comply with the condition
listed in the Conditional Compliance Review Building 1012 letter from DEQ dated October 31,
2023.

Copyright:© 2013 National Geographic Society, i-cubed
SITE LOCATION MAP
ATANDO - DOUBLE OAKS PROPERTY 1302 & 1340 NEWLAND AVENUE
CHARLOTTE, NORTH CAROLINA
DATE: 11-16-21
JOB NO: BWR-013
REVISION NO: 0
FIGURE NO: 1
2923 South Tryon Street - Suite 100Charlotte, North Carolina 28203704-586-0007 (p) 704-586-0373 (f)License # C-1269 / # C-245 Geology
TITLE
PROJECT
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U.S.G.S. QUADRANGLE MAP
DERITA, NORTH CAROLINA 2013CHARLOTTE EAST, NORTH CAROLINA 2013
QUADRANGLE7.5 MINUTE SERIES (TOPOGRAPHIC)
LEGEND
SITE PROPERTY BOUNDARY
PARCEL BOUNDARY
SURFACE WATER FEATURE
PROPOSED BUILDING FOOTPRINT
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NOTES:
1.AERIAL IMAGERY AND PARCEL DATA OBTAINED
FROM MECKLENBURG COUNTY GIS (2020).
2.DEVELOPMENT PLAN OBTAINED FROM NVR, INC.
DEVELOPMENT LAYOUT IS APPROXIMATE.
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REVISION NO. 0
JOB NO. NVR-019
DATE: 6-12-23
FIGURE NO. 2
ATANDO-DOUBLE OAKS PROPERTY
NEWLAND ROAD
CHARLOTTE, NORTH CAROLINA
SITE MAP
2923 South Tryon Street-Suite 100
Charlotte, North Carolina 28203
704-586-0007(p) 704-586-0373(f)
License # C-1269 / #C-245 Geology
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Table 1
Summary of Sub-Slab Soil Gas Analytical Data
Atando Townhomes - Building 1012
Charlotte, North Carolina
Brownfields Project No. 11037-07-060
H&H Job No. NVR-019
Building Number
Sample ID SS-1012-B SS-1012-D SSV-1012-D SS-1012-D
Sample Date
Units µg/m3
VOCs (TO-15)
Acetone 20,400 9,270 2,690 2,750 39,100 E 38,400 E 33,600 E 627 626 832 NE
Benzene <1.46 <1.46 <0.366 <0.366 <1.46 <1.46 <1.46 0.277 J 0.469 J 0.456 J 12
Carbon Disulfide <1.22 <1.22 2.16 J 6.29 J <1.22 <1.22 6.04 J 0.249 J,B 0.713 J,B 0.697 J,B 4,900
Chloroform <1.73 <1.73 <0.431 <0.431 <1.73 <1.73 <1.73 1.24 J 1.20 J 0.912 J 4.1
Chloromethane <1.34 <1.34 <0.336 <0.336 <1.34 <1.34 13.1 J <0.067 0.526 J 0.408 J 630
Cyclohexane <3.22 <3.22 <0.804 10.5 J <3.22 <3.22 <3.22 1.91 J <0.161 <0.161 42,000
Dichlorodifluoromethane (Freon 12)<2.68 <2.68 <0.672 3.44 J <2.68 <2.68 <2.68 2.35 J 2.42 J 2.37 J 700
Ethyl Acetate <2.72 <2.72 <0.680 <0.680 <2.72 <2.72 <2.72 <0.136 <0.136 1.84 490
Ethylbenzene <2.12 <2.12 <0.532 2.02 J <2.12 <2.12 <2.12 0.395 J 0.425 J 0.577 J 37
4-Ethyltoluene <2.56 <2.56 2.38 J <0.640 <2.56 <2.56 <2.56 <0.128 <0.128 0.403 J NE
Isopropanol 51.9 J 19.2 J 6.72 J 5.94 J 90.9 J 89.4 J 101 1.77 J,B 4.63 J,B 21.8 1,400
2-Butanone (MEK)857 1,160 2,550 2,670 7,710 7,270 1,870 176 177 231 35,000
Methylene Chloride <9.75 <9.75 <2.44 4.97 J <9.75 <9.75 <9.75 <0.488 0.778 J 0.531 J 3,400
Styrene <2.48 <2.48 <0.617 <0.617 <2.48 <2.48 <2.48 <0.124 <0.124 0.353 J 7,000
Tetrachloroethylene <3.62 <3.62 <0.907 <0.907 <3.62 <3.62 <3.62 1.04 J 1.02 J 1.26 J 280
Tetrahydrofuran 35,200 E 13,700 6,550 6,800 51,600 E 50,000 E 113,000 E 1,230 1,230 2,410 14,000
Toluene 17.3 J 29.7 J 76.6 76.4 <1.80 <1.80 184 2.49 2.72 2.50 35,000
Trichloroethylene <3.98 <3.98 <0.990 <0.990 <3.98 <3.98 <3.98 <0.199 <0.199 <0.199 14
Trichlorofluoromethane (Freon 11)12.4 J 11.1 J 3.68 J 4.04 J <2.60 <2.60 <2.60 1.75 J 1.88 J 1.80 J NE
1,2,4-Trimethylbenzene <2.20 66.1 7.69 J 4.55 J <2.20 <2.20 <2.20 1.04 J 1.07 J 1.66 J 420
1,3,5-Trimethylbenzene <4.72 <4.72 2.19 J <1.18 <4.72 <4.72 <4.72 0.403 J <0.236 0.565 J 420
o-Xylene <3.14 9.90 J 3.37 J 2.95 J <3.14 <3.14 <3.14 0.981 J 0.976 J 1.35 J 700
m&p-Xylene <4.34 26.4 J 8.05 J 7.82 J 7.99 J <4.34 7.82 J 1.77 J 1.83 J 2.47 J 700
Xylene (Total)<3.14 36.3 J 11.4 J 10.8 J 7.99 J <3.14 7.82 J 2.75 J 2.81 J 3.82 J 700
DEQ Risk Calculator (2)Acceptable Risk Levels
Cumulative LICR
Cumulative HI <1.0
Sub-Slab and Exterior Soil Gas (SGSLs) dated February 2024.
Bold value indicates an exceedance of the Residential SGSL.
in a laboratory estimated concentration.
3.8
Worst Case Residential - Soil Gas to Indoor Air Worst Case Residential - Soil Gas to Indoor Air Worst Case Residential - Soil Gas to Indoor Air
Building 1012
Residential SGSLs(1)
9/6/2023 11/13/2023 4/30/2024
https://harthick.sharepoint.com/sites/MasterFiles-1/Shared Documents/AAA-Master Projects/NVR, Inc/NVR-019 - Atando Ave/VIMS Install Reports/Building 1012/2024-04 Sub Slab Resample/Table 1 - Bldg 1012 Data Summary 04.30.24 Update Hart & Hickman, PC

Appendix A
VIMS As-Built Drawings

MP-1012-E
MP-1012-F MP-1012-A
MP-1012-D
MP-1012-C
MP-1012-B
RYAN HOMES, AN NVR,
INC COMPANY
10710 SIKES PLACE
SUITE 200
CHARLOTTE, NORTH
CAROLINA 28277
VAPOR MITIGATION
PLAN PREPARED BY
2923 South Tryon Street-Suite 100Charlotte, North Carolina 28203704-586-0007(p) 704-586-0373(f)
License # C-1269 / #C-245 Geology
PROFESSIONAL APPROVAL / SEAL
VAPOR
INTRUSION
MITIGATION
SYSTEM PLAN
VM-1
H&H NO. NVR.019
AS-BUILT DRAWING
BUILDING 1012
OCTOBER 21, 2023
LEGEND
EXTENT OF VAPOR BARRIER (SEE SPECIFICATION #4 ON SHEET
VM-A)
SOIL GAS COLLECTOR MAT (SEE SPECIFICATION #4)
3" SCH 40 PVC VERTICAL RISER - GROUND FLOOR LOCATION
3" SCH 40 PVC VERTICAL RISER - ROOF DISCHARGE LOCATION
2" SCH 40 PVC VACUUM MONITORING POINT WITH OPEN END
THICKENED SLAB AT LOAD BEARING WALL
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NOTES:
1.ONE VACUUM MONITORING POINT WAS INSTALLED PER UNIT. IF THE UNIT IS AN
END UNIT, THEN VACUUM MONITORING POINT WAS INSTALLED ON THE BACKSIDE
OF THE UNIT. IF THE UNITS ARE INTERIOR UNITS, THEN THE VACUUM MONITORING
POINT WAS INSTALLED ON THE FRONT SIDE OF THE UNIT.
2.INTAKE OF MONITORING POINT WAS POSITIONED A MINIMUM OF 3-FT FROM ANY
EXTERIOR TURNED DOWN SLAB.
3.REFER TO SPECIFICATIONS AND SECTION DETAILS ON SHEETS VM-A AND VM-B.
4.EACH UNIT IS APPROXIMATELY 640 SQ FT (16 FT X 40 FT).
UNIT 63 (F)
3114 COQUINA LANE
UNIT 64 (E)
3118 COQUINA LANE
UNIT 65 (D)
3122 COQUINA LANE
UNIT 66 (C)
3126 COQUINA LANE
UNIT 67 (B)
3130 COQUINA LANE
UNIT 68 (A)
3134 COQUINA LANE
COQUINA LANE
5
VM-B
6
VM-B
9
VM-B
4
VM-B
3
VM-B
7
VM-B
8
VM-B
2
VM-B
4
VM-B
3
VM-B
5
VM-B
6
VM-B
7
VM-B
8
VM-B
2
VM-B
4
VM-B
3
VM-B
8
VM-B
5
VM-B
6
VM-B
3
VM-B
7
VM-B
9
VM-B
9
VM-B
2
VM-B
4
VM-B
10
VM-B
10
VM-B
10
VM-B
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RYAN HOMES, AN NVR,
INC COMPANY
10710 SIKES PLACE
SUITE 200
CHARLOTTE, NORTH
CAROLINA 28277
VAPOR MITIGATION
PLAN PREPARED BY
2923 South Tryon Street-Suite 100Charlotte, North Carolina 28203704-586-0007(p) 704-586-0373(f)
License # C-1269 / #C-245 Geology
VAPOR
INTRUSION
MITIGATION
SYSTEM PLAN
VM-A
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H&H NO. NVR.019
AS-BUILT
SPECIFICATIONS
BUILDING 1012
PROFESSIONAL APPROVAL / SEAL
OCTOBER 21, 2023
VAPOR INTRUSION MITIGATION SYSTEM (VIMS) SPECIFICATIONS
1.THE AS-BUILT DRAWINGS ARE INTENDED TO DOCUMENT THE VIMS COMPONENT INSTALLATION ONLY AND ARE NOT INTENDED TO DOCUMENT CONSTRUCTION OF STRUCTURAL COMPONENTS NOT
RELATED TO THE VIMS. CONSTRUCTION CONTRACTORS VERIFIED CONSISTENCY OF VIMS DETAILS WITH APPLICABLE STRUCTURAL, ARCHITECTURAL, MECHANICAL, AND PLUMBING PLANS AND RESOLVED
INCONSISTENCIES WITH THE DESIGN ENGINEER PRIOR TO VIMS INSTALLATION.
2.INSPECTIONS: INSPECTIONS OF EACH COMPONENT OF THE VIMS WERE CONDUCTED BY THE ENGINEER, OR ENGINEER'S DESIGNEE, TO CONFIRM VIMS COMPONENTS WERE INSTALLED PER THE
APPROVED DESIGN. THE INSPECTIONS INCLUDED: (1) INSPECTION OF SUB-SLAB PIPING LAYOUT AND GRAVEL PLACEMENT PRIOR TO INSTALLING VAPOR BARRIER (LINER); (2) INSPECTION OF VAPOR
BARRIER PRIOR TO POURING CONCRETE; (3) INSPECTION OF ABOVE-GRADE PIPING LAYOUT; AND (4) INSPECTION OF FAN AND VENT PIPE CONNECTIONS.
3.CONSTRUCTION CONTRACTORS AND SUB-CONTRACTORS WERE INSTRUCTED TO USE "LOW OR NO VOC" (INCLUDING NO PCE OR TCE) PRODUCTS AND MATERIALS, WHEN POSSIBLE. THE
CONSTRUCTION CONTRACTOR AND SUB-CONTRACTORS PROVIDED SELECT SAFETY DATA SHEETS (SDS) TO THE ENGINEER FOR PRODUCTS AND MATERIALS USED DURING CONSTRUCTION.
4.VIMS VAPOR BARRIER IS VAPORBLOCK PLUS 20 VAPOR BARRIER MANUFACTURED BY VIAFLEX,INC. THE VAPOR BARRIER WAS INSTALLED AS SPECIFIED HEREIN AND PER MANUFACTURER INSTALLATION
INSTRUCTIONS TO CREATE A CONTINUOUS BARRIER BELOW GROUND FLOOR SLABS AND FOOTERS. A BASE COURSE CONSISTING OF CLEAN #57 STONE WAS INSTALLED BENEATH THE VIMS VAPOR
BARRIER. IN AREAS AROUND THE SOIL GAS COLLECTOR MAT, THE BASE COURSE LAYER WAS INSTALLED WITH A MINIMUM 2-INCH LAYER BELOW THE MAT AND A MINIMUM THICKNESS OF 4-INCHES
ACROSS THE ENTIRE SLAB.
PENETRATIONS WERE SEALED IN GENERAL ACCORDANCE TO VAPOR BARRIER MANUFACTURER INSTALLATION INSTRUCTIONS AS FOUND IN THE MANUFACTURER INSTALLATION GUIDELINES. SMALL
PUNCTURE HOLES WERE SEALED WITH THE VAPORSEALTM TAPE AND LARGER TEARS OR DAMAGE WERE REPAIRED USING A PATCH THAT OVERLAPPED THE DAMAGED AREA AND THEN WAS TAPED ALONG
THE SEAMS.
5.CONSTRUCTION CONTRACTORS AND SUB-CONTRACTORS WERE INSTRUCTED TO AVOID THE USE OF TEMPORARY FORM BOARDS THAT PENETRATE THE VAPOR BARRIER WHERE POSSIBLE. IF
TEMPORARY FORM BOARDS WERE USED, THE SIZE AND NUMBER OF PENETRATIONS THROUGH THE VAPOR BARRIER WERE LIMITED AND SMALL DIAMETER STAKES (I.E. SOLID METAL STAKES) WERE USED.
AS FORM BOARDS WERE REMOVED, THE CONTRACTOR OR SUB-CONTRACTORS SEALED PENETRATIONS IN ACCORDANCE WITH VAPOR BARRIER MANUFACTURER INSTALLATION INSTRUCTIONS.
6.VIMS BELOW AND ABOVE GRADE PIPING WAS SLOPED A MINIMUM OF 18 UNIT VERTICAL IN 12 UNITS HORIZONTAL (1% SLOPE) TO GRAVITY DRAIN. SOLID SECTIONS OF HORIZONTAL COLLECTION
PIPE WERE SUPPORTED TO PREVENT PIPE SAG OR LOW POINT AND MAINTAIN 1% SLOPE TOWARD SLOTTED SECTIONS TO DRAIN CONDENSATION. HORIZONTAL SUB-SLAB COLLECTION SYSTEM CONSISTS
SOIL GAS COLLECTOR MAT WHICH IS APPROXIMATELY 1-INCH THICK BY 12-INCHES WIDE RECTANGULAR CONDUIT.
7.3” SCH 40 PVC RISER DUCT PIPING EXTENDS IN A VERTICAL ORIENTATION THROUGH THE BUILDING ROOF AND TERMINATES A MINIMUM OF 1 FT ABOVE THE BUILDING ROOF LINE. ACTIVE
VENTILATION PRODUCTS AURA AV-3-PVC ALUMINUM VENTILATORS WERE INSTALLED ON THE EXHAUST DISCHARGE END OF EACH RISER DUCT PIPE. THE VENTILATOR WAS SECURED TO THE PVC RISER IN
A VERTICAL ORIENTATION. EXHAUST DISCHARGE IS NOT LESS THAN 10 FT (IN ANY DIRECTION) FROM AIR INTAKE OPENINGS INCLUDE WINDOWS, DOORS, AND OTHER GRAVITY AIR INTAKE OPENINGS. AN
ELECTRICAL JUNCTION BOX (120VAC) WAS INSTALLED NEAR THE RISER WITHIN THE ATTICE SPACE FOR CONVERSION TO ELECTRIC FANS, IF REQUIRED.
8.ABOVE-SLAB ACCESSIBLE RISER DUCT PIPING WAS PERMANENTLY IDENTIFIED BY MEANS OF A LABEL AT A MINIMUM OF ONCE EVERY 10-LINEAR FT WITH "VAPOR MITIGATION - CONTACT
MAINTENANCE". THE RISER PIPE AT THE VENTILATOR WAS LABELED WITH "VAPOR MITIGATION SYSTEM - CONTACT HOA IF DAMAGED" IN AN ACCESSIBLE LOCATION IN THE ATTIC.
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VIMS VAPOR BARRIER AND BASE COURSE1
NTSVM-B
BASE COURSE - CLEAN # 57 STONE (WASHED
WITH NO FINES), MIN 4" THICK BENEATH VIMS
VAPOR BARRIER (SEE SPECIFICATION #4)
VAPOR BARRIER (SEE SPECIFICATION #4)CONCRETE FLOOR SLAB
SUB-BASE
CONCRETE FLOOR SLAB
VIMS SUB-SLAB SLOTTED COLLECTION PIPE2
NTSVM-B
SUB-BASE
SOIL GAS COLLECTOR MAT SET WITHIN MIN
4" BASE COURSE (SEE SPECIFICATION #4)
SECTION THROUGH EXTERIOR WALL3
NTSVM-B
VAPOR BARRIER SEALED TO CONCRETE
PER MANUFACTURER INSTRUCTIONS
SUB-BASEIF EXTERIOR GRADE IS HIGHER THAN THE
SLAB ELEVATION, VAPOR BARRIER WAS
WRAPPED UP THE SIDE OF THE FOOTER
EXTERIOR GRADE (VARIES)
FULLY GROUTED CMU
BLOCK WALL
STUD WALL
BRICK OR HOUSE SIDING
EXTERNAL WALL (NOT
PRESENT AT ALL LOCATIONS)
BASE COURSE
VAPOR BARRIER
FOOTER
SECTION THROUGH TURNED DOWN SLAB AT DRIVEWAY4
NTSVM-B
COMPACTED FILL
BELOW DRIVEWAY
DRIVEWAY
STUD WALL OR EXTERNAL WALL
(NOT PRESENT IN ALL LOCATIONS)
GARAGE
SUB-BASE
BASE COURSE
VAPOR BARRIER SEALED TO CONCRETE
PER MANUFACTURER INSTRUCTIONSEXTEND VAPOR BARRIER TO OUTSIDE
OF FOOTER
SECTION THROUGH TENANT SEPARATION BLOCK WALL5
NTSVM-B
VAPOR BARRIER SEALED TO CONCRETE
PER MANUFACTURER INSTRUCTIONS
SUB-BASE
BASE COURSE
FOOTER
VAPOR BARRIER BENEATH
CONCRETE BLOCK FOUNDATION
FULLY GROUTED CMU
BLOCK WALL, WHERE
PRESENT
SINGLE OR DOUBLE STUD
SEPARATION WALL
CONCRETE
FLOOR SLAB
BASE COURSE
SUB-BASE
VIMS PIPING THROUGH THICKENED SLAB
NTS
6
VM-B
SOLID 3"
SCH 40 PVC
VAPOR BARRIER SEALED TO PIPE
PER MANUFACTURER
INSTRUCTIONS
PIPE SUPPORT TO PREVENT LOW POINT
IN SOLID PIPE. MAINTAINED 1% SLOPE
TOWARD SLOTTED SECTION OF PIPE
VAPOR
BARRIER
VAPOR BARRIER
BENEATH FOOTER
WALL (VARIES)
SOIL GAS
COLLECTOR MAT
MANUFACTURER SPECIFIED
FITTING TO 3" SCH 40 PVC
SOIL GAS COLLECTOR MAT WAS NOT
INSTALLED THROUGH CONCRETE FOOTERS
OR THICKENED SLABS
VIMS PIPING THROUGH SLAB STEPS
NTS
7
VM-B
SUB-BASE MINIMUM 1% SLOPE TOWARD
SLOTTED SECTIONS
BASE COURSE
3" SCH 40 PVC
45-DEGREE ELBOW
VAPOR BARRIER SEALED TO
PIPE PER MANUFACTURER
INSTRUCTIONS
SOLID 3" SCH 40 PVC
WALL (VARIES)
VAPOR BARRIER
SLOPE
MANUFACTURER SPECIFIED
FITTING TO 3" SCH 40 PVC
SOIL GAS
COLLECTOR MAT
VIMS AT VERTICAL RISER
NTS
8
VM-B
BRICK OR HOUSE SIDING
EXTERNAL WALL (NOT PRESENT
AT ALL LOCATIONS)
STUD WALL
VAPOR BARRIER SEALED TO
PIPE AND CONCRETE PER
MANUFACTURER INSTRUCTIONS.
3" SCH 40 PVC RISER DUCT PIPE
(SEE SPECIFICATION #6 & #7)
4" TO 3" PVC REDUCER
4" SCH 40 PVC RISER DUCT PIPE
BASE COURSE
SOIL GAS
COLLECTOR MAT
SUB-BASE
SOIL GAS COLLECTOR MAT CONNECTION SEALED TO
4" SCH 40 PVC RISER WITH POLYURETHANE SEALANT
SOIL GAS COLLECTOR MAT CONNECTION BLOCK TO PVC (ONE 0.5"
DIAMETER HOLE DRILLED IN BOTTOM FOR MOISTURE DRAINAGE)
VAPOR BARRIER
TERMINATED AT SOIL
GRADE
MECH.
CLOSET
VAPOR BARRIER
EXTERIOR PERMANENT VACUUM MONITORING POINT9
NTSVM-B
SLOPE
WALL (VARIES)LOCKABLE WEATHERPROOF
ENCLOSURE PROVIDED ON OUTSIDE OF
BUILDING WALL. LABEL AT BOX WITH
"VAPOR MITIGATION SYSTEM". PLACE
REMOVABLE PIPE PLUG AT END OF 2"
PIPE.
VAPOR BARRIER SEALED TO CONCRETE
PER MANUFACTURER INSTRUCTIONS
2" SCH 40 PVC 90
DEGREE ELBOW
2" SOLID SCH 40 PVC PIPE
FINAL GRADE
(VARIES)BASE COURSE
2" OPEN-ENDED PIPE, PLACED A MINIMUM OF
3' FROM EXTERIOR TURN-DOWN SLABS
VAPOR BARRIER
VAPOR BARRIER SEALED TO PIPE PER
MANUFACTURER INSTRUCTIONS
VIMS EXHAUST AT ROOFTOP WITH HORIZONTAL OFFSET
NTS
FROM RISER
(SEE DETAIL 8)
ROOFTOP
PIPE SUPPORTS
10
VM-B
ATTIC HATCH/OPENING
SOLID 3" SCH 40 PVC,
LENGTH VARIES
ELECTRICAL JUNCTION BOX FOR
POTENTIAL FUTURE VACUUM FAN
(SEE TO SPECIFICATION #7)
DISCHARGE TERMINATES MINIMUM 1' ABOVE ROOF
AND 10-FT FROM OPERABLE OPENING INTO BUILDING.WATERPROOF
FLASHING
STATIONARY VENTILATOR (SEE SPECIFICATION #7)
SLOPE
MIN 1% SLOPE TOWARD
EXTRACTION POINT
RYAN HOMES, AN NVR,
INC COMPANY
10710 SIKES PLACE
SUITE 200
CHARLOTTE, NORTH
CAROLINA 28277
VAPOR MITIGATION
PLAN PREPARED BY
2923 South Tryon Street-Suite 100Charlotte, North Carolina 28203704-586-0007(p) 704-586-0373(f)
License # C-1269 / #C-245 Geology
H&H NO. NVR.019
VAPOR
INTRUSION
MITIGATION
SYSTEM PLAN
VM-B
AS-BUILT DETAILS
BUILDING 1012
PROFESSIONAL APPROVAL / SEAL
OCTOBER 21, 2023
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Appendix B
Field Forms and Field Data

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Appendix C
Laboratory Analytical Reports

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.

11/21/2023
Hart & Hickman (Charlotte) Josh Billiot
2923 South Tryon St. Ste 100 Charlotte, NC, 28203
Ref: Analytical Testing
Lab Report Number: 23-318-0001 Client Project Description: NVR-019-004-D
Dear Josh Billiot:
Waypoint Analytical, LLC (Charlotte) received sample(s) on 11/14/2023 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,
Angela D Overcash Senior Project Manager
Page 1 of 22
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
07/31/202499012State ProgramSouth Carolina
12/31/202399012State ProgramSouth Carolina
Page 1 of 1 00016/23-318-0001
Page 2 of 22
Report Number:
Sample Summary Table
Client Project Description:
23-318-0001
NVR-019-004-D
Lab No Client Sample ID Matrix Date Collected Date Received
11/13/2023 17:04Air 89088 SSV-1012-B 11/14/2023 09:55
11/13/2023Air 89089 SSV-1012-DUP 11/14/2023 09:55
11/13/2023 17:24Air 89090 SSV-1012-D 11/14/2023 09:55
Page 3 of 22
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
23-318-0001
Report Limit
Project:NVR-019-004-D
V 89088SSV-1012-B
E3910011/18/2023 22:24TO-15 Acetone µg/m3 40.4
J90.9 11/18/2023 02:10TO-15 Isopropyl Alcohol µg/m3 2.78
7710 11/18/2023 22:24TO-15 Methyl Ethyl Ketone (MEK)µg/m3 44.8
E5160011/18/2023 22:24TO-15 Tetrahydrofuran µg/m3 21.4
111 11/18/2023 02:10TO-15 1,2,4-Trichlorobenzene µg/m3 4.18
J7.99 11/18/2023 02:10TO-15 m,p-Xylene µg/m3 4.34
J7.99 11/18/2023 02:10TO-15 Xylene (Total)µg/m3 3.14
V 89089SSV-1012-DUP
E3840011/18/2023 23:01TO-15 Acetone µg/m3 40.4
J89.4 11/18/2023 02:47TO-15 Isopropyl Alcohol µg/m3 2.78
7270 11/18/2023 23:01TO-15 Methyl Ethyl Ketone (MEK)µg/m3 44.8
E5000011/18/2023 23:01TO-15 Tetrahydrofuran µg/m3 21.4
85.6 11/18/2023 02:47TO-15 1,2,4-Trichlorobenzene µg/m3 4.18
V 89090SSV-1012-D
E3360011/18/2023 23:37TO-15 Acetone µg/m3 40.4
J6.04 11/18/2023 03:23TO-15 Carbon Disulfide µg/m3 1.22
J13.1 11/18/2023 03:23TO-15 Chloromethane µg/m3 1.34
101 11/18/2023 03:23TO-15 Isopropyl Alcohol µg/m3 2.78
1870 11/18/2023 03:23TO-15 Methyl Ethyl Ketone (MEK)µg/m3 4.48
E11300011/18/2023 23:37TO-15 Tetrahydrofuran µg/m3 21.4
184 11/18/2023 03:23TO-15 Toluene µg/m3 1.80
J27.8 11/18/2023 03:23TO-15 1,2,4-Trichlorobenzene µg/m3 4.18
J7.82 11/18/2023 03:23TO-15 m,p-Xylene µg/m3 4.34
J7.82 11/18/2023 03:23TO-15 Xylene (Total)µg/m3 3.14
Page 4 of 22

Client: Hart & Hickman (Charlotte) CASE NARRATIVE
Project: NVR-019-004-D Lab Report Number: 23-318-0001
Date: 11/20/2023
Volatile Organic Compounds in Air- GC/MS Method TO-15 Sample 89088 (SSV-1012-B) QC Batch No: V40387/V40380
The sample was diluted due to the nature of the sample matrix. Reporting limits have been adjusted accordingly.
Sample 89089 (SSV-1012-DUP) QC Batch No: V40387/V40380
The sample was diluted due to the nature of the sample matrix. Reporting limits have been adjusted accordingly.
Sample 89090 (SSV-1012-D) QC Batch No: V40387/V40380
The sample was diluted due to the nature of the sample matrix. Reporting limits have been adjusted accordingly.

Page 5 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-B
89088 Matrix:
11/13/2023 17:04
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
39100 E µg/m3 40.4 950Acetone 200 11/18/23 22:24 V40403ENM
<1.46 µg/m3 1.46 31.9Benzene 20 11/18/23 02:10 V40387ENM
<2.94 µg/m3 2.94 207Benzyl Chloride 20 11/18/23 02:10 V40387ENM
<3.00 µg/m3 3.00 67.0Bromodichloromethane 20 11/18/23 02:10 V40387ENM
<3.05 µg/m3 3.05 103Bromoform 20 11/18/23 02:10 V40387ENM
<2.30 µg/m3 2.30 38.8Bromomethane 20 11/18/23 02:10 V40387ENM
<6.53 µg/m3 6.53 22.11,3-Butadiene 20 11/18/23 02:10 V40387ENM
<1.22 µg/m3 1.22 125Carbon Disulfide 20 11/18/23 02:10 V40387ENM
<3.10 µg/m3 3.10 62.9Carbon Tetrachloride 20 11/18/23 02:10 V40387ENM
<2.14 µg/m3 2.14 46.0Chlorobenzene 20 11/18/23 02:10 V40387ENM
<4.16 µg/m3 4.16 85.2Chlorodibromomethane 20 11/18/23 02:10 V40387ENM
<3.28 µg/m3 3.28 26.4Chloroethane 20 11/18/23 02:10 V40387ENM
<1.73 µg/m3 1.73 48.8Chloroform 20 11/18/23 02:10 V40387ENM
<1.34 µg/m3 1.34 20.6Chloromethane 20 11/18/23 02:10 V40387ENM
<3.22 µg/m3 3.22 68.8Cyclohexane 20 11/18/23 02:10 V40387ENM
<3.02 µg/m3 3.02 76.81,2-Dibromoethane 20 11/18/23 02:10 V40387ENM
<1.92 µg/m3 1.92 60.11,2-Dichlorobenzene 20 11/18/23 02:10 V40387ENM
<3.48 µg/m3 3.48 2411,3-Dichlorobenzene 20 11/18/23 02:10 V40387ENM
<3.72 µg/m3 3.72 60.11,4-Dichlorobenzene 20 11/18/23 02:10 V40387ENM
<2.68 µg/m3 2.68 49.4Dichlorodifluoromethane 20 11/18/23 02:10 V40387ENM
<2.02 µg/m3 2.02 40.51,1-Dichloroethane 20 11/18/23 02:10 V40387ENM
<2.58 µg/m3 2.58 40.51,2-Dichloroethane 20 11/18/23 02:10 V40387ENM
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 6 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-B
89088 Matrix:
11/13/2023 17:04
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
<2.14 µg/m3 2.14 39.61,1-Dichloroethene 20 11/18/23 02:10 V40387ENM
<1.91 µg/m3 1.91 39.6cis-1,2-Dichloroethene 20 11/18/23 02:10 V40387ENM
<2.16 µg/m3 2.16 39.6trans-1,2-Dichloroethene 20 11/18/23 02:10 V40387ENM
<4.10 µg/m3 4.10 46.21,2-Dichloropropane 20 11/18/23 02:10 V40387ENM
<12.4 µg/m3 12.4 69.91,2-Dichlorotetrafluoroethane 20 11/18/23 02:10 V40387ENM
<3.56 µg/m3 3.56 45.4cis-1,3-Dichloropropene 20 11/18/23 02:10 V40387ENM
<3.56 µg/m3 3.56 45.4trans-1,3-Dichloropropene 20 11/18/23 02:10 V40387ENM
<8.69 µg/m3 8.69 36.01,4-Dioxane 20 11/18/23 02:10 V40387ENM
<2.72 µg/m3 2.72 36.0Ethyl Acetate 20 11/18/23 02:10 V40387ENM
<2.12 µg/m3 2.12 43.4Ethylbenzene 20 11/18/23 02:10 V40387ENM
<2.56 µg/m3 2.56 49.24-Ethyltoluene 20 11/18/23 02:10 V40387ENM
<11.2 µg/m3 11.2 76.61,1,2-Trichloro-1,2,2-trifluoroethane 20 11/18/23 02:10 V40387ENM
<2.86 µg/m3 2.86 41.0Heptane 20 11/18/23 02:10 V40387ENM
<6.62 µg/m3 6.62 107Hexachlorobutadiene 20 11/18/23 02:10 V40387ENM
<0.942 µg/m3 0.942 35.2n-Hexane 20 11/18/23 02:10 V40387ENM
<5.71 µg/m3 5.71 41.02-Hexanone 20 11/18/23 02:10 V40387ENM
90.9 J µg/m3 2.78 98.3Isopropyl Alcohol 20 11/18/23 02:10 V40387ENM
7710 µg/m3 44.8 295Methyl Ethyl Ketone (MEK)200 11/18/23 22:24 V40403ENM
<0.672 µg/m3 0.672 36.1Methyl tert-butyl ether (MTBE)20 11/18/23 02:10 V40387ENM
<2.42 µg/m3 2.42 41.04-Methyl-2-Pentanone 20 11/18/23 02:10 V40387ENM
<9.75 µg/m3 9.75 34.7Methylene Chloride 20 11/18/23 02:10 V40387ENM
<3.66 µg/m3 3.66 52.4Naphthalene 20 11/18/23 02:10 V40387ENM
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 7 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-B
89088 Matrix:
11/13/2023 17:04
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
<4.84 µg/m3 4.84 17.2Propene 20 11/18/23 02:10 V40387ENM
<2.48 µg/m3 2.48 42.6Styrene 20 11/18/23 02:10 V40387ENM
<2.08 µg/m3 2.08 68.61,1,2,2-Tetrachloroethane 20 11/18/23 02:10 V40387ENM
<3.62 µg/m3 3.62 67.8Tetrachloroethene 20 11/18/23 02:10 V40387ENM
51600 E µg/m3 21.4 295Tetrahydrofuran 200 11/18/23 22:24 V40403ENM
<1.80 µg/m3 1.80 37.7Toluene 20 11/18/23 02:10 V40387ENM
111 µg/m3 4.18 74.21,2,4-Trichlorobenzene 20 11/18/23 02:10 V40387ENM
<2.88 µg/m3 2.88 54.61,1,1-Trichloroethane 20 11/18/23 02:10 V40387ENM
<1.75 µg/m3 1.75 54.61,1,2-Trichloroethane 20 11/18/23 02:10 V40387ENM
<3.98 µg/m3 3.98 43.0Trichloroethene 20 11/18/23 02:10 V40387ENM
<2.60 µg/m3 2.60 56.2Trichlorofluoromethane 20 11/18/23 02:10 V40387ENM
<2.20 µg/m3 2.20 49.21,2,4-Trimethylbenzene 20 11/18/23 02:10 V40387ENM
<4.72 µg/m3 4.72 49.21,3,5-Trimethylbenzene 20 11/18/23 02:10 V40387ENM
<4.48 µg/m3 4.48 35.2Vinyl Acetate 20 11/18/23 02:10 V40387ENM
<2.54 µg/m3 2.54 25.6Vinyl Chloride 20 11/18/23 02:10 V40387ENM
<3.14 µg/m3 3.14 43.4o-Xylene 20 11/18/23 02:10 V40387ENM
7.99 J µg/m3 4.34 113m,p-Xylene 20 11/18/23 02:10 V40387ENM
7.99 J µg/m3 3.14 43.4Xylene (Total)20 11/18/23 02:10 V40387
Surrogate: 4-Bromofluorobenzene 125 Limits: 70-130%11/18/23 02:1020 ENM V40387
Surrogate: 4-Bromofluorobenzene 97.8 Limits: 70-130%11/18/23 22:24200 ENM V40403
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 8 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-DUP
89089 Matrix:
11/13/2023 0:00
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
38400 E µg/m3 40.4 950Acetone 200 11/18/23 23:01 V40403ENM
<1.46 µg/m3 1.46 31.9Benzene 20 11/18/23 02:47 V40387ENM
<2.94 µg/m3 2.94 207Benzyl Chloride 20 11/18/23 02:47 V40387ENM
<3.00 µg/m3 3.00 67.0Bromodichloromethane 20 11/18/23 02:47 V40387ENM
<3.05 µg/m3 3.05 103Bromoform 20 11/18/23 02:47 V40387ENM
<2.30 µg/m3 2.30 38.8Bromomethane 20 11/18/23 02:47 V40387ENM
<6.53 µg/m3 6.53 22.11,3-Butadiene 20 11/18/23 02:47 V40387ENM
<1.22 µg/m3 1.22 125Carbon Disulfide 20 11/18/23 02:47 V40387ENM
<3.10 µg/m3 3.10 62.9Carbon Tetrachloride 20 11/18/23 02:47 V40387ENM
<2.14 µg/m3 2.14 46.0Chlorobenzene 20 11/18/23 02:47 V40387ENM
<4.16 µg/m3 4.16 85.2Chlorodibromomethane 20 11/18/23 02:47 V40387ENM
<3.28 µg/m3 3.28 26.4Chloroethane 20 11/18/23 02:47 V40387ENM
<1.73 µg/m3 1.73 48.8Chloroform 20 11/18/23 02:47 V40387ENM
<1.34 µg/m3 1.34 20.6Chloromethane 20 11/18/23 02:47 V40387ENM
<3.22 µg/m3 3.22 68.8Cyclohexane 20 11/18/23 02:47 V40387ENM
<3.02 µg/m3 3.02 76.81,2-Dibromoethane 20 11/18/23 02:47 V40387ENM
<1.92 µg/m3 1.92 60.11,2-Dichlorobenzene 20 11/18/23 02:47 V40387ENM
<3.48 µg/m3 3.48 2411,3-Dichlorobenzene 20 11/18/23 02:47 V40387ENM
<3.72 µg/m3 3.72 60.11,4-Dichlorobenzene 20 11/18/23 02:47 V40387ENM
<2.68 µg/m3 2.68 49.4Dichlorodifluoromethane 20 11/18/23 02:47 V40387ENM
<2.02 µg/m3 2.02 40.51,1-Dichloroethane 20 11/18/23 02:47 V40387ENM
<2.58 µg/m3 2.58 40.51,2-Dichloroethane 20 11/18/23 02:47 V40387ENM
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 9 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-DUP
89089 Matrix:
11/13/2023 0:00
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
<2.14 µg/m3 2.14 39.61,1-Dichloroethene 20 11/18/23 02:47 V40387ENM
<1.91 µg/m3 1.91 39.6cis-1,2-Dichloroethene 20 11/18/23 02:47 V40387ENM
<2.16 µg/m3 2.16 39.6trans-1,2-Dichloroethene 20 11/18/23 02:47 V40387ENM
<4.10 µg/m3 4.10 46.21,2-Dichloropropane 20 11/18/23 02:47 V40387ENM
<12.4 µg/m3 12.4 69.91,2-Dichlorotetrafluoroethane 20 11/18/23 02:47 V40387ENM
<3.56 µg/m3 3.56 45.4cis-1,3-Dichloropropene 20 11/18/23 02:47 V40387ENM
<3.56 µg/m3 3.56 45.4trans-1,3-Dichloropropene 20 11/18/23 02:47 V40387ENM
<8.69 µg/m3 8.69 36.01,4-Dioxane 20 11/18/23 02:47 V40387ENM
<2.72 µg/m3 2.72 36.0Ethyl Acetate 20 11/18/23 02:47 V40387ENM
<2.12 µg/m3 2.12 43.4Ethylbenzene 20 11/18/23 02:47 V40387ENM
<2.56 µg/m3 2.56 49.24-Ethyltoluene 20 11/18/23 02:47 V40387ENM
<11.2 µg/m3 11.2 76.61,1,2-Trichloro-1,2,2-trifluoroethane 20 11/18/23 02:47 V40387ENM
<2.86 µg/m3 2.86 41.0Heptane 20 11/18/23 02:47 V40387ENM
<6.62 µg/m3 6.62 107Hexachlorobutadiene 20 11/18/23 02:47 V40387ENM
<0.942 µg/m3 0.942 35.2n-Hexane 20 11/18/23 02:47 V40387ENM
<5.71 µg/m3 5.71 41.02-Hexanone 20 11/18/23 02:47 V40387ENM
89.4 J µg/m3 2.78 98.3Isopropyl Alcohol 20 11/18/23 02:47 V40387ENM
7270 µg/m3 44.8 295Methyl Ethyl Ketone (MEK)200 11/18/23 23:01 V40403ENM
<0.672 µg/m3 0.672 36.1Methyl tert-butyl ether (MTBE)20 11/18/23 02:47 V40387ENM
<2.42 µg/m3 2.42 41.04-Methyl-2-Pentanone 20 11/18/23 02:47 V40387ENM
<9.75 µg/m3 9.75 34.7Methylene Chloride 20 11/18/23 02:47 V40387ENM
<3.66 µg/m3 3.66 52.4Naphthalene 20 11/18/23 02:47 V40387ENM
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 10 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-DUP
89089 Matrix:
11/13/2023 0:00
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
<4.84 µg/m3 4.84 17.2Propene 20 11/18/23 02:47 V40387ENM
<2.48 µg/m3 2.48 42.6Styrene 20 11/18/23 02:47 V40387ENM
<2.08 µg/m3 2.08 68.61,1,2,2-Tetrachloroethane 20 11/18/23 02:47 V40387ENM
<3.62 µg/m3 3.62 67.8Tetrachloroethene 20 11/18/23 02:47 V40387ENM
50000 E µg/m3 21.4 295Tetrahydrofuran 200 11/18/23 23:01 V40403ENM
<1.80 µg/m3 1.80 37.7Toluene 20 11/18/23 02:47 V40387ENM
85.6 µg/m3 4.18 74.21,2,4-Trichlorobenzene 20 11/18/23 02:47 V40387ENM
<2.88 µg/m3 2.88 54.61,1,1-Trichloroethane 20 11/18/23 02:47 V40387ENM
<1.75 µg/m3 1.75 54.61,1,2-Trichloroethane 20 11/18/23 02:47 V40387ENM
<3.98 µg/m3 3.98 43.0Trichloroethene 20 11/18/23 02:47 V40387ENM
<2.60 µg/m3 2.60 56.2Trichlorofluoromethane 20 11/18/23 02:47 V40387ENM
<2.20 µg/m3 2.20 49.21,2,4-Trimethylbenzene 20 11/18/23 02:47 V40387ENM
<4.72 µg/m3 4.72 49.21,3,5-Trimethylbenzene 20 11/18/23 02:47 V40387ENM
<4.48 µg/m3 4.48 35.2Vinyl Acetate 20 11/18/23 02:47 V40387ENM
<2.54 µg/m3 2.54 25.6Vinyl Chloride 20 11/18/23 02:47 V40387ENM
<3.14 µg/m3 3.14 43.4o-Xylene 20 11/18/23 02:47 V40387ENM
<4.34 µg/m3 4.34 113m,p-Xylene 20 11/18/23 02:47 V40387ENM
<3.14 µg/m3 3.14 43.4Xylene (Total)20 11/18/23 02:47 V40387
Surrogate: 4-Bromofluorobenzene 92.5 Limits: 70-130%11/18/23 02:4720 ENM V40387
Surrogate: 4-Bromofluorobenzene 98.6 Limits: 70-130%11/18/23 23:01200 ENM V40403
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 11 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-D
89090 Matrix:
11/13/2023 17:24
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
33600 E µg/m3 40.4 950Acetone 200 11/18/23 23:37 V40403ENM
<1.46 µg/m3 1.46 31.9Benzene 20 11/18/23 03:23 V40387ENM
<2.94 µg/m3 2.94 207Benzyl Chloride 20 11/18/23 03:23 V40387ENM
<3.00 µg/m3 3.00 67.0Bromodichloromethane 20 11/18/23 03:23 V40387ENM
<3.05 µg/m3 3.05 103Bromoform 20 11/18/23 03:23 V40387ENM
<2.30 µg/m3 2.30 38.8Bromomethane 20 11/18/23 03:23 V40387ENM
<6.53 µg/m3 6.53 22.11,3-Butadiene 20 11/18/23 03:23 V40387ENM
6.04 J µg/m3 1.22 125Carbon Disulfide 20 11/18/23 03:23 V40387ENM
<3.10 µg/m3 3.10 62.9Carbon Tetrachloride 20 11/18/23 03:23 V40387ENM
<2.14 µg/m3 2.14 46.0Chlorobenzene 20 11/18/23 03:23 V40387ENM
<4.16 µg/m3 4.16 85.2Chlorodibromomethane 20 11/18/23 03:23 V40387ENM
<3.28 µg/m3 3.28 26.4Chloroethane 20 11/18/23 03:23 V40387ENM
<1.73 µg/m3 1.73 48.8Chloroform 20 11/18/23 03:23 V40387ENM
13.1 J µg/m3 1.34 20.6Chloromethane 20 11/18/23 03:23 V40387ENM
<3.22 µg/m3 3.22 68.8Cyclohexane 20 11/18/23 03:23 V40387ENM
<3.02 µg/m3 3.02 76.81,2-Dibromoethane 20 11/18/23 03:23 V40387ENM
<1.92 µg/m3 1.92 60.11,2-Dichlorobenzene 20 11/18/23 03:23 V40387ENM
<3.48 µg/m3 3.48 2411,3-Dichlorobenzene 20 11/18/23 03:23 V40387ENM
<3.72 µg/m3 3.72 60.11,4-Dichlorobenzene 20 11/18/23 03:23 V40387ENM
<2.68 µg/m3 2.68 49.4Dichlorodifluoromethane 20 11/18/23 03:23 V40387ENM
<2.02 µg/m3 2.02 40.51,1-Dichloroethane 20 11/18/23 03:23 V40387ENM
<2.58 µg/m3 2.58 40.51,2-Dichloroethane 20 11/18/23 03:23 V40387ENM
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 12 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-D
89090 Matrix:
11/13/2023 17:24
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
<2.14 µg/m3 2.14 39.61,1-Dichloroethene 20 11/18/23 03:23 V40387ENM
<1.91 µg/m3 1.91 39.6cis-1,2-Dichloroethene 20 11/18/23 03:23 V40387ENM
<2.16 µg/m3 2.16 39.6trans-1,2-Dichloroethene 20 11/18/23 03:23 V40387ENM
<4.10 µg/m3 4.10 46.21,2-Dichloropropane 20 11/18/23 03:23 V40387ENM
<12.4 µg/m3 12.4 69.91,2-Dichlorotetrafluoroethane 20 11/18/23 03:23 V40387ENM
<3.56 µg/m3 3.56 45.4cis-1,3-Dichloropropene 20 11/18/23 03:23 V40387ENM
<3.56 µg/m3 3.56 45.4trans-1,3-Dichloropropene 20 11/18/23 03:23 V40387ENM
<8.69 µg/m3 8.69 36.01,4-Dioxane 20 11/18/23 03:23 V40387ENM
<2.72 µg/m3 2.72 36.0Ethyl Acetate 20 11/18/23 03:23 V40387ENM
<2.12 µg/m3 2.12 43.4Ethylbenzene 20 11/18/23 03:23 V40387ENM
<2.56 µg/m3 2.56 49.24-Ethyltoluene 20 11/18/23 03:23 V40387ENM
<11.2 µg/m3 11.2 76.61,1,2-Trichloro-1,2,2-trifluoroethane 20 11/18/23 03:23 V40387ENM
<2.86 µg/m3 2.86 41.0Heptane 20 11/18/23 03:23 V40387ENM
<6.62 µg/m3 6.62 107Hexachlorobutadiene 20 11/18/23 03:23 V40387ENM
<0.942 µg/m3 0.942 35.2n-Hexane 20 11/18/23 03:23 V40387ENM
<5.71 µg/m3 5.71 41.02-Hexanone 20 11/18/23 03:23 V40387ENM
101 µg/m3 2.78 98.3Isopropyl Alcohol 20 11/18/23 03:23 V40387ENM
1870 µg/m3 4.48 29.5Methyl Ethyl Ketone (MEK)20 11/18/23 03:23 V40387ENM
<0.672 µg/m3 0.672 36.1Methyl tert-butyl ether (MTBE)20 11/18/23 03:23 V40387ENM
<2.42 µg/m3 2.42 41.04-Methyl-2-Pentanone 20 11/18/23 03:23 V40387ENM
<9.75 µg/m3 9.75 34.7Methylene Chloride 20 11/18/23 03:23 V40387ENM
<3.66 µg/m3 3.66 52.4Naphthalene 20 11/18/23 03:23 V40387ENM
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 13 of 22
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
23-318-0001
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Josh Billiot
Charlotte
Received : 11/14/2023
NVR-019-004-D
Report Date : 11/21/2023
Sample ID :
Lab No :
Sampled:SSV-1012-D
89090 Matrix:
11/13/2023 17:24
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V40380 11/17/23 09:00 V40402 11/18/23 09:00
<4.84 µg/m3 4.84 17.2Propene 20 11/18/23 03:23 V40387ENM
<2.48 µg/m3 2.48 42.6Styrene 20 11/18/23 03:23 V40387ENM
<2.08 µg/m3 2.08 68.61,1,2,2-Tetrachloroethane 20 11/18/23 03:23 V40387ENM
<3.62 µg/m3 3.62 67.8Tetrachloroethene 20 11/18/23 03:23 V40387ENM
113000 E µg/m3 21.4 295Tetrahydrofuran 200 11/18/23 23:37 V40403ENM
184 µg/m3 1.80 37.7Toluene 20 11/18/23 03:23 V40387ENM
27.8 J µg/m3 4.18 74.21,2,4-Trichlorobenzene 20 11/18/23 03:23 V40387ENM
<2.88 µg/m3 2.88 54.61,1,1-Trichloroethane 20 11/18/23 03:23 V40387ENM
<1.75 µg/m3 1.75 54.61,1,2-Trichloroethane 20 11/18/23 03:23 V40387ENM
<3.98 µg/m3 3.98 43.0Trichloroethene 20 11/18/23 03:23 V40387ENM
<2.60 µg/m3 2.60 56.2Trichlorofluoromethane 20 11/18/23 03:23 V40387ENM
<2.20 µg/m3 2.20 49.21,2,4-Trimethylbenzene 20 11/18/23 03:23 V40387ENM
<4.72 µg/m3 4.72 49.21,3,5-Trimethylbenzene 20 11/18/23 03:23 V40387ENM
<4.48 µg/m3 4.48 35.2Vinyl Acetate 20 11/18/23 03:23 V40387ENM
<2.54 µg/m3 2.54 25.6Vinyl Chloride 20 11/18/23 03:23 V40387ENM
<3.14 µg/m3 3.14 43.4o-Xylene 20 11/18/23 03:23 V40387ENM
7.82 J µg/m3 4.34 113m,p-Xylene 20 11/18/23 03:23 V40387ENM
7.82 J µg/m3 3.14 43.4Xylene (Total)20 11/18/23 03:23 V40387
Surrogate: 4-Bromofluorobenzene 87.4 Limits: 70-130%11/18/23 03:2320 ENM V40387
Surrogate: 4-Bromofluorobenzene 114 Limits: 70-130%11/18/23 23:37200 ENM V40403
Qualifiers/
Definitions
Result above calibration rangeEDilution FactorDF
Method Quantitation LimitMQLEstimated valueJ
Page 14 of 22
Quality Control Data
23-318-0001Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V40387QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V40380
Associated Lab Samples: 89088, 89089, 89090
LRB-V40380 Matrix: AIRLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
11/17/23 10:201.600.073<0.073µg/m3Benzene
11/17/23 10:2010.40.147<0.147µg/m3Benzyl Chloride
11/17/23 10:203.350.150<0.150µg/m3Bromodichloromethane
11/17/23 10:205.170.153<0.153µg/m3Bromoform
11/17/23 10:201.940.115<0.115µg/m3Bromomethane
11/17/23 10:201.110.328<0.328µg/m31,3-Butadiene
11/17/23 10:206.230.060<0.060µg/m3Carbon Disulfide
11/17/23 10:203.150.155<0.155µg/m3Carbon Tetrachloride
11/17/23 10:202.300.107<0.107µg/m3Chlorobenzene
11/17/23 10:204.260.208<0.208µg/m3Chlorodibromomethane
11/17/23 10:201.320.164<0.164µg/m3Chloroethane
11/17/23 10:202.440.086<0.086µg/m3Chloroform
11/17/23 10:201.030.067<0.067µg/m3Chloromethane
11/17/23 10:203.440.161<0.161µg/m3Cyclohexane
11/17/23 10:203.840.151<0.151µg/m31,2-Dibromoethane
11/17/23 10:203.010.096<0.096µg/m31,2-Dichlorobenzene
11/17/23 10:2012.00.174<0.174µg/m31,3-Dichlorobenzene
11/17/23 10:203.010.186<0.186µg/m31,4-Dichlorobenzene
11/17/23 10:202.470.134<0.134µg/m3Dichlorodifluoromethane
11/17/23 10:202.020.101<0.101µg/m31,1-Dichloroethane
11/17/23 10:202.020.129<0.129µg/m31,2-Dichloroethane
11/17/23 10:201.980.107<0.107µg/m31,1-Dichloroethene
11/17/23 10:201.980.095<0.095µg/m3cis-1,2-Dichloroethene
11/17/23 10:201.980.108<0.108µg/m3trans-1,2-Dichloroethene
11/17/23 10:202.310.205<0.205µg/m31,2-Dichloropropane
11/17/23 10:203.500.622<0.622µg/m31,2-Dichlorotetrafluoroethane
11/17/23 10:202.270.178<0.178µg/m3cis-1,3-Dichloropropene
Page 1 of 6Date:11/21/2023 04:03 PM
Page 15 of 22
Quality Control Data
23-318-0001Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V40387QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V40380
Associated Lab Samples: 89088, 89089, 89090
LRB-V40380 Matrix: AIRLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
11/17/23 10:202.270.178<0.178µg/m3trans-1,3-Dichloropropene
11/17/23 10:201.800.435<0.435µg/m31,4-Dioxane
11/17/23 10:201.800.136<0.136µg/m3Ethyl Acetate
11/17/23 10:202.170.106<0.106µg/m3Ethylbenzene
11/17/23 10:202.460.128<0.128µg/m34-Ethyltoluene
11/17/23 10:203.830.561<0.561µg/m31,1,2-Trichloro-1,2,2-trifluoroethane
11/17/23 10:202.050.143<0.143µg/m3Heptane
11/17/23 10:205.330.330<0.330µg/m3Hexachlorobutadiene
11/17/23 10:201.760.047<0.047µg/m3n-Hexane
11/17/23 10:202.050.285<0.285µg/m32-Hexanone
11/17/23 10:204.920.1392.29µg/m3Isopropyl Alcohol
11/17/23 10:201.470.224<0.224µg/m3Methyl Ethyl Ketone (MEK)
11/17/23 10:201.800.033<0.033µg/m3Methyl tert-butyl ether (MTBE)
11/17/23 10:202.050.121<0.121µg/m34-Methyl-2-Pentanone
11/17/23 10:201.740.488<0.488µg/m3Methylene Chloride
11/17/23 10:202.620.183<0.183µg/m3Naphthalene
11/17/23 10:200.8600.242<0.242µg/m3Propene
11/17/23 10:202.130.124<0.124µg/m3Styrene
11/17/23 10:203.430.104<0.104µg/m31,1,2,2-Tetrachloroethane
11/17/23 10:203.390.181<0.181µg/m3Tetrachloroethene
11/17/23 10:201.880.090<0.090µg/m3Toluene
11/17/23 10:203.710.209<0.209µg/m31,2,4-Trichlorobenzene
11/17/23 10:202.730.144<0.144µg/m31,1,1-Trichloroethane
11/17/23 10:202.730.087<0.087µg/m31,1,2-Trichloroethane
11/17/23 10:202.150.199<0.199µg/m3Trichloroethene
11/17/23 10:202.810.130<0.130µg/m3Trichlorofluoromethane
11/17/23 10:202.460.110<0.110µg/m31,2,4-Trimethylbenzene
Page 2 of 6Date:11/21/2023 04:03 PM
Page 16 of 22
Quality Control Data
23-318-0001Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V40387QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V40380
Associated Lab Samples: 89088, 89089, 89090
LRB-V40380 Matrix: AIRLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
11/17/23 10:202.460.236<0.236µg/m31,3,5-Trimethylbenzene
11/17/23 10:201.760.224<0.224µg/m3Vinyl Acetate
11/17/23 10:201.280.127<0.127µg/m3Vinyl Chloride
11/17/23 10:202.170.157<0.157µg/m3o-Xylene
11/17/23 10:205.650.217<0.217µg/m3m,p-Xylene
11/17/23 10:204-Bromofluorobenzene (S)95.5 70-130
LCS-V40380Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
10116.116.0µg/m3Benzene 70-130
11329.225.9µg/m3Benzyl Chloride 70-130
99.433.333.5µg/m3Bromodichloromethane 70-130
99.251.351.7µg/m3Bromoform 70-130
10821.019.4µg/m3Bromomethane 70-130
10311.411.1µg/m31,3-Butadiene 70-130
11217.515.6µg/m3Carbon Disulfide 70-130
98.431.031.5µg/m3Carbon Tetrachloride 70-130
10123.223.0µg/m3Chlorobenzene 70-130
10142.942.6µg/m3Chlorodibromomethane 70-130
10614.013.2µg/m3Chloroethane 70-130
10225.024.4µg/m3Chloroform 70-130
10811.110.3µg/m3Chloromethane 70-130
10117.317.2µg/m3Cyclohexane 70-130
10239.238.4µg/m31,2-Dibromoethane 70-130
10932.930.1µg/m31,2-Dichlorobenzene 70-130
11033.130.1µg/m31,3-Dichlorobenzene 70-130
Page 3 of 6Date:11/21/2023 04:03 PM
Page 17 of 22
Quality Control Data
23-318-0001Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V40387QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V40380
LCS-V40380Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
11133.330.1µg/m31,4-Dichlorobenzene 70-130
10726.424.7µg/m3Dichlorodifluoromethane 70-130
10922.020.2µg/m31,1-Dichloroethane 70-130
10120.520.2µg/m31,2-Dichloroethane 70-130
11021.719.8µg/m31,1-Dichloroethene 70-130
10921.619.8µg/m3cis-1,2-Dichloroethene 70-130
10821.419.8µg/m3trans-1,2-Dichloroethene 70-130
99.523.023.1µg/m31,2-Dichloropropane 70-130
10938.035.0µg/m31,2-Dichlorotetrafluoroethane 70-130
10123.022.7µg/m3cis-1,3-Dichloropropene 70-130
10022.822.7µg/m3trans-1,3-Dichloropropene 70-130
95.017.118.0µg/m31,4-Dioxane 70-130
10118.218.0µg/m3Ethyl Acetate 70-130
93.020.221.7µg/m3Ethylbenzene 70-130
10525.924.6µg/m34-Ethyltoluene 70-130
10841.238.3µg/m31,1,2-Trichloro-1,2,2-trifluoroethane 70-130
97.520.020.5µg/m3Heptane 70-130
90.948.553.3µg/m3Hexachlorobutadiene 70-130
10418.317.6µg/m3n-Hexane 70-130
96.519.820.5µg/m32-Hexanone 70-130
10312.712.3µg/m3Isopropyl Alcohol 70-130
10014.814.8µg/m3Methyl Ethyl Ketone (MEK)70-130
10719.218.0µg/m3Methyl tert-butyl ether (MTBE)70-130
94.619.420.5µg/m34-Methyl-2-Pentanone 70-130
10618.417.4µg/m3Methylene Chloride 70-130
11129.126.2µg/m3Naphthalene 70-130
99.18.548.61µg/m3Propene 70-130
Page 4 of 6Date:11/21/2023 04:03 PM
Page 18 of 22
Quality Control Data
23-318-0001Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V40387QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V40380
LCS-V40380Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
10422.121.3µg/m3Styrene 70-130
10536.134.3µg/m31,1,2,2-Tetrachloroethane 70-130
97.633.133.9µg/m3Tetrachloroethene 70-130
98.418.518.8µg/m3Toluene 70-130
10739.837.1µg/m31,2,4-Trichlorobenzene 70-130
99.227.127.3µg/m31,1,1-Trichloroethane 70-130
10328.227.3µg/m31,1,2-Trichloroethane 70-130
97.026.126.9µg/m3Trichloroethene 70-130
10830.328.1µg/m3Trichlorofluoromethane 70-130
10926.824.6µg/m31,2,4-Trimethylbenzene 70-130
10726.424.6µg/m31,3,5-Trimethylbenzene 70-130
10919.117.6µg/m3Vinyl Acetate 70-130
10613.612.8µg/m3Vinyl Chloride 70-130
10322.321.7µg/m3o-Xylene 70-130
10244.143.4µg/m3m,p-Xylene 70-130
1014-Bromofluorobenzene (S)70-130
Page 5 of 6Date:11/21/2023 04:03 PM
Page 19 of 22
Quality Control Data
23-318-0001Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V40403QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V40402
Associated Lab Samples: 89088, 89089, 89090
LRB-V40402 Matrix: AIRLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
11/18/23 14:484.750.202<0.202µg/m3Acetone
11/18/23 14:481.470.224<0.224µg/m3Methyl Ethyl Ketone (MEK)
11/18/23 14:481.470.107<0.107µg/m3Tetrahydrofuran
11/18/23 14:484-Bromofluorobenzene (S)96.0 70-130
LCS-V40402Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
10812.811.9µg/m3Acetone 70-130
10315.214.8µg/m3Methyl Ethyl Ketone (MEK)70-130
10114.914.7µg/m3Tetrahydrofuran 70-130
1014-Bromofluorobenzene (S)70-130
Page 6 of 6Date:11/21/2023 04:03 PM
Page 20 of 22
Fed Ex
UPS
US Postal
Client
Lab
Courier
Other :
Shipment Receipt Form
Customer Number:
Customer Name:
Report Number:23-318-0001
Hart & Hickman (Charlotte)
01102
Shipping Method
Shipping container/cooler uncompromised?
Thermometer ID:N/A
Chain of Custody (COC) present?Yes No
Yes No Not Present
Yes No Not Present
Yes No
COC agrees with sample label(s)? Yes No
COC properly completed
Samples in proper containers?
Sample containers intact?
Sufficient sample volume for indicated test(s)?
All samples received within holding time?
Cooler temperature in compliance?
Yes No
Yes No
Yes No
Yes No
Yes No
Yes NoCooler/Samples arrived at the laboratory on ice.
Samples were considered acceptable as cooling
process had begun.
Yes No
Yes No N/A
Yes No N/A
Yes No N/ASoil VOA method 5035 – compliance criteria met
Water - Sample containers properly preserved
Water - VOA vials free of headspace Yes No N/A
Trip Blanks received with VOAs
Low concentration EnCore samplers (48 hr)
High concentration pre-weighed (methanol -14 d) Low conc pre-weighed vials (Sod Bis -14 d)
High concentration container (48 hr)
Custody seals intact on shipping container/cooler?
Custody seals intact on sample bottles?
Number of coolers/boxes received
Yes No
1
Signature:Angelo Norvell Date & Time:11/14/2023 09:58:23
Special precautions or instructions included?
Comments:
Page 21 of 22
Page 22 of 22

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.

5/14/2024
Hart & Hickman (Charlotte) Trinh Desa
2923 South Tryon St. Ste 100 Charlotte, NC, 28203
Ref: Analytical Testing
Lab Report Number: 24-121-0011 Client Project Description: NVR-019-004-D
Dear Trinh Desa:
Waypoint Analytical, LLC (Charlotte) received sample(s) on 4/30/2024 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,
Angela D Overcash Senior Project Manager
Page 1 of 23
Certification Summary
Laboratory ID: WP CNC: Waypoint Analytical Carolina, Inc. (C), Charlotte, NC
State Program Lab ID Expiration Date
07/31/202437735State ProgramNorth Carolina
12/31/2024402State ProgramNorth Carolina
07/31/202499012State ProgramSouth Carolina
12/31/202499012State ProgramSouth Carolina
Page 1 of 1 00016/24-121-0011
Page 2 of 23
Report Number:
Sample Summary Table
Client Project Description:
24-121-0011
NVR-019-004-D
Lab No Client Sample ID Matrix Date Collected Date Received
04/30/2024 13:20Air 92297 SS-1012-B 04/30/2024 14:24
04/30/2024Air 92298 SS-1012-DUP 04/30/2024 14:24
04/30/2024 13:48Air 92299 SS-1012-D 04/30/2024 14:24
Page 3 of 23
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
24-121-0011
Report Limit
Project:NVR-019-004-D
V 92297SS-1012-B
627 05/10/2024 22:31TO-15 Acetone µg/m3 4.04
J0.277 05/11/2024 20:59TO-15 Benzene µg/m3 0.073
JB0.249 05/11/2024 20:59TO-15 Carbon Disulfide µg/m3 0.060
J1.24 05/11/2024 20:59TO-15 Chloroform µg/m3 0.086
J1.91 05/11/2024 20:59TO-15 Cyclohexane µg/m3 0.161
J2.35 05/11/2024 20:59TO-15 Dichlorodifluoromethane µg/m3 0.134
J0.395 05/11/2024 20:59TO-15 Ethylbenzene µg/m3 0.106
JB1.77 05/11/2024 20:59TO-15 Isopropyl Alcohol µg/m3 0.139
176 05/10/2024 22:31TO-15 Methyl Ethyl Ketone (MEK)µg/m3 4.48
J1.04 05/11/2024 20:59TO-15 Tetrachloroethene µg/m3 0.181
1230 05/10/2024 22:31TO-15 Tetrahydrofuran µg/m3 2.14
2.49 05/11/2024 20:59TO-15 Toluene µg/m3 0.090
J1.75 05/11/2024 20:59TO-15 Trichlorofluoromethane µg/m3 0.130
J1.04 05/11/2024 20:59TO-15 1,2,4-Trimethylbenzene µg/m3 0.110
J0.403 05/11/2024 20:59TO-15 1,3,5-Trimethylbenzene µg/m3 0.236
J0.981 05/11/2024 20:59TO-15 o-Xylene µg/m3 0.157
J1.77 05/11/2024 20:59TO-15 m,p-Xylene µg/m3 0.217
J2.75 05/11/2024 20:59TO-15 Xylene (Total)µg/m3 0.157
V 92298SS-1012-DUP
626 05/10/2024 23:08TO-15 Acetone µg/m3 4.04
J0.469 05/11/2024 21:53TO-15 Benzene µg/m3 0.073
JB0.713 05/11/2024 21:53TO-15 Carbon Disulfide µg/m3 0.060
J1.20 05/11/2024 21:53TO-15 Chloroform µg/m3 0.086
J0.526 05/11/2024 21:53TO-15 Chloromethane µg/m3 0.067
J2.42 05/11/2024 21:53TO-15 Dichlorodifluoromethane µg/m3 0.134
J0.425 05/11/2024 21:53TO-15 Ethylbenzene µg/m3 0.106
JB4.63 05/11/2024 21:53TO-15 Isopropyl Alcohol µg/m3 0.139
177 05/10/2024 23:08TO-15 Methyl Ethyl Ketone (MEK)µg/m3 4.48
J0.778 05/11/2024 21:53TO-15 Methylene Chloride µg/m3 0.488
J1.02 05/11/2024 21:53TO-15 Tetrachloroethene µg/m3 0.181
1230 05/10/2024 23:08TO-15 Tetrahydrofuran µg/m3 2.14
2.72 05/11/2024 21:53TO-15 Toluene µg/m3 0.090
J1.88 05/11/2024 21:53TO-15 Trichlorofluoromethane µg/m3 0.130
J1.07 05/11/2024 21:53TO-15 1,2,4-Trimethylbenzene µg/m3 0.110
J0.976 05/11/2024 21:53TO-15 o-Xylene µg/m3 0.157
J1.83 05/11/2024 21:53TO-15 m,p-Xylene µg/m3 0.217
Page 4 of 23
Summary of Detected Analytes
QualifiersAnalyzedUnitsResult
Report Number:
Client Sample ID
Method Parameters
Lab Sample ID
24-121-0011
Report Limit
Project:NVR-019-004-D
V 92298SS-1012-DUP
J2.81 05/11/2024 21:53TO-15 Xylene (Total)µg/m3 0.157
V 92299SS-1012-D
832 05/10/2024 23:45TO-15 Acetone µg/m3 4.04
J0.456 05/11/2024 22:46TO-15 Benzene µg/m3 0.073
JB0.697 05/11/2024 22:46TO-15 Carbon Disulfide µg/m3 0.060
J0.912 05/11/2024 22:46TO-15 Chloroform µg/m3 0.086
J0.408 05/11/2024 22:46TO-15 Chloromethane µg/m3 0.067
J2.37 05/11/2024 22:46TO-15 Dichlorodifluoromethane µg/m3 0.134
1.84 05/11/2024 22:46TO-15 Ethyl Acetate µg/m3 0.136
J0.577 05/11/2024 22:46TO-15 Ethylbenzene µg/m3 0.106
J0.403 05/11/2024 22:46TO-15 4-Ethyltoluene µg/m3 0.128
21.8 05/11/2024 22:46TO-15 Isopropyl Alcohol µg/m3 0.139
231 05/10/2024 23:45TO-15 Methyl Ethyl Ketone (MEK)µg/m3 4.48
J0.531 05/11/2024 22:46TO-15 Methylene Chloride µg/m3 0.488
J0.353 05/11/2024 22:46TO-15 Styrene µg/m3 0.124
J1.26 05/11/2024 22:46TO-15 Tetrachloroethene µg/m3 0.181
2410 05/10/2024 23:45TO-15 Tetrahydrofuran µg/m3 2.14
2.50 05/11/2024 22:46TO-15 Toluene µg/m3 0.090
J1.80 05/11/2024 22:46TO-15 Trichlorofluoromethane µg/m3 0.130
J1.66 05/11/2024 22:46TO-15 1,2,4-Trimethylbenzene µg/m3 0.110
J0.565 05/11/2024 22:46TO-15 1,3,5-Trimethylbenzene µg/m3 0.236
J1.35 05/11/2024 22:46TO-15 o-Xylene µg/m3 0.157
J2.47 05/11/2024 22:46TO-15 m,p-Xylene µg/m3 0.217
J3.82 05/11/2024 22:46TO-15 Xylene (Total)µg/m3 0.157
Page 5 of 23

Client: Hart & Hickman (Charlotte) CASE NARRATIVE
Project: NVR-019-004-D Lab Report Number: 24-121-0011
Date: 5/14/2024
Volatile Organic Compounds in Air- GC/MS Method TO-15 Analyte: Carbon Disulfide QC Batch No: V47235/V47233
Target analyte(s) was identified in the method blank associated with this project, below the Method Quantitation Limit. Per laboratory protocol any associated affected sample result is flagged "B" to indicate that it was detected
in the method blank.
Analyte: Isopropyl alcohol QC Batch No: V47235/V47233
Target analyte(s) was identified in the method blank associated with this project, below the Method Quantitation Limit. Per laboratory protocol any associated affected sample result is flagged "B" to indicate that it was detected
in the method blank.

Page 6 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-B
92297 Matrix:
4/30/2024 13:20
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
627 µg/m3 4.04 95.0Acetone 20 05/10/24 22:31 V47252ENM
0.277 J µg/m3 0.073 1.60Benzene 1 05/11/24 20:59 V47235ENM
<0.147 µg/m3 0.147 10.4Benzyl Chloride 1 05/11/24 20:59 V47235ENM
<0.150 µg/m3 0.150 3.35Bromodichloromethane 1 05/11/24 20:59 V47235ENM
<0.153 µg/m3 0.153 5.17Bromoform 1 05/11/24 20:59 V47235ENM
<0.115 µg/m3 0.115 1.94Bromomethane 1 05/11/24 20:59 V47235ENM
<0.328 µg/m3 0.328 1.111,3-Butadiene 1 05/11/24 20:59 V47235ENM
0.249 JB µg/m3 0.060 6.23Carbon Disulfide 1 05/11/24 20:59 V47235ENM
<0.155 µg/m3 0.155 3.15Carbon Tetrachloride 1 05/11/24 20:59 V47235ENM
<0.107 µg/m3 0.107 2.30Chlorobenzene 1 05/11/24 20:59 V47235ENM
<0.208 µg/m3 0.208 4.26Chlorodibromomethane 1 05/11/24 20:59 V47235ENM
<0.164 µg/m3 0.164 1.32Chloroethane 1 05/11/24 20:59 V47235ENM
1.24 J µg/m3 0.086 2.44Chloroform 1 05/11/24 20:59 V47235ENM
<0.067 µg/m3 0.067 1.03Chloromethane 1 05/11/24 20:59 V47235ENM
1.91 J µg/m3 0.161 3.44Cyclohexane 1 05/11/24 20:59 V47235ENM
<0.151 µg/m3 0.151 3.841,2-Dibromoethane 1 05/11/24 20:59 V47235ENM
<0.096 µg/m3 0.096 3.011,2-Dichlorobenzene 1 05/11/24 20:59 V47235ENM
<0.174 µg/m3 0.174 12.01,3-Dichlorobenzene 1 05/11/24 20:59 V47235ENM
<0.186 µg/m3 0.186 3.011,4-Dichlorobenzene 1 05/11/24 20:59 V47235ENM
2.35 J µg/m3 0.134 2.47Dichlorodifluoromethane 1 05/11/24 20:59 V47235ENM
<0.101 µg/m3 0.101 2.021,1-Dichloroethane 1 05/11/24 20:59 V47235ENM
<0.129 µg/m3 0.129 2.021,2-Dichloroethane 1 05/11/24 20:59 V47235ENM
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 7 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-B
92297 Matrix:
4/30/2024 13:20
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
<0.107 µg/m3 0.107 1.981,1-Dichloroethene 1 05/11/24 20:59 V47235ENM
<0.095 µg/m3 0.095 1.98cis-1,2-Dichloroethene 1 05/11/24 20:59 V47235ENM
<0.108 µg/m3 0.108 1.98trans-1,2-Dichloroethene 1 05/11/24 20:59 V47235ENM
<0.205 µg/m3 0.205 2.311,2-Dichloropropane 1 05/11/24 20:59 V47235ENM
<0.622 µg/m3 0.622 3.501,2-Dichlorotetrafluoroethane 1 05/11/24 20:59 V47235ENM
<0.178 µg/m3 0.178 2.27cis-1,3-Dichloropropene 1 05/11/24 20:59 V47235ENM
<0.178 µg/m3 0.178 2.27trans-1,3-Dichloropropene 1 05/11/24 20:59 V47235ENM
<0.435 µg/m3 0.435 1.801,4-Dioxane 1 05/11/24 20:59 V47235ENM
<0.136 µg/m3 0.136 1.80Ethyl Acetate 1 05/11/24 20:59 V47235ENM
0.395 J µg/m3 0.106 2.17Ethylbenzene 1 05/11/24 20:59 V47235ENM
<0.128 µg/m3 0.128 2.464-Ethyltoluene 1 05/11/24 20:59 V47235ENM
<0.561 µg/m3 0.561 3.831,1,2-Trichloro-1,2,2-trifluoroethane 1 05/11/24 20:59 V47235ENM
<0.143 µg/m3 0.143 2.05Heptane 1 05/11/24 20:59 V47235ENM
<0.330 µg/m3 0.330 5.33Hexachlorobutadiene 1 05/11/24 20:59 V47235ENM
<0.047 µg/m3 0.047 1.76n-Hexane 1 05/11/24 20:59 V47235ENM
<0.285 µg/m3 0.285 2.052-Hexanone 1 05/11/24 20:59 V47235ENM
1.77 JB µg/m3 0.139 4.92Isopropyl Alcohol 1 05/11/24 20:59 V47235ENM
176 µg/m3 4.48 29.5Methyl Ethyl Ketone (MEK)20 05/10/24 22:31 V47252ENM
<0.033 µg/m3 0.033 1.80Methyl tert-butyl ether (MTBE)1 05/11/24 20:59 V47235ENM
<0.121 µg/m3 0.121 2.054-Methyl-2-Pentanone 1 05/11/24 20:59 V47235ENM
<0.488 µg/m3 0.488 1.74Methylene Chloride 1 05/11/24 20:59 V47235ENM
<0.183 µg/m3 0.183 2.62Naphthalene 1 05/11/24 20:59 V47235ENM
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 8 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-B
92297 Matrix:
4/30/2024 13:20
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
<0.242 µg/m3 0.242 0.860Propene 1 05/11/24 20:59 V47235ENM
<0.124 µg/m3 0.124 2.13Styrene 1 05/11/24 20:59 V47235ENM
<0.104 µg/m3 0.104 3.431,1,2,2-Tetrachloroethane 1 05/11/24 20:59 V47235ENM
1.04 J µg/m3 0.181 3.39Tetrachloroethene 1 05/11/24 20:59 V47235ENM
1230 µg/m3 2.14 29.5Tetrahydrofuran 20 05/10/24 22:31 V47252ENM
2.49 µg/m3 0.090 1.88Toluene 1 05/11/24 20:59 V47235ENM
<0.209 µg/m3 0.209 3.711,2,4-Trichlorobenzene 1 05/11/24 20:59 V47235ENM
<0.144 µg/m3 0.144 2.731,1,1-Trichloroethane 1 05/11/24 20:59 V47235ENM
<0.087 µg/m3 0.087 2.731,1,2-Trichloroethane 1 05/11/24 20:59 V47235ENM
<0.199 µg/m3 0.199 2.15Trichloroethene 1 05/11/24 20:59 V47235ENM
1.75 J µg/m3 0.130 2.81Trichlorofluoromethane 1 05/11/24 20:59 V47235ENM
1.04 J µg/m3 0.110 2.461,2,4-Trimethylbenzene 1 05/11/24 20:59 V47235ENM
0.403 J µg/m3 0.236 2.461,3,5-Trimethylbenzene 1 05/11/24 20:59 V47235ENM
<0.224 µg/m3 0.224 1.76Vinyl Acetate 1 05/11/24 20:59 V47235ENM
<0.127 µg/m3 0.127 1.28Vinyl Chloride 1 05/11/24 20:59 V47235ENM
0.981 J µg/m3 0.157 2.17o-Xylene 1 05/11/24 20:59 V47235ENM
1.77 J µg/m3 0.217 5.65m,p-Xylene 1 05/11/24 20:59 V47235ENM
2.75 J µg/m3 0.157 2.17Xylene (Total)1 05/11/24 20:59 V47235
Surrogate: 4-Bromofluorobenzene 103 Limits: 70-130%05/11/24 20:591 ENM V47235
Surrogate: 4-Bromofluorobenzene 98.6 Limits: 70-130%05/10/24 22:3120 ENM V47252
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 9 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-DUP
92298 Matrix:
4/30/2024 0:00
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
626 µg/m3 4.04 95.0Acetone 20 05/10/24 23:08 V47252ENM
0.469 J µg/m3 0.073 1.60Benzene 1 05/11/24 21:53 V47235ENM
<0.147 µg/m3 0.147 10.4Benzyl Chloride 1 05/11/24 21:53 V47235ENM
<0.150 µg/m3 0.150 3.35Bromodichloromethane 1 05/11/24 21:53 V47235ENM
<0.153 µg/m3 0.153 5.17Bromoform 1 05/11/24 21:53 V47235ENM
<0.115 µg/m3 0.115 1.94Bromomethane 1 05/11/24 21:53 V47235ENM
<0.328 µg/m3 0.328 1.111,3-Butadiene 1 05/11/24 21:53 V47235ENM
0.713 JB µg/m3 0.060 6.23Carbon Disulfide 1 05/11/24 21:53 V47235ENM
<0.155 µg/m3 0.155 3.15Carbon Tetrachloride 1 05/11/24 21:53 V47235ENM
<0.107 µg/m3 0.107 2.30Chlorobenzene 1 05/11/24 21:53 V47235ENM
<0.208 µg/m3 0.208 4.26Chlorodibromomethane 1 05/11/24 21:53 V47235ENM
<0.164 µg/m3 0.164 1.32Chloroethane 1 05/11/24 21:53 V47235ENM
1.20 J µg/m3 0.086 2.44Chloroform 1 05/11/24 21:53 V47235ENM
0.526 J µg/m3 0.067 1.03Chloromethane 1 05/11/24 21:53 V47235ENM
<0.161 µg/m3 0.161 3.44Cyclohexane 1 05/11/24 21:53 V47235ENM
<0.151 µg/m3 0.151 3.841,2-Dibromoethane 1 05/11/24 21:53 V47235ENM
<0.096 µg/m3 0.096 3.011,2-Dichlorobenzene 1 05/11/24 21:53 V47235ENM
<0.174 µg/m3 0.174 12.01,3-Dichlorobenzene 1 05/11/24 21:53 V47235ENM
<0.186 µg/m3 0.186 3.011,4-Dichlorobenzene 1 05/11/24 21:53 V47235ENM
2.42 J µg/m3 0.134 2.47Dichlorodifluoromethane 1 05/11/24 21:53 V47235ENM
<0.101 µg/m3 0.101 2.021,1-Dichloroethane 1 05/11/24 21:53 V47235ENM
<0.129 µg/m3 0.129 2.021,2-Dichloroethane 1 05/11/24 21:53 V47235ENM
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 10 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-DUP
92298 Matrix:
4/30/2024 0:00
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
<0.107 µg/m3 0.107 1.981,1-Dichloroethene 1 05/11/24 21:53 V47235ENM
<0.095 µg/m3 0.095 1.98cis-1,2-Dichloroethene 1 05/11/24 21:53 V47235ENM
<0.108 µg/m3 0.108 1.98trans-1,2-Dichloroethene 1 05/11/24 21:53 V47235ENM
<0.205 µg/m3 0.205 2.311,2-Dichloropropane 1 05/11/24 21:53 V47235ENM
<0.622 µg/m3 0.622 3.501,2-Dichlorotetrafluoroethane 1 05/11/24 21:53 V47235ENM
<0.178 µg/m3 0.178 2.27cis-1,3-Dichloropropene 1 05/11/24 21:53 V47235ENM
<0.178 µg/m3 0.178 2.27trans-1,3-Dichloropropene 1 05/11/24 21:53 V47235ENM
<0.435 µg/m3 0.435 1.801,4-Dioxane 1 05/11/24 21:53 V47235ENM
<0.136 µg/m3 0.136 1.80Ethyl Acetate 1 05/11/24 21:53 V47235ENM
0.425 J µg/m3 0.106 2.17Ethylbenzene 1 05/11/24 21:53 V47235ENM
<0.128 µg/m3 0.128 2.464-Ethyltoluene 1 05/11/24 21:53 V47235ENM
<0.561 µg/m3 0.561 3.831,1,2-Trichloro-1,2,2-trifluoroethane 1 05/11/24 21:53 V47235ENM
<0.143 µg/m3 0.143 2.05Heptane 1 05/11/24 21:53 V47235ENM
<0.330 µg/m3 0.330 5.33Hexachlorobutadiene 1 05/11/24 21:53 V47235ENM
<0.047 µg/m3 0.047 1.76n-Hexane 1 05/11/24 21:53 V47235ENM
<0.285 µg/m3 0.285 2.052-Hexanone 1 05/11/24 21:53 V47235ENM
4.63 JB µg/m3 0.139 4.92Isopropyl Alcohol 1 05/11/24 21:53 V47235ENM
177 µg/m3 4.48 29.5Methyl Ethyl Ketone (MEK)20 05/10/24 23:08 V47252ENM
<0.033 µg/m3 0.033 1.80Methyl tert-butyl ether (MTBE)1 05/11/24 21:53 V47235ENM
<0.121 µg/m3 0.121 2.054-Methyl-2-Pentanone 1 05/11/24 21:53 V47235ENM
0.778 J µg/m3 0.488 1.74Methylene Chloride 1 05/11/24 21:53 V47235ENM
<0.183 µg/m3 0.183 2.62Naphthalene 1 05/11/24 21:53 V47235ENM
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 11 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-DUP
92298 Matrix:
4/30/2024 0:00
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
<0.242 µg/m3 0.242 0.860Propene 1 05/11/24 21:53 V47235ENM
<0.124 µg/m3 0.124 2.13Styrene 1 05/11/24 21:53 V47235ENM
<0.104 µg/m3 0.104 3.431,1,2,2-Tetrachloroethane 1 05/11/24 21:53 V47235ENM
1.02 J µg/m3 0.181 3.39Tetrachloroethene 1 05/11/24 21:53 V47235ENM
1230 µg/m3 2.14 29.5Tetrahydrofuran 20 05/10/24 23:08 V47252ENM
2.72 µg/m3 0.090 1.88Toluene 1 05/11/24 21:53 V47235ENM
<0.209 µg/m3 0.209 3.711,2,4-Trichlorobenzene 1 05/11/24 21:53 V47235ENM
<0.144 µg/m3 0.144 2.731,1,1-Trichloroethane 1 05/11/24 21:53 V47235ENM
<0.087 µg/m3 0.087 2.731,1,2-Trichloroethane 1 05/11/24 21:53 V47235ENM
<0.199 µg/m3 0.199 2.15Trichloroethene 1 05/11/24 21:53 V47235ENM
1.88 J µg/m3 0.130 2.81Trichlorofluoromethane 1 05/11/24 21:53 V47235ENM
1.07 J µg/m3 0.110 2.461,2,4-Trimethylbenzene 1 05/11/24 21:53 V47235ENM
<0.236 µg/m3 0.236 2.461,3,5-Trimethylbenzene 1 05/11/24 21:53 V47235ENM
<0.224 µg/m3 0.224 1.76Vinyl Acetate 1 05/11/24 21:53 V47235ENM
<0.127 µg/m3 0.127 1.28Vinyl Chloride 1 05/11/24 21:53 V47235ENM
0.976 J µg/m3 0.157 2.17o-Xylene 1 05/11/24 21:53 V47235ENM
1.83 J µg/m3 0.217 5.65m,p-Xylene 1 05/11/24 21:53 V47235ENM
2.81 J µg/m3 0.157 2.17Xylene (Total)1 05/11/24 21:53 V47235
Surrogate: 4-Bromofluorobenzene 104 Limits: 70-130%05/11/24 21:531 ENM V47235
Surrogate: 4-Bromofluorobenzene 106 Limits: 70-130%05/10/24 23:0820 ENM V47252
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 12 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-D
92299 Matrix:
4/30/2024 13:48
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
832 µg/m3 4.04 95.0Acetone 20 05/10/24 23:45 V47252ENM
0.456 J µg/m3 0.073 1.60Benzene 1 05/11/24 22:46 V47235ENM
<0.147 µg/m3 0.147 10.4Benzyl Chloride 1 05/11/24 22:46 V47235ENM
<0.150 µg/m3 0.150 3.35Bromodichloromethane 1 05/11/24 22:46 V47235ENM
<0.153 µg/m3 0.153 5.17Bromoform 1 05/11/24 22:46 V47235ENM
<0.115 µg/m3 0.115 1.94Bromomethane 1 05/11/24 22:46 V47235ENM
<0.328 µg/m3 0.328 1.111,3-Butadiene 1 05/11/24 22:46 V47235ENM
0.697 JB µg/m3 0.060 6.23Carbon Disulfide 1 05/11/24 22:46 V47235ENM
<0.155 µg/m3 0.155 3.15Carbon Tetrachloride 1 05/11/24 22:46 V47235ENM
<0.107 µg/m3 0.107 2.30Chlorobenzene 1 05/11/24 22:46 V47235ENM
<0.208 µg/m3 0.208 4.26Chlorodibromomethane 1 05/11/24 22:46 V47235ENM
<0.164 µg/m3 0.164 1.32Chloroethane 1 05/11/24 22:46 V47235ENM
0.912 J µg/m3 0.086 2.44Chloroform 1 05/11/24 22:46 V47235ENM
0.408 J µg/m3 0.067 1.03Chloromethane 1 05/11/24 22:46 V47235ENM
<0.161 µg/m3 0.161 3.44Cyclohexane 1 05/11/24 22:46 V47235ENM
<0.151 µg/m3 0.151 3.841,2-Dibromoethane 1 05/11/24 22:46 V47235ENM
<0.096 µg/m3 0.096 3.011,2-Dichlorobenzene 1 05/11/24 22:46 V47235ENM
<0.174 µg/m3 0.174 12.01,3-Dichlorobenzene 1 05/11/24 22:46 V47235ENM
<0.186 µg/m3 0.186 3.011,4-Dichlorobenzene 1 05/11/24 22:46 V47235ENM
2.37 J µg/m3 0.134 2.47Dichlorodifluoromethane 1 05/11/24 22:46 V47235ENM
<0.101 µg/m3 0.101 2.021,1-Dichloroethane 1 05/11/24 22:46 V47235ENM
<0.129 µg/m3 0.129 2.021,2-Dichloroethane 1 05/11/24 22:46 V47235ENM
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 13 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-D
92299 Matrix:
4/30/2024 13:48
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
<0.107 µg/m3 0.107 1.981,1-Dichloroethene 1 05/11/24 22:46 V47235ENM
<0.095 µg/m3 0.095 1.98cis-1,2-Dichloroethene 1 05/11/24 22:46 V47235ENM
<0.108 µg/m3 0.108 1.98trans-1,2-Dichloroethene 1 05/11/24 22:46 V47235ENM
<0.205 µg/m3 0.205 2.311,2-Dichloropropane 1 05/11/24 22:46 V47235ENM
<0.622 µg/m3 0.622 3.501,2-Dichlorotetrafluoroethane 1 05/11/24 22:46 V47235ENM
<0.178 µg/m3 0.178 2.27cis-1,3-Dichloropropene 1 05/11/24 22:46 V47235ENM
<0.178 µg/m3 0.178 2.27trans-1,3-Dichloropropene 1 05/11/24 22:46 V47235ENM
<0.435 µg/m3 0.435 1.801,4-Dioxane 1 05/11/24 22:46 V47235ENM
1.84 µg/m3 0.136 1.80Ethyl Acetate 1 05/11/24 22:46 V47235ENM
0.577 J µg/m3 0.106 2.17Ethylbenzene 1 05/11/24 22:46 V47235ENM
0.403 J µg/m3 0.128 2.464-Ethyltoluene 1 05/11/24 22:46 V47235ENM
<0.561 µg/m3 0.561 3.831,1,2-Trichloro-1,2,2-trifluoroethane 1 05/11/24 22:46 V47235ENM
<0.143 µg/m3 0.143 2.05Heptane 1 05/11/24 22:46 V47235ENM
<0.330 µg/m3 0.330 5.33Hexachlorobutadiene 1 05/11/24 22:46 V47235ENM
<0.047 µg/m3 0.047 1.76n-Hexane 1 05/11/24 22:46 V47235ENM
<0.285 µg/m3 0.285 2.052-Hexanone 1 05/11/24 22:46 V47235ENM
21.8 µg/m3 0.139 4.92Isopropyl Alcohol 1 05/11/24 22:46 V47235ENM
231 µg/m3 4.48 29.5Methyl Ethyl Ketone (MEK)20 05/10/24 23:45 V47252ENM
<0.033 µg/m3 0.033 1.80Methyl tert-butyl ether (MTBE)1 05/11/24 22:46 V47235ENM
<0.121 µg/m3 0.121 2.054-Methyl-2-Pentanone 1 05/11/24 22:46 V47235ENM
0.531 J µg/m3 0.488 1.74Methylene Chloride 1 05/11/24 22:46 V47235ENM
<0.183 µg/m3 0.183 2.62Naphthalene 1 05/11/24 22:46 V47235ENM
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 14 of 23
,
REPORT OF ANALYSISReport Number :
Project
Information :
NC 28203
24-121-0011
01102
Hart & Hickman (Charlotte)
2923 South Tryon St. Ste 100
Trinh Desa
Charlotte
Received : 04/30/2024
NVR-019-004-D
Report Date : 05/14/2024
Sample ID :
Lab No :
Sampled:SS-1012-D
92299 Matrix:
4/30/2024 13:48
Air
Analytical Method:
Prep Method:
Test Results Units MDL MQL By Analytical
Batch
Date / Time
Analyzed
DF
TO-15 Prep
TO-15 Prep Batch(es):V47233 05/11/24 12:54 V47245 05/10/24 09:00
<0.242 µg/m3 0.242 0.860Propene 1 05/11/24 22:46 V47235ENM
0.353 J µg/m3 0.124 2.13Styrene 1 05/11/24 22:46 V47235ENM
<0.104 µg/m3 0.104 3.431,1,2,2-Tetrachloroethane 1 05/11/24 22:46 V47235ENM
1.26 J µg/m3 0.181 3.39Tetrachloroethene 1 05/11/24 22:46 V47235ENM
2410 µg/m3 2.14 29.5Tetrahydrofuran 20 05/10/24 23:45 V47252ENM
2.50 µg/m3 0.090 1.88Toluene 1 05/11/24 22:46 V47235ENM
<0.209 µg/m3 0.209 3.711,2,4-Trichlorobenzene 1 05/11/24 22:46 V47235ENM
<0.144 µg/m3 0.144 2.731,1,1-Trichloroethane 1 05/11/24 22:46 V47235ENM
<0.087 µg/m3 0.087 2.731,1,2-Trichloroethane 1 05/11/24 22:46 V47235ENM
<0.199 µg/m3 0.199 2.15Trichloroethene 1 05/11/24 22:46 V47235ENM
1.80 J µg/m3 0.130 2.81Trichlorofluoromethane 1 05/11/24 22:46 V47235ENM
1.66 J µg/m3 0.110 2.461,2,4-Trimethylbenzene 1 05/11/24 22:46 V47235ENM
0.565 J µg/m3 0.236 2.461,3,5-Trimethylbenzene 1 05/11/24 22:46 V47235ENM
<0.224 µg/m3 0.224 1.76Vinyl Acetate 1 05/11/24 22:46 V47235ENM
<0.127 µg/m3 0.127 1.28Vinyl Chloride 1 05/11/24 22:46 V47235ENM
1.35 J µg/m3 0.157 2.17o-Xylene 1 05/11/24 22:46 V47235ENM
2.47 J µg/m3 0.217 5.65m,p-Xylene 1 05/11/24 22:46 V47235ENM
3.82 J µg/m3 0.157 2.17Xylene (Total)1 05/11/24 22:46 V47235
Surrogate: 4-Bromofluorobenzene 106 Limits: 70-130%05/11/24 22:461 ENM V47235
Surrogate: 4-Bromofluorobenzene 98.3 Limits: 70-130%05/10/24 23:4520 ENM V47252
Qualifiers/
Definitions
Dilution FactorDFAnalyte detected in blankB
Method Quantitation LimitMQLEstimated valueJ
Page 15 of 23
Quality Control Data
24-121-0011Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V47235QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V47233
Associated Lab Samples: 92297, 92298, 92299
LRB-V47233 Matrix: AIRLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
05/11/24 14:201.600.073<0.073µg/m3Benzene
05/11/24 14:2010.40.147<0.147µg/m3Benzyl Chloride
05/11/24 14:203.350.150<0.150µg/m3Bromodichloromethane
05/11/24 14:205.170.153<0.153µg/m3Bromoform
05/11/24 14:201.940.115<0.115µg/m3Bromomethane
05/11/24 14:201.110.328<0.328µg/m31,3-Butadiene
05/11/24 14:206.230.0600.439µg/m3Carbon Disulfide
05/11/24 14:203.150.155<0.155µg/m3Carbon Tetrachloride
05/11/24 14:202.300.107<0.107µg/m3Chlorobenzene
05/11/24 14:204.260.208<0.208µg/m3Chlorodibromomethane
05/11/24 14:201.320.164<0.164µg/m3Chloroethane
05/11/24 14:202.440.086<0.086µg/m3Chloroform
05/11/24 14:201.030.067<0.067µg/m3Chloromethane
05/11/24 14:203.440.161<0.161µg/m3Cyclohexane
05/11/24 14:203.840.151<0.151µg/m31,2-Dibromoethane
05/11/24 14:203.010.096<0.096µg/m31,2-Dichlorobenzene
05/11/24 14:2012.00.174<0.174µg/m31,3-Dichlorobenzene
05/11/24 14:203.010.186<0.186µg/m31,4-Dichlorobenzene
05/11/24 14:202.470.134<0.134µg/m3Dichlorodifluoromethane
05/11/24 14:202.020.101<0.101µg/m31,1-Dichloroethane
05/11/24 14:202.020.129<0.129µg/m31,2-Dichloroethane
05/11/24 14:201.980.107<0.107µg/m31,1-Dichloroethene
05/11/24 14:201.980.095<0.095µg/m3cis-1,2-Dichloroethene
05/11/24 14:201.980.108<0.108µg/m3trans-1,2-Dichloroethene
05/11/24 14:202.310.205<0.205µg/m31,2-Dichloropropane
05/11/24 14:203.500.622<0.622µg/m31,2-Dichlorotetrafluoroethane
05/11/24 14:202.270.178<0.178µg/m3cis-1,3-Dichloropropene
Page 1 of 6Date:05/14/2024 05:41 PM
Page 16 of 23
Quality Control Data
24-121-0011Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V47235QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V47233
Associated Lab Samples: 92297, 92298, 92299
LRB-V47233 Matrix: AIRLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
05/11/24 14:202.270.178<0.178µg/m3trans-1,3-Dichloropropene
05/11/24 14:201.800.435<0.435µg/m31,4-Dioxane
05/11/24 14:201.800.136<0.136µg/m3Ethyl Acetate
05/11/24 14:202.170.106<0.106µg/m3Ethylbenzene
05/11/24 14:202.460.128<0.128µg/m34-Ethyltoluene
05/11/24 14:203.830.561<0.561µg/m31,1,2-Trichloro-1,2,2-trifluoroethane
05/11/24 14:202.050.143<0.143µg/m3Heptane
05/11/24 14:205.330.330<0.330µg/m3Hexachlorobutadiene
05/11/24 14:201.760.047<0.047µg/m3n-Hexane
05/11/24 14:202.050.285<0.285µg/m32-Hexanone
05/11/24 14:204.920.1390.496µg/m3Isopropyl Alcohol
05/11/24 14:201.800.033<0.033µg/m3Methyl tert-butyl ether (MTBE)
05/11/24 14:202.050.121<0.121µg/m34-Methyl-2-Pentanone
05/11/24 14:201.740.488<0.488µg/m3Methylene Chloride
05/11/24 14:202.620.183<0.183µg/m3Naphthalene
05/11/24 14:200.8600.242<0.242µg/m3Propene
05/11/24 14:202.130.124<0.124µg/m3Styrene
05/11/24 14:203.430.104<0.104µg/m31,1,2,2-Tetrachloroethane
05/11/24 14:203.390.181<0.181µg/m3Tetrachloroethene
05/11/24 14:201.880.090<0.090µg/m3Toluene
05/11/24 14:203.710.209<0.209µg/m31,2,4-Trichlorobenzene
05/11/24 14:202.730.144<0.144µg/m31,1,1-Trichloroethane
05/11/24 14:202.730.087<0.087µg/m31,1,2-Trichloroethane
05/11/24 14:202.150.199<0.199µg/m3Trichloroethene
05/11/24 14:202.810.130<0.130µg/m3Trichlorofluoromethane
05/11/24 14:202.460.110<0.110µg/m31,2,4-Trimethylbenzene
05/11/24 14:202.460.236<0.236µg/m31,3,5-Trimethylbenzene
Page 2 of 6Date:05/14/2024 05:41 PM
Page 17 of 23
Quality Control Data
24-121-0011Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V47235QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V47233
Associated Lab Samples: 92297, 92298, 92299
LRB-V47233 Matrix: AIRLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
05/11/24 14:201.760.224<0.224µg/m3Vinyl Acetate
05/11/24 14:201.280.127<0.127µg/m3Vinyl Chloride
05/11/24 14:202.170.157<0.157µg/m3o-Xylene
05/11/24 14:205.650.217<0.217µg/m3m,p-Xylene
05/11/24 14:204-Bromofluorobenzene (S)93.8 70-130
LCS-V47233Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
10416.716.0µg/m3Benzene 70-130
10527.325.9µg/m3Benzyl Chloride 70-130
10334.533.5µg/m3Bromodichloromethane 70-130
10152.451.7µg/m3Bromoform 70-130
98.919.219.4µg/m3Bromomethane 70-130
99.011.011.1µg/m31,3-Butadiene 70-130
10616.615.6µg/m3Carbon Disulfide 70-130
10533.131.5µg/m3Carbon Tetrachloride 70-130
10524.123.0µg/m3Chlorobenzene 70-130
10444.542.6µg/m3Chlorodibromomethane 70-130
96.212.713.2µg/m3Chloroethane 70-130
10525.524.4µg/m3Chloroform 70-130
10310.610.3µg/m3Chloromethane 70-130
99.417.117.2µg/m3Cyclohexane 70-130
10740.938.4µg/m31,2-Dibromoethane 70-130
10531.630.1µg/m31,2-Dichlorobenzene 70-130
10531.530.1µg/m31,3-Dichlorobenzene 70-130
10531.730.1µg/m31,4-Dichlorobenzene 70-130
Page 3 of 6Date:05/14/2024 05:41 PM
Page 18 of 23
Quality Control Data
24-121-0011Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V47235QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V47233
LCS-V47233Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
97.124.024.7µg/m3Dichlorodifluoromethane 70-130
10721.720.2µg/m31,1-Dichloroethane 70-130
10220.620.2µg/m31,2-Dichloroethane 70-130
10721.119.8µg/m31,1-Dichloroethene 70-130
10921.619.8µg/m3cis-1,2-Dichloroethene 70-130
11021.719.8µg/m3trans-1,2-Dichloroethene 70-130
10123.323.1µg/m31,2-Dichloropropane 70-130
97.134.035.0µg/m31,2-Dichlorotetrafluoroethane 70-130
10824.622.7µg/m3cis-1,3-Dichloropropene 70-130
10624.122.7µg/m3trans-1,3-Dichloropropene 70-130
10318.518.0µg/m31,4-Dioxane 70-130
10418.818.0µg/m3Ethyl Acetate 70-130
10723.321.7µg/m3Ethylbenzene 70-130
10024.724.6µg/m34-Ethyltoluene 70-130
10640.738.3µg/m31,1,2-Trichloro-1,2,2-trifluoroethane 70-130
11022.620.5µg/m3Heptane 70-130
10857.453.3µg/m3Hexachlorobutadiene 70-130
10919.117.6µg/m3n-Hexane 70-130
10722.020.5µg/m32-Hexanone 70-130
10613.012.3µg/m3Isopropyl Alcohol 70-130
10919.618.0µg/m3Methyl tert-butyl ether (MTBE)70-130
10722.020.5µg/m34-Methyl-2-Pentanone 70-130
96.516.817.4µg/m3Methylene Chloride 70-130
11129.026.2µg/m3Naphthalene 70-130
97.68.418.61µg/m3Propene 70-130
10221.721.3µg/m3Styrene 70-130
10235.134.3µg/m31,1,2,2-Tetrachloroethane 70-130
Page 4 of 6Date:05/14/2024 05:41 PM
Page 19 of 23
Quality Control Data
24-121-0011Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V47235QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V47233
LCS-V47233Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
10234.533.9µg/m3Tetrachloroethene 70-130
10720.218.8µg/m3Toluene 70-130
11341.937.1µg/m31,2,4-Trichlorobenzene 70-130
10328.027.3µg/m31,1,1-Trichloroethane 70-130
10428.427.3µg/m31,1,2-Trichloroethane 70-130
10327.726.9µg/m3Trichloroethene 70-130
10730.028.1µg/m3Trichlorofluoromethane 70-130
10425.724.6µg/m31,2,4-Trimethylbenzene 70-130
10024.724.6µg/m31,3,5-Trimethylbenzene 70-130
11119.517.6µg/m3Vinyl Acetate 70-130
95.312.212.8µg/m3Vinyl Chloride 70-130
10723.221.7µg/m3o-Xylene 70-130
10947.443.4µg/m3m,p-Xylene 70-130
96.64-Bromofluorobenzene (S)70-130
Page 5 of 6Date:05/14/2024 05:41 PM
Page 20 of 23
Quality Control Data
24-121-0011Report No:
Project Description:
Client ID:Hart & Hickman (Charlotte)
NVR-019-004-D
QC Prep Batch Method:
Volatile Organic Compounds in Air- GC/MS
TO-15
V47252QC Analytical Batch(es):
Analysis Method:
Analysis Description:
TO-15 Prep
QC Prep:V47245
Associated Lab Samples: 92297, 92298, 92299
LRB-V47245 Matrix: AIRLab Reagent Blank
Parameter
AnalyzedMQLMDLBlank
ResultUnits
%
Recovery
% Rec
Limits
05/10/24 13:364.750.2020.648µg/m3Acetone
05/10/24 13:361.470.224<0.224µg/m3Methyl Ethyl Ketone (MEK)
05/10/24 13:361.470.1070.359µg/m3Tetrahydrofuran
05/10/24 13:364-Bromofluorobenzene (S)97.7 70-130
LCS-V47245Laboratory Control Sample
Parameter
LCS %RecLCS
Result
Spike
Conc.Units
% Rec
Limits
10212.111.9µg/m3Acetone 70-130
99.314.714.8µg/m3Methyl Ethyl Ketone (MEK)70-130
10114.814.7µg/m3Tetrahydrofuran 70-130
93.54-Bromofluorobenzene (S)70-130
Page 6 of 6Date:05/14/2024 05:41 PM
Page 21 of 23
Fed Ex
UPS
US Postal
Client
Lab
Courier
Other :
Shipment Receipt Form
Customer Number:
Customer Name:
Report Number:24-121-0011
Hart & Hickman (Charlotte)
01102
Shipping Method
Shipping container/cooler uncompromised?
Thermometer ID:N/A
Chain of Custody (COC) present?Yes No
Yes No Not Present
Yes No Not Present
Yes No
COC agrees with sample label(s)? Yes No
COC properly completed
Samples in proper containers?
Sample containers intact?
Sufficient sample volume for indicated test(s)?
All samples received within holding time?
Cooler temperature in compliance?
Yes No
Yes No
Yes No
Yes No
Yes No
Yes NoCooler/Samples arrived at the laboratory on ice.
Samples were considered acceptable as cooling
process had begun.
Yes No
Yes No N/A
Yes No N/A
Yes No N/ASoil VOA method 5035 – compliance criteria met
Water - Sample containers properly preserved
Water - VOA vials free of headspace Yes No N/A
Trip Blanks received with VOAs
Low concentration EnCore samplers (48 hr)
High concentration pre-weighed (methanol -14 d) Low conc pre-weighed vials (Sod Bis -14 d)
High concentration container (48 hr)
Custody seals intact on shipping container/cooler?
Custody seals intact on sample bottles?
Number of coolers/boxes received
Yes No
1
Signature:Angelo Norvell Date & Time:04/30/2024 14:32:02
Special precautions or instructions included?
Comments:
Page 22 of 23
Page 23 of 23

Appendix D
PVC Primer and PVC Glue Material Safety Data Sheets
SAFETY DATA SHEET
1. Identification
Oatey Purple Primer- NSF Listed for PVC and CPVCProduct identifier
Other means of identification
1402CSDS number
Part Numbers: 30755(TV), 30756(TV), 30757(TV), 30758, 30759, 30927, 31480, 31481, 31482,
31483Synonyms
Joining PVC PipesRecommended use
None known.Recommended restrictions
Manufacturer/Importer/Supplier/Distributor information
Company Name Oatey Co.
Address 4700 West 160th St.
Cleveland, OH 44135
Telephone [phone]
E-mail [e-mail]
Transport Emergency Chemtrec 1-800-424-9300 (Outside the US 1-703-527-3887)
Emergency First Aid 1-877-740-5015
Contact person MSDS Coordinator
2. Hazard(s) identification
Category 2Flammable liquidsPhysical hazards
Category 1Physical hazards not otherwise classified
Category 4Acute toxicity, oralHealth hazards
Category 2Skin corrosion/irritation
Category 2ASerious eye damage/eye irritation
Category 3 respiratory tract irritationSpecific target organ toxicity, single exposure
Category 3 narcotic effectsSpecific target organ toxicity, single exposure
Category 1Aspiration hazard
Category 1Health hazards not otherwise classified
Not classified.Environmental hazards
Label elements
Signal word Danger
Hazard statement Highly flammable liquid and vapor. Harmful if swallowed. May be fatal if swallowed and enters
airways. Causes skin irritation. Causes serious eye irritation. May cause respiratory irritation. May
cause drowsiness or dizziness.
Precautionary statement
Prevention Keep away from heat, hot surfaces, sparks, open flames and other ignition sources. No smoking.
Keep container tightly closed. Ground/bond container and receiving equipment. Use
explosion-proof electrical/ventilating/lighting/equipment. Use non-sparking tools. Take action to
prevent static discharges. Avoid breathing mist or vapor. Wash thoroughly after handling. Do not
eat, drink or smoke when using this product. Use only outdoors or in a well-ventilated area. Wear
protective gloves/protective clothing/eye protection/face protection.
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 1 / 9
Response IF SWALLOWED: Immediately call a POISON CENTER or doctor/physician. IF ON SKIN (or hair):
Take off immediately all contaminated clothing. Rinse skin with water. IF INHALED: Remove
victim to fresh air and keep at rest in a position comfortable for breathing. IF IN EYES: Rinse
cautiously with water for several minutes. Remove contact lenses, if present and easy to do.
Continue rinsing. Call a POISON CENTER or doctor/physician if you feel unwell. Rinse mouth. Do
NOT induce vomiting. Take off contaminated clothing and wash it before reuse. In case of fire:
Use appropriate media to extinguish.
Storage Keep cool. Store in a well-ventilated place. Keep container tightly closed. Store locked up.
Disposal Dispose of contents/container in accordance with local/regional/national/international regulations.
Other hazards Frequent or prolonged contact may defat and dry the skin, leading to discomfort and dermatitis.
May form explosive peroxides.
Supplemental information Not applicable.
3. Composition/information on ingredients
Mixtures
67-64-1 25-40Acetone
CAS number %Chemical name
108-94-1 25-40Cyclohexanone
78-93-3 15-30Methyl ethyl ketone
All concentrations are in percent by weight unless ingredient is a gas. Gas concentrations are in percent by volume.
4. First-aid measures
Remove victim to fresh air and keep at rest in a position comfortable for breathing. Call a POISON
CENTER or doctor/physician if you feel unwell.
Inhalation
Take off immediately all contaminated clothing. Wash with plenty of soap and water. If skin
irritation occurs: Get medical advice/attention.
Skin contact
Immediately flush eyes with plenty of water for at least 15 minutes. Remove contact lenses, if
present and easy to do. Continue rinsing. If eye irritation persists: Get medical advice/attention.
Eye contact
Call a physician or poison control center immediately. Do not induce vomiting. If vomiting occurs,
keep head low so that stomach content doesn't get into the lungs. Aspiration may cause
pulmonary edema and pneumonitis.
Ingestion
Irritation of nose and throat. Aspiration may cause pulmonary edema and pneumonitis. Severe eye
irritation. Symptoms may include stinging, tearing, redness, swelling, and blurred vision. May
cause respiratory irritation. Vapors have a narcotic effect and may cause headache, fatigue,
dizziness and nausea. Skin irritation. May cause redness and pain.
Most important
symptoms/effects, acute and
delayed
Provide general supportive measures and treat symptomatically. Thermal burns: Flush with water
immediately. While flushing, remove clothes which do not adhere to affected area. Call an
ambulance. Continue flushing during transport to hospital. In case of shortness of breath, give
oxygen. Keep victim warm. Keep victim under observation. Symptoms may be delayed.
Indication of immediate
medical attention and special
treatment needed
Take off all contaminated clothing immediately. IF exposed or concerned: Get medical
advice/attention. Ensure that medical personnel are aware of the material(s) involved, and take
precautions to protect themselves. Wash contaminated clothing before reuse.
General information
5. Fire-fighting measures
Alcohol resistant foam. Water fog. Dry chemical powder. Carbon dioxide (CO2).Suitable extinguishing media
Do not use water jet as an extinguisher, as this will spread the fire.Unsuitable extinguishing
media
Vapors may form explosive mixtures with air. Vapors may travel considerable distance to a source
of ignition and flash back. During fire, gases hazardous to health may be formed.
Specific hazards arising from
the chemical
Self-contained breathing apparatus and full protective clothing must be worn in case of fire.Special protective equipment
and precautions for firefighters
In case of fire and/or explosion do not breathe fumes. Move containers from fire area if you can do
so without risk.
Fire fighting
equipment/instructions
Use standard firefighting procedures and consider the hazards of other involved materials. Cool
containers exposed to flames with water until well after the fire is out.Specific methods
Highly flammable liquid and vapor. This product contains tetrahydrofuran that may form explosive
organic peroxide when exposed to air or light or with age.
General fire hazards
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 2 / 9
6. Accidental release measures
Keep unnecessary personnel away. Keep people away from and upwind of spill/leak. Keep out of
low areas. Eliminate all ignition sources (no smoking, flares, sparks, or flames in immediate area).
Wear appropriate protective equipment and clothing during clean-up. Avoid inhalation of vapors or
mists. Do not touch damaged containers or spilled material unless wearing appropriate protective
clothing. Ventilate closed spaces before entering them. Local authorities should be advised if
significant spillages cannot be contained. For personal protection, see section 8 of the SDS.
Personal precautions,
protective equipment and
emergency procedures
Eliminate all ignition sources (no smoking, flares, sparks, or flames in immediate area). Take
precautionary measures against static discharge. Use only non-sparking tools. Keep combustibles
(wood, paper, oil, etc.) away from spilled material.
Large Spills: Stop the flow of material, if this is without risk. Dike the spilled material, where this is
possible. Cover with plastic sheet to prevent spreading. Use a non-combustible material like
vermiculite, sand or earth to soak up the product and place into a container for later disposal. Use
water spray to reduce vapors or divert vapor cloud drift. Following product recovery, flush area with
water.
Small Spills: Wipe up with absorbent material (e.g. cloth, fleece). Clean surface thoroughly to
remove residual contamination.
Never return spills to original containers for re-use. This product is miscible in water. For waste
disposal, see section 13 of the SDS.
Methods and materials for
containment and cleaning up
Avoid discharge into drains, water courses or onto the ground.Environmental precautions
7. Handling and storage
Vapors may form explosive mixtures with air. Do not handle, store or open near an open flame,
sources of heat or sources of ignition. Protect material from direct sunlight. Take precautionary
measures against static discharges. All equipment used when handling the product must be
grounded. Use non-sparking tools and explosion-proof equipment. Do not taste or swallow. Avoid
breathing mist or vapor. Avoid contact with skin. Avoid contact with eyes. Avoid prolonged
exposure. Avoid contact with clothing. Provide adequate ventilation. Wear appropriate personal
protective equipment. Observe good industrial hygiene practices. When using, do not eat, drink or
smoke. Wash hands thoroughly after handling.
Precautions for safe handling
Store locked up. Keep away from heat, sparks and open flame. Prevent electrostatic charge
build-up by using common bonding and grounding techniques. Store in original tightly closed
container. Store in a cool, dry place out of direct sunlight. Store in a well-ventilated place. Store
away from incompatible materials (see Section 10 of the SDS). Keep in an area equipped with
sprinklers.
Conditions for safe storage,
including any incompatibilities
8. Exposure controls/personal protection
Occupational exposure limits
US. ACGIH Threshold Limit Values
ValueTypeComponents
STEL 500 ppmAcetone (CAS 67-64-1)
TWA 250 ppm
STEL 50 ppmCyclohexanone (CAS
108-94-1)
TWA 20 ppm
STEL 300 ppmMethyl ethyl ketone (CAS
78-93-3)
TWA 200 ppm
Canada. Alberta OELs (Occupational Health & Safety Code, Schedule 1, Table 2)
ValueTypeComponents
STEL 1800 mg/m3Acetone (CAS 67-64-1)
750 ppm
TWA 1200 mg/m3
500 ppm
STEL 200 mg/m3Cyclohexanone (CAS
108-94-1)
50 ppm
TWA 80 mg/m3
20 ppm
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 3 / 9
Canada. Alberta OELs (Occupational Health & Safety Code, Schedule 1, Table 2)
ValueTypeComponents
STEL 885 mg/m3Methyl ethyl ketone (CAS
78-93-3)
300 ppm
TWA 590 mg/m3
200 ppm
Canada. British Columbia OELs. (Occupational Exposure Limits for Chemical Substances, Occupational Health and
Safety Regulation 296/97, as amended)
ValueTypeComponents
STEL 500 ppmAcetone (CAS 67-64-1)
TWA 250 ppm
STEL 50 ppmCyclohexanone (CAS
108-94-1)
TWA 20 ppm
STEL 100 ppmMethyl ethyl ketone (CAS
78-93-3)
TWA 50 ppm
Canada. Manitoba OELs (Reg. 217/2006, The Workplace Safety And Health Act)
ValueTypeComponents
STEL 500 ppmAcetone (CAS 67-64-1)
TWA 250 ppm
STEL 50 ppmCyclohexanone (CAS
108-94-1)
TWA 20 ppm
STEL 300 ppmMethyl ethyl ketone (CAS
78-93-3)
TWA 200 ppm
Canada. Ontario OELs. (Control of Exposure to Biological or Chemical Agents)
ValueTypeComponents
STEL 750 ppmAcetone (CAS 67-64-1)
TWA 500 ppm
STEL 50 ppmCyclohexanone (CAS
108-94-1)
TWA 20 ppm
STEL 300 ppmMethyl ethyl ketone (CAS
78-93-3)
TWA 200 ppm
Canada. Quebec OELs. (Ministry of Labor - Regulation Respecting the Quality of the Work Environment)
ValueTypeComponents
STEL 2380 mg/m3Acetone (CAS 67-64-1)
1000 ppm
TWA 1190 mg/m3
500 ppm
TWA 100 mg/m3Cyclohexanone (CAS
108-94-1)
25 ppm
STEL 300 mg/m3Methyl ethyl ketone (CAS
78-93-3)
100 ppm
TWA 150 mg/m3
50 ppm
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 4 / 9
Biological limit values
ACGIH Biological Exposure Indices
Value Sampling TimeDeterminant SpecimenComponents
25 mg/l Acetone Urine *Acetone (CAS 67-64-1)
80 mg/l 1,2-Cyclohexan
ediol,with
hydrolysis
Urine *Cyclohexanone (CAS
108-94-1)
8 mg/l Cyclohexanol,
with hydrolysis
Urine *
2 mg/l MEK Urine *Methyl ethyl ketone (CAS
78-93-3)
* - For sampling details, please see the source document.
Exposure guidelines
Canada - Alberta OELs: Skin designation
Cyclohexanone (CAS 108-94-1) Can be absorbed through the skin.
Canada - British Columbia OELs: Skin designation
Cyclohexanone (CAS 108-94-1) Can be absorbed through the skin.
Canada - Manitoba OELs: Skin designation
Cyclohexanone (CAS 108-94-1) Can be absorbed through the skin.
Canada - Ontario OELs: Skin designation
Cyclohexanone (CAS 108-94-1) Can be absorbed through the skin.
Canada - Quebec OELs: Skin designation
Cyclohexanone (CAS 108-94-1) Can be absorbed through the skin.
Canada - Saskatchewan OELs: Skin designation
Cyclohexanone (CAS 108-94-1) Can be absorbed through the skin.
US ACGIH Threshold Limit Values: Skin designation
Cyclohexanone (CAS 108-94-1) Can be absorbed through the skin.
Explosion-proof general and local exhaust ventilation. Good general ventilation (typically 10 air
changes per hour) should be used. Ventilation rates should be matched to conditions. If
applicable, use process enclosures, local exhaust ventilation, or other engineering controls to
maintain airborne levels below recommended exposure limits. If exposure limits have not been
established, maintain airborne levels to an acceptable level. Eye wash facilities and emergency
shower must be available when handling this product.
Appropriate engineering
controls
Individual protection measures, such as personal protective equipment
Wear safety glasses with side shields (or goggles).Eye/face protection
Skin protection
Wear appropriate chemical resistant gloves.Hand protection
Wear appropriate chemical resistant clothing.Other
If engineering controls do not maintain airborne concentrations below recommended exposure
limits (where applicable) or to an acceptable level (in countries where exposure limits have not
been established), an approved respirator must be worn.
Respiratory protection
Wear appropriate thermal protective clothing, when necessary.Thermal hazards
When using, do not eat, drink or smoke. Always observe good personal hygiene measures, such
as washing after handling the material and before eating, drinking, and/or smoking. Routinely wash
work clothing and protective equipment to remove contaminants.
General hygiene
considerations
9. Physical and chemical properties
Appearance
Liquid.Physical state
Translucent liquid.Form
PurpleColor
Solvent.Odor
Odor threshold Not available.
pH Not available.
Melting point/freezing point Not available.
Initial boiling point and boiling
range
151 °F (66.11 °C)
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 5 / 9
Flash point 14.0 - 23.0 °F (-10.0 - -5.0 °C)
Evaporation rate 5.5 - 8
Not available.Flammability (solid, gas)
Upper/lower flammability or explosive limits
Flammability limit - lower
(%)
1.8
Flammability limit - upper
(%)
11.8
Explosive limit - lower (%)Not available.
Explosive limit - upper (%)Not available.
Vapor pressure 145 mm Hg @ 20 C
Vapor density 2.5
Relative density 0.84 +/- 0.02 @20°C
Solubility(ies)
Solubility (water)Negligible
Partition coefficient
(n-octanol/water)
Not available.
Auto-ignition temperature Not available.
Decomposition temperature Not available.
Viscosity Not available.
Other information
Bulk density 7 lb/gal
VOC (Weight %)505 g/l SQACMD Method 24
10. Stability and reactivity
The product is stable and non-reactive under normal conditions of use, storage and transport.Reactivity
Material is stable under normal conditions.Chemical stability
No dangerous reaction known under conditions of normal use.Possibility of hazardous
reactions
Avoid heat, sparks, open flames and other ignition sources. Avoid temperatures exceeding the
flash point. Contact with incompatible materials.
Conditions to avoid
Acids. Strong oxidizing agents. Ammonia. Amines. Isocyanates. Caustics.Incompatible materials
No hazardous decomposition products are known.Hazardous decomposition
products
11. Toxicological information
Information on likely routes of exposure
Inhalation May be fatal if swallowed and enters airways. May cause irritation to the respiratory system.
Vapors have a narcotic effect and may cause headache, fatigue, dizziness and nausea.
Prolonged inhalation may be harmful.
Skin contact Causes skin irritation.
Eye contac Causes serious eye irritation.
Ingestion May be fatal if swallowed and enters airways. Harmful if swallowed.
Symptoms related to the
physical, chemical and
toxicological characteristics
Irritation of nose and throat. Aspiration may cause pulmonary edema and pneumonitis. Severe
eye irritation. Symptoms may include stinging, tearing, redness, swelling, and blurred vision. Skin
irritation. May cause redness and pain. Symptoms of overexposure may be headache, dizziness,
tiredness, nausea and vomitin .
Information on toxicological effects
Acute toxicit May be fatal if swallowed and enters airways. Narcotic effects. May cause respiratory irritation.
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 6 / 9
Test ResultsComponents Species
Acetone (CAS 67-64-1)
LD50 Rabbit
Dermal
Acute
20 ml/kg
LC50 Rat
Inhalation
50 mg/l, 8 Hours
LD50 Rat
Oral
5800 mg/kg
Cyclohexanone (CAS 108-94-1)
LD50 Rabbit
Dermal
Acute
948 mg/kg
LC50 Rat
Inhalation
8000 ppm, 4 hours
LD50 Rat
Oral
800 mg/kg
* Estimates for product may be based on additional component data not shown.
Causes skin irritation.Skin corrosion/irritation
Causes serious eye irritation.Serious eye damage/eye
irritation
Respiratory or skin sensitization
Respiratory sensitization Not available.
This product is not expected to cause skin sensitization.Skin sensitization
No data available to indicate product or any components present at greater than 0.1% are
mutagenic or genotoxic.
Germ cell mutagenicity
Carcinogenicity In 2012 USEPA Integrated Risk Information System (IRIS) reviewed a two species inhalation
lifetime study on THF conducted by NTP (1998). Male rats developed renal tumors and female
mice developed liver tumors while neither the female rats nor the male mice showed similar
results. Because the carcinogenic mechanisms could not be identified clearly in either species for
either tumor, the EPA determined that the male rat and female mouse findings are relevant to the
assessment of carcinogenic potential in humans. Therefore, the IRIS review concludes that these
data in aggregate indicate that there is "suggestive evidence of carcinogenic potential" following
exposure to THF by all routes of exposure.
ACGIH Carcinogens
Acetone (CAS 67-64-1) A4 Not classifiable as a human carcinogen.
Cyclohexanone (CAS 108-94-1) A3 Confirmed animal carcinogen with unknown relevance to
humans.
Canada - Manitoba OELs: carcinogenicity
ACETONE (CAS 67-64-1) Not classifiable as a human carcinogen.
CYCLOHEXANONE (CAS 108-94-1) Confirmed animal carcinogen with unknown relevance to humans.
IARC Monographs. Overall Evaluation of Carcinogenicity
Cyclohexanone (CAS 108-94-1) 3 Not classifiable as to carcinogenicity to humans.
This product is not expected to cause reproductive or developmental effects.Reproductive toxicity
Specific target organ toxicity -
single exposure
Narcotic effects. Respiratory tract irritation.
Specific target organ toxicity -
repeated exposure
Not classified.
Aspiration hazard May be fatal if swallowed and enters airways.
Chronic effects Prolonged inhalation may be harmful.
12. Ecological information
The product is not classified as environmentally hazardous. However, this does not exclude the
possibility that large or frequent spills can have a harmful or damaging effect on the environment.
Ecotoxicity
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 7 / 9
Components Test ResultsSpecies
Acetone (CAS 67-64-1)
Aquatic
LC50Fish > 100 mg/l, 96 hoursFathead minnow (Pimephales promelas)
* Estimates for product may be based on additional component data not shown.
Cyclohexanone (CAS 108-94-1)
Aquatic
LC50Fish 481 - 578 mg/l, 96 hoursFathead minnow (Pimephales promelas)
No data is available on the degradability of this product.Persistence and degradability
No data available.Bioaccumulative potential
Partition coefficient n-octanol / water (log Kow)
Acetone (CAS 67-64-1) -0.24
Cyclohexanone (CAS 108-94-1) 0.81
Methyl ethyl ketone (CAS 78-93-3) 0.29
No data available.Mobility in soil
Other adverse effects No other adverse environmental effects (e.g. ozone depletion, photochemical ozone creation
potential, endocrine disruption, global warming potential) are expected from this component.
13. Disposal considerations
Collect and reclaim or dispose in sealed containers at licensed waste disposal site. This material
and its container must be disposed of as hazardous waste. Do not allow this material to drain into
sewers/water supplies. Do not contaminate ponds, waterways or ditches with chemical or used
container. Dispose of contents/container in accordance with local/regional/national/international
regulations.
Disposal instructions
Dispose in accordance with all applicable regulations.Local disposal regulations
The waste code should be assigned in discussion between the user, the producer and the waste
disposal company.
Hazardous waste code
Dispose of in accordance with local regulations. Empty containers or liners may retain some
product residues. This material and its container must be disposed of in a safe manner (see:
Disposal instructions).
Waste from residues / unused
products
Since emptied containers may retain product residue, follow label warnings even after container is
emptied. Empty containers should be taken to an approved waste handling site for recycling or
disposal.
Contaminated packaging
14. Transport information
TDG
UN1993UN number
FLAMMABLE LIQUID, N.O.S. (Methyl ethyl ketone, Acetone)UN proper shipping name
3Class
Transport hazard class(es)
-Subsidiary risk
IIPacking group
DEnvironmental hazards
Read safety instructions, SDS and emergency procedures before handling.Special precautions for user
IATA
UN1993UN number
Flammable liquid, n.o.s. (Methyl ethyl ketone, Acetone)UN proper shipping name
3Class
Transport hazard class(es)
-Subsidiary risk
IIPacking group
No.Environmental hazards
3HERG Code
Read safety instructions, SDS and emergency procedures before handling.Special precautions for user
IMDG
UN1993UN number
FLAMMABLE LIQUID, N.O.S. (Methyl ethyl ketone, Acetone)UN proper shipping name
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 8 / 9
3Class
Transport hazard class(es)
-Subsidiary risk
IIPacking group
No.Marine pollutant
Environmental hazards
F-E, S-EEmS
Read safety instructions, SDS and emergency procedures before handling.Special precautions for user
Not available.Transport in bulk according to
Annex II of MARPOL 73/78 and
the IBC Code
15. Regulatory information
This product has been classified in accordance with the hazard criteria of the HPR and the SDS
contains all the information required by the HPR.
Canadian regulations
Controlled Drugs and Substances Act
Not regulated.
Export Control List (CEPA 1999, Schedule 3)
Not listed.
Greenhouse Gases
Not listed.
Precursor Control Regulations
Acetone (CAS 67-64-1) Class B
Methyl ethyl ketone (CAS 78-93-3) Class B
International regulations
Stockholm Convention
Not applicable.
Rotterdam Convention
Not applicable.
Kyoto protocol
Not applicable.
Montreal Protocol
Not applicable.
Basel Convention
Not applicable.
International Inventories
Country(s) or region Inventory name On inventory (yes/no)*
Domestic Substances List (DSL) YesCanada
Non-Domestic Substances List (NDSL) NoCanada
*A "Yes" indicates this product complies with the inventory requirements administered by the governing country(s).
"No" indicates that one or more components of the product are not listed or exempt from listing on the inventory administered by the governing
country(s).
Toxic Substances Control Act (TSCA) Inventory YesUnited States & Puerto Rico
16. Other Information
21-December-2015Issue date
-Revision date
Version #01
Oatey Co. cannot anticipate all conditions under which this information and its product, or the
products of other manufacturers in combination with its product, may be used. It is the user’s
responsibility to ensure safe conditions for handling, storage and disposal of the product, and to
assume liability for loss, injury, damage or expense due to improper use. The information in the
sheet was written based on the best knowledge and experience currently available.
Disclaimer
Oatey Purple Primer- NSF Listed for PVC and CPVC SDS Canada
926733 Version #: 01 Revision date: - Issue date: 21-December-2015 9 / 9
SAFETY DATA SHEET
1. Identification
PVC Regular Clear CementProduct identifier
Other means of identification
1100EProduct code
Part Numbers: 31012, 31013, 31014, 31015, 31016, 31958, 31959, 31960, 31961Synonyms
Joining PVC PipesRecommended use
None known.Recommended restrictions
Manufacturer/Importer/Supplier/Distributor information
Company Name Oatey Co.
Address 4700 West 160th St.
Cleveland, OH 44135
Telephone [phone]
E-mail [e-mail]
Transport Emergency Chemtrec 1-800-424-9300 (Outside the US 1-703-527-3887)
Emergency First Aid 1-877-740-5015
Contact person MSDS Coordinator
2. Hazard(s) identification
Category 2Flammable liquidsPhysical hazards
Category 4Acute toxicity, oralHealth hazards
Category 2Skin corrosion/irritation
Category 2ASerious eye damage/eye irritation
Category 3 respiratory tract irritationSpecific target organ toxicity, single exposure
Category 3 narcotic effectsSpecific target organ toxicity, single exposure
Category 1Aspiration hazard
Not classified.OSHA defined hazards
Label elements
Signal word Danger
Hazard statement Highly flammable liquid and vapor. Harmful if swallowed. May be fatal if swallowed and enters
airways. Causes skin irritation. Causes serious eye irritation. May cause respiratory irritation. May
cause drowsiness or dizziness.
Precautionary statement
Prevention Keep away from heat/sparks/open flames/hot surfaces. - No smoking. Keep container tightly
closed. Ground/bond container and receiving equipment. Use explosion-proof
electrical/ventilating/lighting equipment. Use only non-sparking tools. Take precautionary
measures against static discharge. Avoid breathing mist or vapor. Wash thoroughly after
handling. Do not eat, drink or smoke when using this product. Use only outdoors or in a
well-ventilated area. Wear protective gloves/protective clothing/eye protection/face protection.
Response If swallowed: Immediately call a poison center/doctor. If on skin (or hair): Take off immediately all
contaminated clothing. Rinse skin with water/shower. If inhaled: Remove person to fresh air and
keep comfortable for breathing. If in eyes: Rinse cautiously with water for several minutes.
Remove contact lenses, if present and easy to do. Continue rinsing. Call a poison center/doctor if
you feel unwell. Rinse mouth. Do NOT induce vomiting. If skin irritation occurs: Get medical
advice/attention. If eye irritation persists: Get medical advice/attention. Take off contaminated
clothing and wash before reuse. In case of fire: Use appropriate media to extinguish.
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 1 / 10
Storage Store in a well-ventilated place. Keep container tightly closed. Keep cool. Store locked up.
Disposal Dispose of contents/container in accordance with local/regional/national/international regulations.
Hazard(s) not otherwise
classified (HNOC)
Frequent or prolonged contact may defat and dry the skin, leading to discomfort and dermatitis.
May form explosive peroxides. Contains a chemical classified by the US EPA as a suspected
possible carcinogen.
Supplemental information
Not applicable.
3. Composition/information on ingredients
Mixtures
78-93-3 25-40Methyl ethyl ketone
CAS number %Chemical name
108-94-1 10-25Cyclohexanone
109-99-9 10-25Furan, Tetrahydro-
67-64-1 5-15Acetone
9002-86-2 5-15Polyvinyl chloride
*Designates that a specific chemical identity and/or percentage of composition has been withheld as a trade secret.
4. First-aid measures
Remove victim to fresh air and keep at rest in a position comfortable for breathing. Call a POISON
CENTER or doctor/physician if you feel unwell.Inhalation
Take off immediately all contaminated clothing. Wash with plenty of soap and water. If skin
irritation occurs: Get medical advice/attention.
Skin contact
Immediately flush eyes with plenty of water for at least 15 minutes. Remove contact lenses, if
present and easy to do. Continue rinsing. If eye irritation persists: Get medical advice/attention.Eye contact
Call a physician or poison control center immediately. Do not induce vomiting. If vomiting occurs,
keep head low so that stomach content doesn't get into the lungs. Aspiration may cause
pulmonary edema and pneumonitis.
Ingestion
Irritation of nose and throat. Aspiration may cause pulmonary edema and pneumonitis. Severe eye
irritation. Symptoms may include stinging, tearing, redness, swelling, and blurred vision. May
cause respiratory irritation. Vapors have a narcotic effect and may cause headache, fatigue,
dizziness and nausea. Skin irritation. May cause redness and pain.
Most important
symptoms/effects, acute and
delayed
Provide general supportive measures and treat symptomatically. Thermal burns: Flush with water
immediately. While flushing, remove clothes which do not adhere to affected area. Call an
ambulance. Continue flushing during transport to hospital. In case of shortness of breath, give
oxygen. Keep victim warm. Keep victim under observation. Symptoms may be delayed.
Indication of immediate
medical attention and special
treatment needed
Take off all contaminated clothing immediately. Ensure that medical personnel are aware of the
material(s) involved, and take precautions to protect themselves. Wash contaminated clothing
before reuse.
General information
5. Fire-fighting measures
Alcohol resistant foam. Water fog. Dry chemical powder. Carbon dioxide (CO2).Suitable extinguishing media
Do not use water jet as an extinguisher, as this will spread the fire.Unsuitable extinguishing
media
Vapors may form explosive mixtures with air. Vapors may travel considerable distance to a source
of ignition and flash back. During fire, gases hazardous to health may be formed.
Specific hazards arising from
the chemical
Self-contained breathing apparatus and full protective clothing must be worn in case of fire.Special protective equipment
and precautions for firefighters
In case of fire and/or explosion do not breathe fumes. Move containers from fire area if you can do
so without risk.
Fire fighting
equipment/instructions
Use standard firefighting procedures and consider the hazards of other involved materials.Specific methods
Highly flammable liquid and vapor. This product contains tetrahydrofuran that may form explosive
organic peroxide when exposed to air or light or with age.General fire hazards
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 2 / 10
6. Accidental release measures
Keep unnecessary personnel away. Keep people away from and upwind of spill/leak. Keep out of
low areas. Eliminate all ignition sources (no smoking, flares, sparks, or flames in immediate area).
Wear appropriate protective equipment and clothing during clean-up. Avoid breathing mist or
vapor. Do not touch damaged containers or spilled material unless wearing appropriate protective
clothing. Ventilate closed spaces before entering them. Local authorities should be advised if
significant spillages cannot be contained. For personal protection, see section 8 of the SDS.
Personal precautions,
protective equipment and
emergency procedures
Eliminate all ignition sources (no smoking, flares, sparks, or flames in immediate area). Take
precautionary measures against static discharge. Use only non-sparking tools. Keep combustibles
(wood, paper, oil, etc.) away from spilled material. This product is miscible in water.
Large Spills: Stop the flow of material, if this is without risk. Use water spray to reduce vapors or
divert vapor cloud drift. Dike the spilled material, where this is possible. Cover with plastic sheet to
prevent spreading. Use a non-combustible material like vermiculite, sand or earth to soak up the
product and place into a container for later disposal. Prevent entry into waterways, sewer,
basements or confined areas. Following product recovery, flush area with water.
Small Spills: Absorb with earth, sand or other non-combustible material and transfer to containers
for later disposal. Wipe up with absorbent material (e.g. cloth, fleece). Clean surface thoroughly to
remove residual contamination.
Never return spills to original containers for re-use. For waste disposal, see section 13 of the SDS.
Methods and materials for
containment and cleaning up
Avoid discharge into drains, water courses or onto the ground.Environmental precautions
7. Handling and storage
Vapors may form explosive mixtures with air. Do not handle, store or open near an open flame,
sources of heat or sources of ignition. Protect material from direct sunlight. Explosion-proof
general and local exhaust ventilation. Take precautionary measures against static discharges. All
equipment used when handling the product must be grounded. Use non-sparking tools and
explosion-proof equipment. Avoid breathing mist or vapor. Avoid contact with eyes, skin, and
clothing. Avoid prolonged exposure. Do not taste or swallow. When using, do not eat, drink or
smoke. Wear appropriate personal protective equipment. Wash hands thoroughly after handling.
Observe good industrial hygiene practices.
Precautions for safe handling
Store locked up. Keep away from heat, sparks and open flame. Prevent electrostatic charge
build-up by using common bonding and grounding techniques. Store in a cool, dry place out of
direct sunlight. Store in original tightly closed container. Store in a well-ventilated place. Store
away from incompatible materials (see Section 10 of the SDS).
Conditions for safe storage,
including any incompatibilities
8. Exposure controls/personal protection
Occupational exposure limits
US. OSHA Specifically Regulated Substances (29 CFR 1910.1001-1050)
ValueTypeComponents
STEL 5 ppmPolyvinyl chloride (CAS
9002-86-2)
TWA 1 ppm
US. OSHA Table Z-1 Limits for Air Contaminants (29 CFR 1910.1000)
ValueType FormComponents
PEL 2400 mg/m3Acetone (CAS 67-64-1)
1000 ppm
PEL 200 mg/m3Cyclohexanone (CAS
108-94-1)
50 ppm
PEL 590 mg/m3Furan, Tetrahydro- (CAS
109-99-9)
200 ppm
PEL 590 mg/m3Methyl ethyl ketone (CAS
78-93-3)
200 ppm
PEL 5 mg/m3 Respirable fraction.Polyvinyl chloride (CAS
9002-86-2)
15 mg/m3 Total dust.
PVC Regular Clear Cement SDS US
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 3 / 10
US. ACGIH Threshold Limit Values
ValueType FormComponents
STEL 750 ppmAcetone (CAS 67-64-1)
TWA 500 ppm
STEL 50 ppmCyclohexanone (CAS
108-94-1)
TWA 20 ppm
STEL 100 ppmFuran, Tetrahydro- (CAS
109-99-9)
TWA 50 ppm
STEL 300 ppmMethyl ethyl ketone (CAS
78-93-3)
TWA 200 ppm
TWA 1 mg/m3 Respirable fraction.Polyvinyl chloride (CAS
9002-86-2)
US. NIOSH: Pocket Guide to Chemical Hazards
ValueTypeComponents
TWA 590 mg/m3Acetone (CAS 67-64-1)
250 ppm
TWA 100 mg/m3Cyclohexanone (CAS
108-94-1)
25 ppm
STEL 735 mg/m3Furan, Tetrahydro- (CAS
109-99-9)
250 ppm
TWA 590 mg/m3
200 ppm
STEL 885 mg/m3Methyl ethyl ketone (CAS
78-93-3)
300 ppm
TWA 590 mg/m3
200 ppm
Biological limit values
ACGIH Biological Exposure Indices
Value Sampling TimeDeterminant SpecimenComponents
50 mg/l Acetone Urine *Acetone (CAS 67-64-1)
80 mg/l 1,2-Cyclohexanediol,with
hydrolysis
Urine *Cyclohexanone (CAS
108-94-1)
8 mg/l Cyclohexanol,
with hydrolysis
Urine *
2 mg/l Tetrahydrofura
n
Urine *Furan, Tetrahydro- (CAS
109-99-9)
2 mg/l MEK Urine *Methyl ethyl ketone (CAS
78-93-3)
* - For sampling details, please see the source document.
Exposure guidelines
US - California OELs: Skin designation
Cyclohexanone (CAS 108-94-1)Can be absorbed through the skin.
US - Minnesota Haz Subs: Skin designation applies
Cyclohexanone (CAS 108-94-1)Skin designation applies.
US - Tennessee OELs: Skin designation
Cyclohexanone (CAS 108-94-1)Can be absorbed through the skin.
US ACGIH Threshold Limit Values: Skin designation
Cyclohexanone (CAS 108-94-1)Can be absorbed through the skin.
Furan, Tetrahydro- (CAS 109-99-9)Can be absorbed through the skin.
US. NIOSH: Pocket Guide to Chemical Hazards
Cyclohexanone (CAS 108-94-1)Can be absorbed through the skin.
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 4 / 10
Explosion-proof general and local exhaust ventilation. Good general ventilation (typically 10 air
changes per hour) should be used. Ventilation rates should be matched to conditions. If
applicable, use process enclosures, local exhaust ventilation, or other engineering controls to
maintain airborne levels below recommended exposure limits. If exposure limits have not been
established, maintain airborne levels to an acceptable level. Eye wash facilities and emergency
shower must be available when handling this product.
Appropriate engineering
controls
Individual protection measures, such as personal protective equipment
Face shield is recommended. Wear safety glasses with side shields (or goggles).Eye/face protection
Skin protection
Wear appropriate chemical resistant gloves.Hand protection
Wear appropriate chemical resistant clothing.Other
If engineering controls do not maintain airborne concentrations below recommended exposure
limits (where applicable) or to an acceptable level (in countries where exposure limits have not
been established), an approved respirator must be worn.
Respiratory protection
Wear appropriate thermal protective clothing, when necessary.Thermal hazards
When using, do not eat, drink or smoke. Always observe good personal hygiene measures, such
as washing after handling the material and before eating, drinking, and/or smoking. Routinely wash
work clothing and protective equipment to remove contaminants.
General hygiene
considerations
9. Physical and chemical properties
Appearance
Liquid.Physical state
Translucent liquid.Form
Clear.Color
Solvent.Odor
Odor threshold Not available.
pH Not available.
Melting point/freezing point Not available.
Initial boiling point and boiling
range
151 °F (66.11 °C)
Flash point -4.0 °F (-20.0 °C)
Evaporation rate 5.5 - 8
Not available.Flammability (solid, gas)
Upper/lower flammability or explosive limits
Flammability limit - lower
(%)
1.8
Flammability limit - upper
(%)
11.8
Explosive limit - lower (%)Not available.
Explosive limit - upper (%)Not available.
Vapor pressure 145 mm Hg @ 20 C
Vapor density 2.5
Relative density 0.9 +/- 0.02
Solubility(ies)
Solubility (water)Negligible
Partition coefficient
(n-octanol/water)
Not available.
Auto-ignition temperature Not available.
Decomposition temperature Not available.
Viscosity 80 - 500 cP
Other information
VOC (Weight %)<510 g/l SCAQMD 1168/M316A
10. Stability and reactivity
The product is stable and non-reactive under normal conditions of use, storage and transport.Reactivity
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 5 / 10
Material is stable under normal conditions.Chemical stability
No dangerous reaction known under conditions of normal use.Possibility of hazardous
reactions
Avoid heat, sparks, open flames and other ignition sources. Avoid temperatures exceeding the
flash point. Contact with incompatible materials.Conditions to avoid
Acids. Strong oxidizing agents. Ammonia. Amines. Isocyanates. Caustics.Incompatible materials
No hazardous decomposition products are known.Hazardous decomposition
products
11. Toxicological information
Information on likely routes of exposure
Inhalation May be fatal if swallowed and enters airways. Headache. Nausea, vomiting. May cause irritation
to the respiratory system. Vapors have a narcotic effect and may cause headache, fatigue,
dizziness and nausea. Prolonged inhalation may be harmful.
Skin contact Causes skin irritation.
Eye contac Causes serious eye irritation.
Ingestion May be fatal if swallowed and enters airways. Harmful if swallowed. Harmful if swallowed. Droplets
of the product aspirated into the lungs through ingestion or vomiting may cause a serious
chemical pneumonia.
Symptoms related to the
physical, chemical and
toxicological characteristics
Irritation of nose and throat. Aspiration may cause pulmonary edema and pneumonitis. Severe
eye irritation. Symptoms may include stinging, tearing, redness, swelling, and blurred vision. May
cause respiratory irritation. Skin irritation. May cause redness and pain. Symptoms of
overex osure ma be headache, dizziness, tiredness, nausea and vomitin .
Information on toxicological effects
Acute toxicit May be fatal if swallowed and enters airways. Narcotic effects. May cause respiratory irritation.
Test ResultsComponentsSpecies
Acetone (CAS 67-64-1)
LD50 Rabbit
Dermal
Acute
20 ml/kg
LC50 Rat
Inhalation
50 mg/l, 8 Hours
LD50 Rat
Oral
5800 mg/kg
Cyclohexanone (CAS 108-94-1)
LD50 Rabbit
Dermal
Acute
948 mg/kg
LC50 Rat
Inhalation
8000 ppm, 4 hours
LD50 Rat
Oral
1540 mg/kg
* Estimates for product may be based on additional component data not shown.
Causes skin irritation.Skin corrosion/irritation
Causes serious eye irritation.Serious eye damage/eye
irritation
Respiratory or skin sensitization
Respiratory sensitization Not available.
This product is not expected to cause skin sensitization.Skin sensitization
No data available to indicate product or any components present at greater than 0.1% are
mutagenic or genotoxic.Germ cell mutagenicity
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 6 / 10
Carcinogenicity In 2012 USEPA Integrated Risk Information System (IRIS) reviewed a two species inhalation
lifetime study on THF conducted by NTP (1998). Male rats developed renal tumors and female
mice developed liver tumors while neither the female rats nor the male mice showed similar
results. Because the carcinogenic mechanisms could not be identified clearly in either species for
either tumor, the EPA determined that the male rat and female mouse findings are relevant to the
assessment of carcinogenic potential in humans. Therefore, the IRIS review concludes that these
data in aggregate indicate that there is "suggestive evidence of carcinogenic potential" following
exposure to THF by all routes of exposure.
IARC Monographs. Overall Evaluation of Carcinogenicity
Cyclohexanone (CAS 108-94-1) 3 Not classifiable as to carcinogenicity to humans.
Polyvinyl chloride (CAS 9002-86-2) 3 Not classifiable as to carcinogenicity to humans.
OSHA Specifically Regulated Substances (29 CFR 1910.1001-1050)
Polyvinyl chloride (CAS 9002-86-2) Cancer
This product is not expected to cause reproductive or developmental effects.Reproductive toxicity
Specific target organ toxicity -
single exposure
Narcotic effects. May cause drowsiness and dizziness. Respiratory tract irritation.
Specific target organ toxicity -
repeated exposure
Not classified.
Aspiration hazard May be fatal if swallowed and enters airways.
Chronic effects Prolonged inhalation may be harmful.
12. Ecological information
The product is not classified as environmentally hazardous. However, this does not exclude the
possibility that large or frequent spills can have a harmful or damaging effect on the environment.
Ecotoxicity
Components Test ResultsSpecies
Acetone (CAS 67-64-1)
Aquatic
LC50Fish > 100 mg/l, 96 hoursFathead minnow (Pimephales promelas)
* Estimates for product may be based on additional component data not shown.
Cyclohexanone (CAS 108-94-1)
Aquatic
LC50Fish 481 - 578 mg/l, 96 hoursFathead minnow (Pimephales promelas)
No data is available on the degradability of this product.Persistence and degradability
No data available.Bioaccumulative potential
Partition coefficient n-octanol / water (log Kow)
Acetone (CAS 67-64-1)-0.24
Cyclohexanone (CAS 108-94-1)0.81
Furan, Tetrahydro- (CAS 109-99-9)0.46
Methyl ethyl ketone (CAS 78-93-3)0.29
No data available.Mobility in soil
Other adverse effects No other adverse environmental effects (e.g. ozone depletion, photochemical ozone creation
potential, endocrine disruption, global warming potential) are expected from this component.
13. Disposal considerations
Collect and reclaim or dispose in sealed containers at licensed waste disposal site. This material
and its container must be disposed of as hazardous waste. Do not allow this material to drain into
sewers/water supplies. Do not contaminate ponds, waterways or ditches with chemical or used
container. Dispose of contents/container in accordance with local/regional/national/international
regulations.
Disposal instructions
Dispose in accordance with all applicable regulations.Local disposal regulations
The waste code should be assigned in discussion between the user, the producer and the waste
disposal company.
Hazardous waste code
Dispose of in accordance with local regulations. Empty containers or liners may retain some
product residues. This material and its container must be disposed of in a safe manner (see:
Disposal instructions).
Waste from residues / unused
products
Empty containers should be taken to an approved waste handling site for recycling or disposal.
Since emptied containers may retain product residue, follow label warnings even after container is
emptied.
Contaminated packaging
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 7 / 10
14. Transport information
DOT
UN1133UN number
AdhesivesUN proper shipping name
3Class
Transport hazard class(es)
-Subsidiary risk
3Label(s)
IIPacking group
Read safety instructions, SDS and emergency procedures before handling.Special precautions for user
T11, TP1, TP8, TP27Special provisions
Packaging exceptions
Packaging non bulk
150
201
243Packaging bulk
IATA
UN1133UN number
AdhesivesUN proper shipping name
3Class
Transport hazard class(es)
-Subsidiary risk
IIPacking group
No.Environmental hazards
3LERG Code
Read safety instructions, SDS and emergency procedures before handling.Special precautions for user
IMDG
UN number UN1133
ADHESIVESUN proper shipping name
3Class
Transport hazard class(es)
-Subsidiary risk
IIPacking group
Environmental hazards
Marine pollutant No.
EmS F-E, S-D
Special precautions for user Read safety instructions, SDS and emergency procedures before handling.
Not available.Transport in bulk according to
Annex II of MARPOL 73/78 and
the IBC Code
15. Regulatory information
This product is a "Hazardous Chemical" as defined by the OSHA Hazard Communication
Standard, 29 CFR 1910.1200.
All components are on the U.S. EPA TSCA Inventory List.
US federal regulations
TSCA Section 12(b) Export Notification (40 CFR 707, Subpt. D)
Not regulated.
OSHA Specifically Regulated Substances (29 CFR 1910.1001-1050)
Polyvinyl chloride (CAS 9002-86-2)Cancer
Central nervous system
Liver
Blood
Flammability
CERCLA Hazardous Substance List (40 CFR 302.4)
Acetone (CAS 67-64-1)LISTED
Cyclohexanone (CAS 108-94-1)LISTED
Furan, Tetrahydro- (CAS 109-99-9)LISTED
Methyl ethyl ketone (CAS 78-93-3)LISTED
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 8 / 10
Superfund Amendments and Reauthorization Act of 1986 (SARA)
Immediate Hazard - Yes
Delayed Hazard - No
Fire Hazard - Yes
Pressure Hazard - No
Reactivity Hazard - No
Hazard categories
SARA 302 Extremely hazardous substance
Not listed.
NoSARA 311/312 Hazardous
chemical
SARA 313 (TRI reporting)
Not regulated.
Other federal regulations
Clean Air Act (CAA) Section 112 Hazardous Air Pollutants (HAPs) List
Not regulated.
Clean Air Act (CAA) Section 112(r) Accidental Release Prevention (40 CFR 68.130)
Not regulated.
Not regulated.Safe Drinking Water Act
(SDWA)
Drug Enforcement Administration (DEA). List 2, Essential Chemicals (21 CFR 1310.02(b) and 1310.04(f)(2) and
Chemical Code Number
Acetone (CAS 67-64-1)6532
Methyl ethyl ketone (CAS 78-93-3)6714
Drug Enforcement Administration (DEA). List 1 & 2 Exempt Chemical Mixtures (21 CFR 1310.12(c))
Acetone (CAS 67-64-1)35 %WV
Methyl ethyl ketone (CAS 78-93-3)35 %WV
DEA Exempt Chemical Mixtures Code Number
Acetone (CAS 67-64-1)6532
Methyl ethyl ketone (CAS 78-93-3)6714
US state regulations
US. Massachusetts RTK - Substance List
Acetone (CAS 67-64-1)
Cyclohexanone (CAS 108-94-1)
Furan, Tetrahydro- (CAS 109-99-9)
Methyl ethyl ketone (CAS 78-93-3)
US. New Jersey Worker and Community Right-to-Know Act
Acetone (CAS 67-64-1)
Cyclohexanone (CAS 108-94-1)
Furan, Tetrahydro- (CAS 109-99-9)
Methyl ethyl ketone (CAS 78-93-3)
Polyvinyl chloride (CAS 9002-86-2)
US. Pennsylvania Worker and Community Right-to-Know Law
Acetone (CAS 67-64-1)
Cyclohexanone (CAS 108-94-1)
Furan, Tetrahydro- (CAS 109-99-9)
Methyl ethyl ketone (CAS 78-93-3)
US. Rhode Island RTK
Acetone (CAS 67-64-1)
Cyclohexanone (CAS 108-94-1)
Furan, Tetrahydro- (CAS 109-99-9)
Methyl ethyl ketone (CAS 78-93-3)
US. California Proposition 65
California Safe Drinking Water and Toxic Enforcement Act of 1986 (Proposition 65): This material is not known to contain
any chemicals currently listed as carcinogens or reproductive toxins.
International Inventories
Country(s) or region Inventory name On inventory (yes/no)*
Domestic Substances List (DSL)YesCanada
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 9 / 10
Country(s) or region Inventory name On inventory (yes/no)*
*A "Yes" indicates this product complies with the inventory requirements administered by the governing country(s).
"No" indicates that one or more components of the product are not listed or exempt from listing on the inventory administered by the governing
country(s).
Toxic Substances Control Act (TSCA) Inventory NoUnited States & Puerto Rico
16. Other information, including date of preparation or last revision
05-27-2015Issue date
-Revision date
Version #01
Health: 2
Flammability: 3
Physical hazard: 0
HMIS® ratings
NFPA ratings
02
3
The information in the sheet was written based on the best knowledge and experience currently
available. Oatey Co. cannot anticipate all conditions under which this information and its product,
or the products of other manufacturers in combination with its product, may be used. It is the
user’s responsibility to ensure safe conditions for handling, storage and disposal of the product,
and to assume liability for loss, injury, damage or expense due to improper use.
Disclaimer
SDS USPVC Regular Clear Cement
927170 Version #: 01 Revision date: 11-22-2017 Issue date: 05-27-2015 10 / 10

Appendix E
DEQ Risk Calculator Summary Pages
Version Date:
Basis:
Site Name:
Site Address:
DEQ Section:
Site ID:
Exposure Unit ID:
Submittal Date:
Reviewed By:
Building 1012 Worst Case Residential Scenario (Nov. 2023 Data)
North Carolina Department of Environmental Quality
Risk Calculator
Atando Avenue
1386 Newland Road Charlotte, NC
DEQ DWM Brownfields
Brownfields Project No. 11037-07-060
July 2023
May 2023 EPA RSL Table
Prepared By:Hart & Hickman, PC
Hart & Hickman, PC
North Carolina DEQ Risk Calculator
Table of Contents
Version Date: July 2023
Basis: May 2023 EPA RSL Table
Site ID: Brownfields Project No. 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (Nov. 2023 Data)
Form No.
Input Form 1A Complete Exposure Pathways
Input Form 1B Exposure Factors and Target Risks
Input Form 1C Contaminant Migration Parameters
Input Form 1D Sample Statistics
Input Form 2A Soil Exposure Point Concentration Table
Input Form 2B Groundwater Exposure Point Concentration Table
Input Form 2C Surface Water Exposure Point Concentration Table
Input Form 2D Soil Gas Exposure Point Concentration Table
Input Form 2E Indoor Air Exposure Point Concentration Table
Output Form 1A Risk for Individual Pathways
Output Form 1B Sitewide Risk
Output Form 2A Resident Soil
Output Form 2B Resident Groundwater Use
Output Form 2C Non-Residential Worker Soil
Output Form 2D Non-Residential Worker Groundwater Use
Output Form 2E Construction Worker Soil
Output Form 2F Recreator/Trespasser Soil
Output Form 2G Recreator/Trespasser Surface Water
Output Form 3A Resident Groundwater to Indoor Air
Output Form 3B Resident Soil Gas to Indoor Air
Output Form 3C Resident Indoor Air
Output Form 3D Non-Residential Worker Groundwater to Indoor Air
Output Form 3E Non-Residential Worker Soil Gas to Indoor Air
Output Form 3F Non-Residential Worker Indoor Air
Output Form 4A Soil to Groundwater - Forward Mode
Output Form 4B Groundwater to Groundwater - Forward Mode
Output Form 4C Soil to Surface Water - Forward Mode
Output Form 4D Groundwater to Surface Water - Forward Mode
Output Form 4E Soil to Groundwater - Backward Mode
Output Form 4F Groundwater to Groundwater - Backward Mode
Output Form 4G Soil to Surface Water - Backward Mode
Output Form 4H Groundwater to Surface Water - Backward Mode
Output Section 4 - Contaminant Migration Worksheets
Output Section 3 - Vapor Intrusion Calculators
TOC
Description
DATA INPUT SHEETS
Check box
if included
Input Section 1 - Exposure Pathways & Parameters
Input Section 2 - Exposure Point Concentrations
DATA OUTPUT SHEETS
Output Section 1 - Summary Output for All Calculators
Output Section 2 - Direct Contact Soil and Groundwater Calculators
North Carolina DEQ Risk Calculator
Complete Exposure Pathways
Version Date: July 2023
Basis: May 2023 EPA RSL Table
Site ID: Brownfields Project No. 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (Nov. 2023 Data)
Note: Risk output will only be calculated for complete exposure pathways.
Receptor Pathway
Check box if
pathway
complete
Soil
Groundwater Use
Soil
Groundwater Use
Construction Worker Soil
Soil
Surface Water
Groundwater to Indoor Air
Soil Gas to Indoor Air
Indoor Air
Groundwater to Indoor Air
Soil Gas to Indoor Air
Indoor Air
Source Soil
Source Groundwater
Source Soil
Source Groundwater
Resident
Non-Residential Worker
CONTAMINANT MIGRATION PATHWAYS
Groundwater
Surface Water
Input Form 1A
VAPOR INTRUSION PATHWAYS
DIRECT CONTACT SOIL AND WATER PATHWAYS
Resident
Non-Residential Worker
Recreator/Trespasser
North Carolina DEQ Risk Calculator
Exposure Point Concentrations
Version Date: July 2023
Basis: May 2023 EPA RSL Table
Site ID: Brownfields Project No. 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (Nov. 2023 Data)
Description of Exposure Point Concentration Selection:
Exposure Point
Concentration
(ug/m3)
Notes: CAS Number Chemical
Minimum
Concentration
(Qualifier)
Maximum
Concentration
(Qualifier)
Units
Location of
Maximum
Concentration
Detection
Frequency
Range of
Detection
Limits
Concentration
Used for
Screening
Background
Value
Screening
Toxicity Value
(Screening
Level) (n/c)
Potential
ARAR/TBC
Value
Potential
ARAR/TBC
Source
COPC Flag
(Y/N)
Rationale for
Selection or
Deletion
39,100 E, SSV-1012-B 67-64-1 Acetone ug/m3
2.94 MDL, SSV-1012-B/DUP/D 100-44-7 Benzyl Chloride ug/m3
3 MDL, SSV-1012-B/DUP/D 75-27-4 Bromodichloromethane ug/m3
6.53 MDL, SSV-1012-B/DUP/D 106-99-0 Butadiene, 1,3-ug/m3
6.04 J, SSV-1012-D 75-15-0 Carbon Disulfide ug/m3
13.1 J, SSV-1012-D 74-87-3 Chloromethane ug/m3
3.02 MDL, SSV-1012-B/DUP/D 106-93-4 Dibromoethane, 1,2-ug/m3
113,000 E, SSV-1012-D 109-99-9 ~Tetrahydrofuran ug/m3
6.62 MDL, SSV-1012-B/DUP/D 87-68-3 Hexachlorobutadiene ug/m3
101 SSV-1012-D 67-63-0 Isopropanol ug/m3
7,710 SS-1012-B 78-93-3 Methyl Ethyl Ketone (2-Butanone)ug/m3
3.66 MDL, SSV-1012-B/DUP/D 91-20-3 ~Naphthalene ug/m3
2.08 MDL, SSV-1012-B/DUP/D 79-34-5 Tetrachloroethane, 1,1,2,2-ug/m3
184 SSV-1012-D 108-88-3 Toluene ug/m3
111 SSV-1012-B 120-82-1 Trichlorobenzene, 1,2,4-ug/m3
1.75 MDL, SSV-1012-B/DUP/D 79-00-5 Trichloroethane, 1,1,2-ug/m3
7.99 J, SS-1012-B 108-38-3 Xylene, m-ug/m3
7.99 J, SS-1012-B 1330-20-7 Xylenes ug/m3
Input Form 2D
Soil Gas Exposure Point Concentration Table
Note: Chemicals highlighted in orange are non-volatile chemicals. Since these chemicals do not pose a vapor intrusion risk, no risk values are calculated for these chemicals.
If the chemical list is changed from a prior calculator run, remember to select "See All Chemicals" on the data output sheet or newly added chemicals will not be included in risk calculations
North Carolina DEQ Risk Calculator
Risk for Individual Pathways Output Form 1A
Version Date: July 2023
Basis: May 2023 EPA RSL Table
Site ID: Brownfields Project No. 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (Nov. 2023 Data)
Receptor Pathway Carcinogenic
Ris Hazard Index Risk exceeded?
Soil NC NC NC
Groundwater Use* NC NC NC
Soil NC NC NC
Groundwater Use* NC NC NC
Construction Worker Soil NC NC NC
Soil NC NC NC
Surface Water* NC NC NC
Receptor Pathway Carcinogenic
Ris Hazard Index Risk exceeded?
Groundwater to Indoor Air NC NC NC
Soil Gas to Indoor Air 2.9E-05 3.8E+00 YES
Indoor Air NC NC NC
Groundwater to Indoor Air NC NC NC
Soil Gas to Indoor Air NC NC NC
Indoor Air NC NC NC
Pathway Source
Source Soil NC
Source Groundwater NC
Source Soil NC
Source Groundwater NC
Groundwater Exceedence of 2L at Receptor?
Exceedence of 2L at Receptor?
1. If lead concentrations were entered in the exposure point concentration tables, see the individual calculator sheets for lead
concentrations in comparison to screening levels. Note that lead is not included in cumulative risk calculations.
Notes:
3. NM = Not modeled, user did not check this pathway as complete.
4. NC = Pathway not calculated, required contaminant migration parameters were not entered.
DIRECT CONTACT SOIL AND WATER CALCULATORS
Resident
Non-Residential Worker
Recreator/Trespasser
2. * = If concentrations in groundwater exceed the NC 2L Standards or IMAC, or concentrations in surface water exceed the
NC 2B Standards, appropriate remediation and/or institutional control measures will be necessary to be eligible for a risk-based
closure.
Surface Water Exceedence of 2B at Receptor?
Exceedence of 2B at Receptor?
VAPOR INTRUSION CALCULATORS
Resident
Non-Residential Worker
CONTAMINANT MIGRATION CALCULATORS
Target Receptor Concentrations Exceeded?
North Carolina DEQ Risk Calculator
DEQ Risk Calculator - Vapor Intrusion - Resident Soil Gas to Indoor Air
Version Date: July 2023
Basis: May 2023 EPA RSL Table
Site ID: Brownfields Project No. 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (Nov. 2023 Data)
CAS # Chemical Name:
Soil Gas
Concentration
(ug/m3)
Calculated
Indoor Air
Concentration
(ug/m3)
Target Indoor
Air Conc. for
Carcinogens @
TCR = 1E-06
Target Indoor Air
Conc. for Non-
Carcinogens @
THQ = 0.2
Calculated
Carcinogenic
Risk
Calculated
Non-
Carcinogenic
Hazard
Quotient
67-64-1 Acetone 39100 1173 - -
100-44-7 Benzyl Chloride 2.94 0.0882 5.7E-02 2.1E-01 1.5E-06 8.5E-02
75-27-4 Bromodichloromethane 3 0.09 7.6E-02 -1.2E-06
106-99-0 Butadiene, 1,3- 6.53 0.1959 9.4E-02 4.2E-01 2.1E-06 9.4E-02
75-15-0 Carbon Disulfide 6.04 0.1812 - 1.5E+02 2.5E-04
74-87-3 Chloromethane 13.1 0.393 - 1.9E+01 4.2E-03
106-93-4 Dibromoethane, 1,2- 3.02 0.0906 4.7E-03 1.9E+00 1.9E-05 9.7E-03
109-99-9 ~Tetrahydrofuran 113000 3390 - 4.2E+02 1.6E+00
87-68-3 Hexachlorobutadiene 6.62 0.1986 1.3E-01 -1.6E-06
67-63-0 Isopropanol 101 3.03 - 4.2E+01 1.5E-02
78-93-3 Methyl Ethyl Ketone (2-Butanone) 7710 231.3 - 1.0E+03 4.4E-02
91-20-3 ~Naphthalene 3.66 0.1098 8.3E-02 6.3E-01 1.3E-06 3.5E-02
79-34-5 Tetrachloroethane, 1,1,2,2- 2.08 0.0624 4.8E-02 -1.3E-06
108-88-3 Toluene 184 5.52 - 1.0E+03 1.1E-03
120-82-1 Trichlorobenzene, 1,2,4- 111 3.33 - 4.2E-01 1.6E+00
79-00-5 Trichloroethane, 1,1,2- 1.75 0.0525 1.8E-01 4.2E-02 3.0E-07 2.5E-01
108-38-3 Xylene, m- 7.99 0.2397 - 2.1E+01 2.3E-03
1330-20-7 Xylenes 7.99 0.2397 - 2.1E+01 2.3E-03
Cumulative: 2.9E-05 3.8E+00
All concentrations are in ug/m3
Output Form 3B
Carcinogenic risk and hazard quotient cells highlighted in orange are associated with non-volatile chemicals. Since these chemicals do not pose a vapor intrusion
risk, no risk values are calculated for these chemicals.
North Carolina DEQ Risk Calculator
Version Date:
Basis:
Site Name:
Site Address:
DEQ Section:
Site ID:
Exposure Unit ID:
Submittal Date:
Reviewed By:
Prepared By:Hart & Hickman, PC
Hart & Hickman, PC
Building 1012 Worst Case Residential Scenario (April 2024 Data)
North Carolina Department of Environmental Quality
Risk Calculator
Atando - Double Oaks
1386 Newland Road, Charlotte, NC
Brownfields Redevelopment Section
11037-07-060
February 2024
November 2023 EPA RSL Table
North Carolina DEQ Risk Calculator
Table of Contents
Version Date: February 2024
Basis: November 2023 EPA RSL Table
Site ID: 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (April 2024 Data)
Form No.
Input Form 1A Complete Exposure Pathways
Input Form 1B Exposure Factors and Target Risks
Input Form 1C Contaminant Migration Parameters
Input Form 1D Sample Statistics
Input Form 2A Soil Exposure Point Concentration Table
Input Form 2B Groundwater Exposure Point Concentration Table
Input Form 2C Surface Water Exposure Point Concentration Table
Input Form 2D Soil Gas Exposure Point Concentration Table
Input Form 2E Indoor Air Exposure Point Concentration Table
Output Form 1A Risk for Individual Pathways
Output Form 1B Sitewide Risk
Output Form 2A Resident Soil
Output Form 2B Resident Groundwater Use
Output Form 2C Non-Residential Worker Soil
Output Form 2D Non-Residential Worker Groundwater Use
Output Form 2E Construction Worker Soil
Output Form 2F Recreator/Trespasser Soil
Output Form 2G Recreator/Trespasser Surface Water
Output Form 3A Resident Groundwater to Indoor Air
Output Form 3B Resident Soil Gas to Indoor Air
Output Form 3C Resident Indoor Air
Output Form 3D Non-Residential Worker Groundwater to Indoor Air
Output Form 3E Non-Residential Worker Soil Gas to Indoor Air
Output Form 3F Non-Residential Worker Indoor Air
Output Form 4A Soil to Groundwater - Forward Mode
Output Form 4B Groundwater to Groundwater - Forward Mode
Output Form 4C Soil to Surface Water - Forward Mode
Output Form 4D Groundwater to Surface Water - Forward Mode
Output Form 4E Soil to Groundwater - Backward Mode
Output Form 4F Groundwater to Groundwater - Backward Mode
Output Form 4G Soil to Surface Water - Backward Mode
Output Form 4H Groundwater to Surface Water - Backward Mode
Output Section 4 - Contaminant Migration Worksheets
Output Section 3 - Vapor Intrusion Calculators
TOC
Description
DATA INPUT SHEETS
Check box
if included
Input Section 1 - Exposure Pathways & Parameters
Input Section 2 - Exposure Point Concentrations
DATA OUTPUT SHEETS
Output Section 1 - Summary Output for All Calculators
Output Section 2 - Direct Contact Soil and Groundwater Calculators
North Carolina DEQ Risk Calculator
Complete Exposure Pathways
Version Date: February 2024
Basis: November 2023 EPA RSL Table
Site ID: 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (April 2024 Data
Note: Risk output will only be calculated for complete exposure pathways.
Receptor Pathway
Check box if
pathway
complete
Soil
Groundwater Use
Soil
Groundwater Use
Construction Worker Soil
Soil
Surface Water
Groundwater to Indoor Air
Soil Gas to Indoor Air
Indoor Air
Groundwater to Indoor Air
Soil Gas to Indoor Air
Indoor Air
Source Soil
Source Groundwater
Source Soil
Source Groundwater
Input Form 1A
VAPOR INTRUSION PATHWAYS
DIRECT CONTACT SOIL AND WATER PATHWAYS
Resident
Non-Residential Worker
Recreator/Trespasser
Resident
Non-Residential Worker
CONTAMINANT MIGRATION PATHWAYS
Groundwater
Surface Water
North Carolina DEQ Risk Calculator
Exposure Point Concentrations
Version Date: February 2024
Basis: November 2023 EPA RSL Table
Site ID: 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (April 2024 Data)
Description of Exposure Point Concentration Selection:
Exposure Point
Concentration
(ug/m3)
Notes: CAS Number Chemical
Minimum
Concentration
(Qualifier)
Maximum
Concentration
(Qualifier)
Units
Location of
Maximum
Concentration
Detection
Frequency
Range of
Detection
Limits
Concentration
Used for
Screening
Background
Value
Screening
Toxicity Value
(Screening
Level) (n/c)
Potential
ARAR/TBC
Value
Potential
ARAR/TBC
Source
COPC Flag
(Y/N)
Rationale for
Selection or
Deletion
832 SS-1012-D 67-64-1 Acetone ug/m3
0.469 J, SS-1012-DUP 71-43-2 Benzene ug/m3
0.713 J,B, SS-1012-DUP 75-15-0 Carbon Disulfide ug/m3
1.24 J, SS-1012-B 67-66-3 Chloroform ug/m3
0.526 J, SS-1012-DUP 74-87-3 Chloromethane ug/m3
1.91 J, SS-1012-B 110-82-7 Cyclohexane ug/m3
2.42 J, SS-1012-DUP 75-71-8 Dichlorodifluoromethane ug/m3
1.84 SS-1012-D 141-78-6 Ethyl Acetate ug/m3
0.577 J, SS-1012-DUP 100-41-4 Ethylbenzene ug/m3
2410 SS-1012-D 109-99-9 ~Tetrahydrofuran ug/m3
21.8 SS-1012-D 67-63-0 Isopropanol ug/m3
231 SS-1012-D 78-93-3 Methyl Ethyl Ketone (2-Butanone)ug/m3
0.778 J, SS-1012-DUP 75-09-2 Methylene Chloride ug/m3
0.353 J, SS-1012-DUP 100-42-5 Styrene ug/m3
1.26 J, SS-1012-D 127-18-4 Tetrachloroethylene ug/m3
2.72 SS-1012-DUP 108-88-3 Toluene ug/m3
1.88 J, SS-1012-DUP 75-69-4 Trichlorofluoromethane ug/m3
1.66 J, SS-1012-D 95-63-6 Trimethylbenzene, 1,2,4-ug/m3
0.565 J, SS-1012-D 108-67-8 Trimethylbenzene, 1,3,5-ug/m3
2.47 J, SS-1012-D 108-38-3 Xylene, m-ug/m3
1.35 J, SS-1012-D 95-47-6 Xylene, o-ug/m3
Input Form 2D
Soil Gas Exposure Point Concentration Table
Note: Chemicals highlighted in orange are non-volatile chemicals. Since these chemicals do not pose a vapor intrusion risk, no risk values are calculated for these chemicals.
If the chemical list is changed from a prior calculator run, remember to select "See All Chemicals" on the data output sheet or newly added chemicals will not be included in risk calculations
North Carolina DEQ Risk Calculator
Risk for Individual Pathways Output Form 1A
Version Date: February 2024
Basis: November 2023 EPA RSL Table
Site ID: 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (April 2024 Data)
Receptor Pathway Carcinogenic
Ris Hazard Index Risk exceeded?
Soil NC NC NC
Groundwater Use* NC NC NC
Soil NC NC NC
Groundwater Use* NC NC NC
Construction Worker Soil NC NC NC
Soil NC NC NC
Surface Water* NC NC NC
Receptor Pathway Carcinogenic
Ris Hazard Index Risk exceeded?
Groundwater to Indoor Air NC NC NC
Soil Gas to Indoor Air 3.6E-07 4.5E-02 NO
Indoor Air NC NC NC
Groundwater to Indoor Air NC NC NC
Soil Gas to Indoor Air NC NC NC
Indoor Air NC NC NC
Pathway Source
Source Soil NC
Source Groundwater NC
Source Soil NC
Source Groundwater NC
3. NM = Not modeled, user did not check this pathway as complete.
4. NC = Pathway not calculated, required contaminant migration parameters were not entered.
DIRECT CONTACT SOIL AND WATER CALCULATORS
Resident
Non-Residential Worker
Recreator/Trespasser
2. * = If concentrations in groundwater exceed the NC 2L Standards or IMAC, or concentrations in surface water exceed the
NC 2B Standards, appropriate remediation and/or institutional control measures will be necessary to be eligible for a risk-based
closure.
Surface Water Exceedence of 2B at Receptor?
Exceedence of 2B at Receptor?
VAPOR INTRUSION CALCULATORS
Resident
Non-Residential Worker
CONTAMINANT MIGRATION CALCULATORS
Target Receptor Concentrations Exceeded?
Groundwater Exceedence of 2L at Receptor?
Exceedence of 2L at Receptor?
1. If lead concentrations were entered in the exposure point concentration tables, see the individual calculator sheets for lead
concentrations in comparison to screening levels. Note that lead is not included in cumulative risk calculations.
Notes:
North Carolina DEQ Risk Calculator
DEQ Risk Calculator - Vapor Intrusion - Resident Soil Gas to Indoor Air
Version Date: February 2024
Basis: November 2023 EPA RSL Table
Site ID: 11037-07-060
Exposure Unit ID: Building 1012 Worst Case Residential Scenario (April 2024 Data)
CAS # Chemical Name:
Soil Gas
Concentration
(ug/m3)
Calculated
Indoor Air
Concentration
(ug/m3)
Target Indoor
Air Conc. for
Carcinogens @
TCR = 1E-06
Target Indoor Air
Conc. for Non-
Carcinogens @
THQ = 0.2
Calculated
Carcinogenic
Risk
Calculated
Non-
Carcinogenic
Hazard
Quotient
67-64-1 Acetone 832 24.96 - -
71-43-2 Benzene 0.469 0.01407 3.6E-01 6.3E+00 3.9E-08 4.5E-04
75-15-0 Carbon Disulfide 0.713 0.02139 - 1.5E+02 2.9E-05
67-66-3 Chloroform 1.24 0.0372 1.2E-01 2.0E+01 3.0E-07 3.6E-04
74-87-3 Chloromethane 0.526 0.01578 - 1.9E+01 1.7E-04
110-82-7 Cyclohexane 1.91 0.0573 - 1.3E+03 9.2E-06
75-71-8 Dichlorodifluoromethane 2.42 0.0726 - 2.1E+01 7.0E-04
141-78-6 Ethyl Acetate 1.84 0.0552 - 1.5E+01 7.6E-04
100-41-4 Ethylbenzene 0.577 0.01731 1.1E+00 2.1E+02 1.5E-08 1.7E-05
109-99-9 ~Tetrahydrofuran 2410 72.3 - 4.2E+02 3.5E-02
67-63-0 Isopropanol 21.8 0.654 - 4.2E+01 3.1E-03
78-93-3 Methyl Ethyl Ketone (2-Butanone) 231 6.93 - 1.0E+03 1.3E-03
75-09-2 Methylene Chloride 0.778 0.02334 1.0E+02 1.3E+02 2.3E-10 3.7E-05
100-42-5 Styrene 0.353 0.01059 - 2.1E+02 1.0E-05
127-18-4 Tetrachloroethylene 1.26 0.0378 1.1E+01 8.3E+00 3.5E-09 9.1E-04
108-88-3 Toluene 2.72 0.0816 - 1.0E+03 1.6E-05
75-69-4 Trichlorofluoromethane 1.88 0.0564 - -
95-63-6 Trimethylbenzene, 1,2,4- 1.66 0.0498 - 1.3E+01 8.0E-04
108-67-8 Trimethylbenzene, 1,3,5- 0.565 0.01695 - 1.3E+01 2.7E-04
108-38-3 Xylene, m- 2.47 0.0741 - 2.1E+01 7.1E-04
95-47-6 Xylene, o- 1.35 0.0405 - 2.1E+01 3.9E-04
Cumulative: 3.6E-07 4.5E-02
All concentrations are in ug/m3
Output Form 3B
Carcinogenic risk and hazard quotient cells highlighted in orange are associated with non-volatile chemicals. Since these chemicals do not pose a vapor intrusion
risk, no risk values are calculated for these chemicals.
North Carolina DEQ Risk Calculator