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Final Grade Soil Sampling Work Plan
HD Supply Brownfields Site
1414 South Tryon Street
Charlotte, North Carolina
Brownfields Project No. 19054-15-060
October 23, 2020
H&H Job No. BCP-064
-
hart Tsw- hickman
SMARTER ENVIRONMENTAL SOLUTIONS
#C-1269 Engineering
#C-245 Geology
2923 South Tryon Street, Suite 100 3921 Sunset Ridge Rd, Suite 301
Charlotte, NC 28203 Raleigh, NC 27607 www.harthickman.com
704.586.0007 main j 919.847.4241 main
Final Grade Soil Sampling Work Plan
HD Supply Brownfields Site
1414 South Tryon Street
Charlotte, North Carolina
Brownfields Project No. 19054-15-060
H&H Job No. BCP-064
Table of Contents
Section
Page No.
1.0 Introduction............................................................................................................................ 1
1.1 Site History........................................................................................................................... 1
1.2 Summary of Previous Assessment and Brownfields Activities ........................................... 2
2.0 Scope of Work........................................................................................................................ 5
2.1 Soil Sampling....................................................................................................................... 5
2.2 Quality Assurance/Quality Control...................................................................................... 6
2.3 Boring Abandonment and Investigation Derived Waste ...................................................... 6
3.0 Reporting................................................................................................................................ 7
List of Tables
Table 1 Proposed Sample Summary
List of Figures
Figure 1 Site Location Map
Figure 2 Site and Sample Location Map
List of Appendix
Appendix A Environmental Site Assessment Work Plan Minimum Requirements Checklist
I
S:\AAA-Master Projects\Beacon Partners- BEP or BCP\BCP-064 1414 and 1422 S. Tryon\Brownfields\Final Grade Sampling Work
Plan\Final Grade Sampling Report - HD Supply.doc
Final Grade Soil Sampling Work Plan
HD Supply Brownfields Site
1414 South Tryon Street
Charlotte, North Carolina
Brownfields Project No. 19054-15-060
H&H Job No. BCP-064
1.0 Introduction
On behalf of RailYard, LLC (Beacon), Hart & Hickman, PC (H&H) has prepared this Final Grade
Soil Sampling Work Plan outlining final grade soil sampling activities to be completed at the HD
Supply Brownfields property (Brownfields Project No. 19054-15-060) located at 1414 South Tryon
Street in Charlotte, Mecklenburg County, North Carolina (Site). A Site location map is provided as
Figure 1.
The HD Supply Brownfields property was initially comprised of one approximately 3.38-acre
parcel of land solely owned by RailYard, LLC (formerly Beacon MPI, LLC). However, RailYard,
LLC sold an approximately 0.74-acre area in the western portion of the Site to Centro RailYard,
LLC on November 27, 2018. Currently, the HD Supply Brownfields property is comprised of two
parcels. The larger approximately 2.77-acres parcel (Parcel No. 07309204) is owned by RailYard,
LLC and has been developed with two multi -purpose high-rise towers (retail and commercial office
space) and a parking deck. The smaller approximately 0.74-acre parcel (Parcel No. 07309217) is
owned by Centro RailYard, LLC and is being developed with a multi -story building including retail
commercial units on the ground floor with multi -family residential apartment units above. A Site
map is provided as Figure 2.
1.1 Site History
Historically, the subject Site was developed with multiple residential structures prior to 1911 based
on review of historic Sanborn Fire Insurance maps. The southeastern portion of the Site was
redeveloped for commercial purposes in 1946 when an approximately 36,000 square foot (sq ft)
multi -use building was constructed. The multi -use building was used as a drycleaner and laundry
facility from initial construction to the late 1960s or early 1970s. From the early 1970s through
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2017 when the building was demolished, the multi -use building was used as a furniture showroom,
offices, and warehouse storage. The western portion of the Site was developed with an
approximately 7,700 sq ft warehouse building in 1984 and was occupied by HD Supply for office
space and electrical supply warehousing from 1984 until 2017 when the building was demolished.
A Site map is provided as Figure 2.
1.2 Previous Brownfields Assessment Activities
Details of previous assessment activities conducted at the Site are provided in the Brownfields
Assessment Report dated June 19, 2017 and the Soil Characterization Report dated January 11,
2019. A brief summary of previous assessment activities detailed in these reports is provided below:
Brownfields Assessment Report
Based on the results of the assessment activities, H&H concluded the following:
• Soil with compound concentrations above Residential and/or Industrial PSRGs is only
present in shallow soil in the area of soil samples SB-4 and SB-6. Results of TCLP analysis
of soil from this area indicates that the soil is not a characteristically hazardous waste.
• Results of the soil gas sampling indicate that concentrations of PCE and 1,2,4-
trimethylbenzene were detected above Residential VISCs in the sample from SG-6 located
below the southwestern portion of the proposed residential apartments. Results of
cumulative risk calculations indicate that cumulative risks for this sample did not exceed the
acceptable LICR risk range of 1 x 10-4 to 1 x 10-6 for potential carcinogenic risks or the
threshold HI of 1 for potential non -carcinogenic risks, although the calculated HI was 0.91
and close to 1. No other soil gas samples in the area of the proposed apartments contained
compound concentrations above Residential SGSLs and no soil gas samples in the area of the
proposed office building contained compound concentrations above Non -Residential SGSLs.
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Based on the results of the assessment activities, H&H recommends the following:
• H&H recommends that shallow soil impacts above PSRGs in the area of borings SB-4/SB-6
be managed in accordance with an Environmental Management Plan (EMP). This soil is
located where the southern office building is proposed. If the building is constructed
concurrently with the rest of the development as currently anticipated, the soil may
potentially be left in place below the building or potentially moved to other areas of the site
to be covered with impervious surface such as the proposed parking deck. If the southern
office building will be constructed after the remainder of the development and this area will
initially be used as green space, then the shallow impacts will likely need to be excavated
and disposed off -site or moved to other areas of the site to be covered with impervious
surface such as the proposed parking deck. The subsurface structure identified in this area
should also be removed as part of the site grading activities.
H&H recommends that vapor mitigation be included for the proposed southern office building.
Because the calculated cumulative HI for sample SG-6 was just below the threshold level of 1, H&H
also recommends that vapor mitigation be included for the southwestern "leg" of the apartment
building in the area of sample SG-6.
Soil Characterization Report
Prior to the start of development activities, H&H characterized soil at the Site to expedite soil
management during development activities. Results of the soil characterization activities are
provided below:
• Analytical results did not indicate the presence of VOCs, SVOCs, or RCRA metals in the
shallow or deep samples collected from Sections 1, 2, 3, or 4 at concentrations above
Residential or Commercial/Industrial PSRGs.
• The shallow soil sample collected from section 5 (SC-5S) indicated the presence of several
SVOCs above laboratory reporting limits, but below Residential and Commercial/Industrial
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PRSGs. Additionally, the polynuclear aromatic hydrocarbons (PAHs) benzo(a)pyrene,
benzo(b)fluoranthene, and dibenz(a,h)anthracene were detected at concentrations above the
Residential PSRGs, but below the Commercial/Industrial PSRGs. Additionally, arsenic was
detected above Residential and Commercial/Residential PSRGs.
• The deeper sample collected from Section 5 did not indicate the presence of VOCs or
SVOCs at concentrations above Residential or Commercial/Industrial PSRGs. Arsenic was
detected at 1.8 J mg/kg in the deeper sample from section 5 which is above the Residential
PSRG, but is below the Commercial/Industrial PSRG.
• The shallow soil sample collected from section 6 indicated the presence of tetrachloroethene
(PCE) at a concentration of 0.0024 mg/kg which is below Residential and
Commercial/Industrial PSRGs. Additionally, arsenic was detected in the shallow sample at a
concentration of 2.2 J mg/kg which is above the Residential PSRG, but below the
Commercial/Industrial PSRG. No other VOCs, SVOCs, or RCRA metals were detected in
the shallow or deeper soil samples collected from section 6 at concentrations above
Residential or Commercial PSRGs.
• Analytical results indicate the presence of PCE and trichloroethene (TCE) at low
concentrations below the Residential and Commercial/Industrial PSRGs in the shallow and
deeper samples collected from section 7. No SVOCs or RCRA metals were detected above
Residential or Commercial PSRGs in the soil samples collected from section 7.
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2.0 Scope of Work
The subject Site is predominately covered with hardscape surfaces with the exception of a small
grassed courtyard located between the two Site tower buildings. As such, the purpose of the final
grade sampling activities will be to collect representative soil samples of the grassed area. The small
courtyard area is depicted on Figure 2.
The proposed final grade soil sampling activities will be performed in general accordance with
DEQ's Inactive Hazardous Sites Branch (IHSB) Guidelines for Assessment and Cleanup
(Guidelines) dated January 2020 and most recent version of the U.S. Environmental Protection
Agency (EPA) Region IV Science and Ecosystem Support Division (SESD) Field Branches Quality
System and Technical Procedures guidance.
2.1 Soil Sampling
H&H proposes to advance three shallow soil borings in the grassed courtyard located between the
northern and southern tower buildings. Soil borings will be advanced to approximately 2 feet (ft)
below ground surface (bgs) at each boring location utilizing a decontaminated stainless -steel hand
auger. Continuous soil samples will be collected from the center of the hand auger bucket at each
soil boring and described for lithologic purposes, observed for the presence of staining, and field
screened for elevated volatile organic vapors using a calibrated photo -ionization detector (PID).
Aliquots of soil from each boring will be placed into a stainless -steel bowl and homogenized to form
one composite soil sample. H&H will also collect a grab sample from one soil boring for laboratory
analysis of volatile organic compounds (VOCs) from the soil boring exhibiting the highest
likelihood for potential impact based on field screening results. If no obvious evidence of impact is
observed at the boring locations, a grab sample will be collected from the 1 ft to 2 ft bgs interval at a
randomly selected soil boring.
The final grade soil samples selected for laboratory analysis will be collected directly into laboratory
supplied glassware, labeled with the sample identification, date, time, and requested analysis and
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placed on ice in a laboratory supplied cooler. The sample will be delivered to a North Carolina
certified laboratory under standard chain of custody protocols for analysis of VOCs by EPA Method
8260, semi -volatile organic compounds (SVOCs) by EPA 8270, and RCRA metals plus hexavalent
chromium by EPA Methods 6020/7471/7199. A sample and analytical summary are provided on
Table 1.
2.2 Quality Assurance/Quality Control
H&H will collect one duplicate soil sample for QA/QC purposes. Additionally, H&H will collect an
equipment blank to evaluate the effectiveness of the field equipment decontamination methods. To
collect the equipment blank, laboratory supplied analyte free water will be poured over the
decontaminated stainless -steel hand auger. The water will be collected off the hand auger directly
into laboratory supplied sample containers. The duplicate soil sample and the equipment blank will
be submitted for analysis of VOCs by EPA Method 8260, SVOCs by EPA 8270, and RCRA metals
plus hexavalent chromium by EPA Methods 6020/7471/7199. H&H will request a Level II QA/QC
data package from the laboratory and the laboratory will report compound detections to the
laboratory -specified method detection limits using J-flags.
2.3 Boring Abandonment and Investigation Derived Waste
Investigation derived waste (IDW) generated during the sampling activities will be thin spread in the
area of generation, unless there is evidence of significant impact (such as free product). If there is
evidence of significant impact, the investigation derived waste from that area will be containerized
in 55-gallon drums. If wastes are containerized, then a composite sample of the materials will be
obtained for waste disposal purposes.
Following sampling activities, the soil borings will be properly abandoned and the surface will be
repaired similar to pre -sampling conditions.
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3.0 Reporting
Following completion of the soil assessment activities and receipt of the analytical data, H&H will
prepare a report which describes the methods and results of the final grade soil sampling activities.
The report will include a description of field activities, field screening results, a tabular summary of
the analytical results in comparison to the DEQ's Preliminary Soil Remediation Goals (PSRGs), risk
calculations, boring logs (will include boring IDs, field screening/PID results, and soil descriptions),
figures depicting the sample locations, laboratory analytical reports including chain of custody
record, a discussion of QA/QC data, and conclusions based upon results of the assessment activities.
The report will be sealed by a North Carolina Professional Engineer (PE) or Professional Geologist
(PG) and the firm PE/PG numbers will be provided.
hart "� hickman
SAAAA-Master Projects\Beacon Partners- BEP or BCP\BCP-064 1414 and 1422 S. Tryon\Brownfields\Final Grade Sampling Work PlanTinal Grade .
Sampling Report - HD Snpply.doc SMARTER ENVIRONMENTAL SOLUTIONS
Table 1
Proposed Sample Summary
HD Supply
1414 South Tryon Street
Charlotte, North Carolina
Brownfields Project No. 19054-15-060
H&H Job No. BCP-064
Number of
RCRA Metals
Hexavalent
Composite Sample
Number of
Sample Depth
composite
VOCs by EPA
SVOCs by EPA
by EPA
Chromium by
Sample Objective
Borings Per
Duplicate
Location Area
Composite Area
(ft)
samples to be
Method 82601
Method 8270
Methods
EPA Method
collected
6020/7471
7199
Future Occupant/Worker
Grassed Courtyard
3
0-2
1
X
X
X
X
X
Protection
Notes
1) The VOC sample will be collected as a grab sample; SVOCs and metals will be field composited from the specified depth interval
VOCs = Volatile Organic Compounds; SVOCs = Semi-VOCs; RCRA = Resource Conservation and Recovery Act
EPA = U.S. Environmental Protection Agency
Table 1 (Page 1 of 1)
S:\AAA-Master Projects\Beacon Partners- BEP or BCP\BCP-0641414 and 1422 S. Tryon\Brownfields\Final Grade Sampling Work Plan\Proposed Sample Summary.xls
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N 0 2000 4000 SITE LOCATION MAP
HD SUPPLY BROWNFIELDS SITE
SCALE IN FEET 1414 SOUTH TRYON STREET
CHARLOTTE, NORTH CAROLINA
CHARLOTTE EAST, NORTH CAROLINA 1991 i 2923 S. Tryon Street, suite 100
hart I hickman Charlotte, NC 28203
U.S.G.S. QUADRANGLE MAP 704.586.0007(p) 704.586.0373(f)
7.5 MINUTE SERIES (TOPOGRAPHIC)
DATE: 11/23/2020 REVISION NO: 0
JOB NO: BCP-064 FIGURE NO: 1
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LEGEND
RAILYARD APARTMENTS
(CENTRO RAILYARD, LLC)
THE RAILYARD (RAILYARD, LLC)
FINAL GRADE SAMPLE LOCATIONS
POTENTIAL AREA OF SOIL
CONTAMINATION
NOTES:
1. AERIAL IMAGERY OBTAINED FROM MECKLENBURG
COUNTY GIS, 2020.
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SCALE IN FEET
SITE MAP
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' f CHARLOTTE, NORTH CAROLINA
2923 South Tryon Street -Suite 100
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Charlotte, North Carolina 28203
704-586-0007(p) 704-586-0373(f)
SMARTER ENVIRONMENTAL SOLUTIONS Licensc # C-1269 / #C-245 Gcolop
y } A DATE: 10-20-20 REVISION NO. 0
y t� JOB NO. BCP-064 FIGURE NO. 2
Appendix A
Environmental Site Assessment Work Plan Minimum Requirements Checklist
Environmental Site Assessment Work Plan
Minimum Requirements Checklist
NCDEQ Brownfields Program — November 2018
Title Page
The title page should include the following information. Letter style reports are acceptable, as long as this
information is somewhere on the first page.
X Title of Work Plan
X Brownfields Project Name (not the development name)
X Brownfields Project Number
X Date (updated with each revision)
X Revision Number
X Firm PE/PG License Number
X Individual PE/PG seal & signature
Section 1— Introduction
X Provide the site location, address, and acreage.
X Provide a BRIEF summary of the history of the property and its history in the program. For example:
reiterating RECs from a Phase I ESA, indicate if the scope of work negotiated during a Data Gap
Meeting, etc.
X Briefly list and describe the data gaps the assessment is attempting to fill
X Indicate if the assessment data is intended for use by any other DEQ programs in addition to the
Brownfields Program (i.e. UST, IHSB, etc.)
Section 2 — Scope of Work
X Provide a general description of proposed scope of work covered in this plan (i.e. 2 new monitoring
wells, six groundwater samples, 5 soil gas sampling points and 6 soil borings)
X Discuss samples to be collected by media and source area/location. Generally, the reasoning for the
sample locations selected.
X Describe depths of samples to be collected (Reference Table 1) or how that decision will be made
X in the field, if needed.
State for what each sample will be analyzed (briefly). Reference Table 1.
Section 3 — Sampling Methodology
X Reference the guidance documents you intend to use. ISHB, EPA SESD, VI Guidance, Well
Construction Rules (NCAC 2C). Note deviations or methodology planned that is not covered by
X such guidance (e.g., multi -increment sampling, passive air samplers).
Describe what will be installed (soil boring, temporary well, permanent well, sub slab, soil gas, etc.).
Include construction details.
X Discuss installation methodology (Hand Auger, DPT, etc.)
X Discuss sample collection procedures. Include the following, at a minimum:
• Equipment to be used
• Purging methods and volumes
• Stabilization parameters for groundwater sampling
• Field screening methods
Work Plan Checklist
Version 1 November 2018
Page 2 of 3
• Leak check procedures for sub -slab and soil gas samples
x
• Discuss how and when vacuum readings will be collected (for summa cans)
Discuss sample point abandonment
Section 4 — Laboratory Analyses
x Discuss the proposed analyses (include method number, preparation method, if there are concerns
with short hold times, etc).
NA Discuss any proposed limitations on the contaminants of concern, if any, and the reason for such
X limitation (sufficient previous data, indoor air interferences, etc).
Discuss laboratory certifications. Please note, NC does not certify labs for air samples. Please
X specify what certification the proposed air lab holds.
Indicate the Reporting Limits/Method Detection Limits will meet applicable screening criteria (to
the extent feasible). Include Reporting of J-Flags to meet criteria.
X Indicate what Level QA/QC will be reported by the laboratory. Level 11 QA/QC is typically
acceptable.
Section 5 — QA/QC
X Specify the duplicate sample frequency. Minimum requirement: 1 duplicate per 20 samples, per
media, per method.
X Discuss Trip Blank. 1 Trip Blank per cooler/shipment of groundwater VOC analyses.
X Discuss how the lab will have sufficient sample volume for MS/MSD analyses.
Discuss chain of custody and shipping.
Section 6 — Investigation Derived Waste (IDW) Management
X Discuss what IDW will be generated and how it is proposed to be managed. Management
recommendations should be in accordance with 15A NCAC 02T.1503 and 15A NCAC 02H. 0106.
Generally, if the Brownfields Property has not previously been assessed, then all IDW must be
containerized and characterized prior to management. Previous assessment data that indicate no
Hazardous Waste (listed or characteristic) is likely to be encountered in the area of proposed
assessment will be required before thin spreading of IDW on -site is permitted.
Section 7 — Reporting
This section should discuss the components of the assessment report which will be prepared as a result of
the above sample collection. At a minimum, the report shall include:
X Reporting/summary of site work conducted for all sections outlined above in this checklist;
X Summary of findings and possible recommendations;
All applicable tables and figures outlined below with the addition of:
Tables for tabulated analytical data per media sampled and analyzed, compared against
applicable screening levels;
Figure depicting actual sample locations collected, with each media depicted in the legend,
graphic scale and north arrow; and
_ Groundwater potentiometric map, with graphic scale and north arrow,
X Firm PE/PG License Number
X Individual PE/PG seal & signature
Work Plan Checklist
Version 1 November 2018
Page 3 of 3
Attachments
X
Table 1 — Proposed Sample Locations and Analyses on a Summary Table that includes:
_ Sample ID
Sample Objective
Proposed Depth(s)
Analytical Method(s)
QA/QC Samples
Background Samples
X Figure 1 — Site Location Map
Site location on a topographic map base.
Graphic scale and north arrow
X Figure 2 — Site Map should include the following
Buildings
_ Historical sample locations
_ RECs or other areas of concern
Proposed sample locations
Sample Identification labels
Background Samples
QA/QC Samples
Graphic scale and north arrow
High quality aerial suggested as the base map
NA Figure 3 — Proposed Development (if available)
Overlay of historical and proposed sample locations,
Graphic scale and north arrow.
NA Appendix — Summary of Historical Analytical Data (if needed)
ROY COOPER NORTH CAROLINA
Governor Environmental Quality
MICHAEL S. REGAN
Secretary October 26, 2020
MICHAEL SCOTT
Director
Sent Via E-Mail
Ralph McGee, PG
Hart & Hickman
2923 South Tryon Street, Suite 100
Charlotte, North Carolina 28203
Subject: Final Grade Soil Sampling Work Plan Approval
HD Supply Brownfields Property
Charlotte, Mecklenburg County
Brownfields Project No. 19054-15-060
Dear Mr. McGee,
The Department of Environmental Quality (DEQ) Brownfields Program received the Final Grade
Soil Sampling Work Plan dated October 23, 2020 for the above referenced Brownfields Property.
DEQ Brownfields reviewed this document and approves the work plan.
Please be advised that this approval from DEQ Brownfields does not waive any applicable
requirement to obtain any necessary permits, licenses or certifications which may be required from
other state or local entities. If you have questions about this correspondence or require additional
information, please feel free to contact me by phone at 704/661-0330 or by email at
carolyn.minnich(c ncdenr.gov
Sincerely,
C'mi— unm-�
Carolyn M ninch
Brownfields Project Manager
ec: Nathan O'Leary nolega&harthickman.com
Jordan Thompson jordan.thompson(ancdenr.gov
c�,DE �Q-
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r—enxonmen� ouei�
North Carolina Department of Environmental Quality I Division of Waste Management
217 West ones Street 11646 Mail Service Center I Raleigh, North Carolina 27699-1646
919,707,8200