HomeMy WebLinkAbout12033_N Tryon Well Installation WP 2013_11_25
Sent Via Email
November 25, 2013
NC DENR Brownfields Section
1314 Mallard Ridge Rd
Tega Cay, SC 29708
Attn: Carolyn F. Minnich
Re: Well Installation and Groundwater Monitoring Work Plan
North Tryon Brownfields Site
Brownfields Project #12033-08-06 Charlotte, North Carolina
H&H Job No. MVT-018
Dear Carolyn:
1.0 Introduction and Background
On behalf of MV Tryon II, LLC (MV Tryon) Hart & Hickman, PC (H&H) is submitting this
Well Installation and Groundwater Monitoring Work Plan (Work Plan) for the North Tryon
Street Site located at 2109 to 2229 North Tryon Street in Charlotte, Mecklenburg County, North
Carolina (Figure 1). Per discussions with the Department of Environment and Natural Resources
(DENR) and in accordance with paragraph 13.d. of the Brownfield Agreement (BFA), a
downgradient monitoring well is to be installed at 2229 North Tryon Street, the former Latimer
Property. Details of the well installation and sampling procedures are described in the following
sections.
The former Latimer property is an approximate 0.23-acre parcel of land located at the west
corner of North Tryon Street and W. 26th Street (Figure 2) and is currently covered with gravel.
According to previous assessment activities, a gas station and dry-cleaning facility previously
operated on the subject property from the 1940s until the 1970s. Site assessment activities
conducted at the property between 2008 and 2013 have indicated the presence of volatile organic
Ms. Carolyn Minnich
November 25, 2013 Page 2
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compounds (VOCs), predominately tetrachloroethene (PCE) and its degradation products above
regulatory screening levels in soil, soil gas, and groundwater.
2.0 Well Installation
The most elevated concentrations of VOCs in groundwater, including PCE up to 6,580 µg/L,
were historically detected in TW-DPT-1. The potentiometric surface generally slopes to the east.
Therefore, the proposed monitoring well will be installed to the east and downgradient of TW-
DPT-1 at the location depicted on Figure 2.
H&H will obtain a Subsurface Investigation Permit (SIP) from Mecklenburg County prior to the
installation of the monitoring well. Prior to installation, H&H will also contact the public utility
locators. In addition, H&H will contract with a private utility locator to clear the proposed
monitoring well location.
The monitoring well will be installed using hollow stem augers by a North Carolina licensed
driller and installed such that the screened interval of the well brackets the water table. In 2008,
groundwater was encountered at the site at 16 to 17 ft below ground surface (bgs). Therefore,
the well will be installed to an estimated depth of 25 ft bgs. The well will be constructed with 2-
inch diameter PVC casing and a 15 ft 0.010-inch PVC well screen.
Following installation, the well will be developed following standard protocol.
3.0 Groundwater Sampling Methods
Per the BFA, a groundwater sample will be collected from the well within two weeks of the well
installation. In addition, the BFA requires annual sampling of the monitoring well for five years
following the initial event.
Ms. Carolyn Minnich
November 25, 2013 Page 3
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Groundwater samples from the monitoring well will be collected using a PVC or polyethylene
bailer. Prior to collecting the sample, the well will be purged and readings of pH, oxidation
reduction potential (ORP), conductivity, and temperature will be recorded until stabilization is
reached. Following stabilization, groundwater samples will be collected directly into laboratory
supplied containers, immediately placed on ice, and shipped to a North Carolina certified
laboratory under standard chain-of-custody protocol. Samples will be analyzed for volatile
organic compounds (VOCs) by EPA Method 8260 and semi-volatile organic compounds
(SVOCs) by EPA Method 8270.
4.0 Investigation Derived Waste
Investigation derived waste (IDW) will be containerized during the monitoring well installation
because concentrations of PCE in groundwater detected in 2008 were up to 6,580 µg/L. Soil
cuttings and development/purge water will be containerized separately. A sample of the soil
cuttings will be collected and analyzed for VOCs using the Toxicity Characteristic Leaching
Procedure (TCLP). Groundwater analytical data will be utilized to profile development and
purge water. Disposal will be based on the results of the analytical data. Should analytical data
indicate that the material is non-hazardous, soil and water will be spread on-site in accordance
with DENR IHSB Guidelines. Purge water from future sampling events would then also be
spread on-site unless concentrations increase and approach characteristically hazardous
thresholds. If analytical data indicate the IDW to be characteristically hazardous, it will be
appropriately profiled and disposed off-site at a facility permitted to accept such waste.
5.0 Reporting
Following initial well installation and sampling, H&H will submit a Groundwater Monitoring
Report detailing the well installation activities and results of the groundwater sampling event.
The report will include a description of the monitoring well installation and sampling methods, a
summary of the groundwater sampling results and field measurements, the laboratory analytical
Ms. Carolyn Minnich
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report along with chain-of-custody, and a site figure. Following each subsequent annual
sampling event, H&H will submit a similar Groundwater Monitoring Report.
If you have any questions or comments, please do not hesitate to contact us.
Sincerely,
Hart & Hickman, PC
Joselyn Harriger, PG Matt Bramblett, PE
Senior Project Geologist Principal
Attachments
cc: Holly Widders, Mount Vernon Asset Management (1 copy via email)
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TITLE
PROJECT
SITE LOCATION MAP
NORTH TRYON ASSEMBLAGE
LATIMER PROPERTY
CHARLOTTE, NORTH CAROLINA
DATE:
JOB NO:
REVISION NO:
FIGURE:
11-13-13 0
1 MVT-018
CHARLOTTE EAST, NC 1967 REVISED/INSPECTED 1988
DERITA, NC 1993
SITE