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HomeMy WebLinkAbout23068_Sir Walter Gun Club_DM_20221114DECISION MEMORANDUM DATE: November 14, 2022 FROM: Brad Atkinson/Sharon Eckard TO: Brownfields Assessment File RE: Sir Walter Gun Club 520 Hinton Pond Road 0 Hinton Oaks Boulevard 810 Silverpoint Drive Knightdale, Wake County Brownfields Project No. 23068-19-092 Based on the following information, it has been determined that the above referenced site, whose intended use is for no uses other than industrial (including flex buildings), office, retail, warehousing, hotel, associated parking, and subject to DEQ's prior written approval, other commercial uses, can be made suitable for such uses. Introduction: The Prospective Developer (PD) is Merritt - MW 1, LLC, a manager -managed limited liability corporation, headquartered at 2066 Lord Baltimore Dr., Baltimore, Maryland 21244. Merritt Properties, LLC is the managing member of Merritt - MW 1, LLC. Merritt Properties, LLC's Project Manager is Nathan Robb, of the same address. The PD purchased the brownfields property on May 12, 2021. The Brownfields Property Application (BPA) was originally for four parcels (Wake County PINS 1744479093, 1744476090, 1744566995, and 1744479612 totaling approximately 46.212 acres; however, the PD did not purchase all of this property, and Wake County has subdivided, recombined the parcels and reassigned numbers for the remainder of that property, so that the Brownfields Property is now comprised of four parcels (PINS 1744476090, 1744467994, 1744573498 and 1744565659) totaling approximately 36.686 acres located at 810 Silverpoint Drive, 0 Hinton Oaks Blvd and 520 Hinton Pond Road in Knightdale, Wake County. The site is roughly bisected by a buffered stream which flows from the southeast corner to the northwest corner of the Brownfields Property. There are ponded and wetland areas at the Brownfields Property. The parcels south of the stream were historically used by the Sir Walter Gun Club as a recreational shooting range consisting of a combined pistol and rifle range and a combined skeet and trap field. The former pistol range was located in an area that is now south of the southern boundary of the Brownfields Property, and which underlies a portion of the shopping center located immediately adjacent to the Brownfields Property. Redevelopment Plans: The PD intends to invest approximately $41.5 million to redevelop the site with five flex - style buildings totaling approximately 271,450 square feet designed for industrial Sir Walter Gun Club/23068-19-092/14Nov2022 (including flex buildings), office, and retail use. Redevelopment is limited to areas outside the wetland on the topographic ridges of the Brownfields Property. Based on the assessment and risk evaluation with the risk calculator, vapor mitigation is not required at the site. Site History: The Brownfields Property was part of the historic Midway Plantation, much of which has been subdivided into commercial lots for redevelopment. The former Sir Walter Gun Club (Gun Club) site is located on one of the remaining undeveloped parcels. The Gun Club leased a portion of the property from about 1958 until 1988 for use as a recreational firing range. Range facilities historically operated by the Gun Club at the site consisted of two adjacent rifle ranges with nominal target distances of 100 and 200 yards; a 50-yard pistol range (which was not located on the Brownfields Property); and a combined skeet and trap field. The rifle ranges included earthen backstops (impact berms), which were approximately 10 feet high and appear to have been constructed from soil obtained onsite. The skeet field was located immediately east of the 100-yard rifle range, which was separated from it by an earthen side berm approximately 80 feet long and 7 feet high. The pistol range, which has been removed and covered by commercial development, was formerly located on a parcel immediately south of the Brownfields Property that was subdivided and sold in 2005. Historic use as a shooting range resulted in contamination of the soil with lead and polycyclic aromatic hydrocarbons (PAHs). On November 9, 1988, Mr. Stanley Atwood, a toxicologist with the North Carolina Division of Health Services, Waste Management Superfund Branch, collected soil samples from the pistol range, rifle ranges, and the skeet field for laboratory analysis of metals (arsenic, barium, cadmium, chromium, copper, lead, mercury, and selenium) and semi -volatile organic compounds (SVOCs). The results were reported in a January 31, 1989 internal memorandum from Mr. Atwood to the Director of Budget and Analysis. In summary, the Atwood memorandum stated there were high levels of lead in each of the three berms and low levels of several PAHs in the berms at the pistol range and the 100-yard rifle range. IHSB Site ID NONCD0000019: The Gun Club has been listed on the DEQ Inactive Hazardous Waste Sites Priority List since at least 1991 (Site ID #NONCD0000019). In an October 5, 2000 memorandum from Joe Grant, NCDENR Site Evaluation and Removal Branch, to Charlotte Jesneck, Head, Inactive Hazardous Sites Branch, NC Division of Waste Management, the NCDENR determined that the Gun Club site did not warrant further action by the Site Evaluation and Removal Branch. During August and September of 1991, limited excavation, removal, and screening of soils from the impact berms was performed by Paragon Environmental Group, Inc. ("Paragon"), on behalf of the Gun Club. In a March 10, 1992 letter report to the Gun Club, Paragon reported removing bullets and soil from the front (impact) face of each of the three impact berms (100-yard and 200-yard rifle ranges and the 50-yard pistol range), which was processed through a mobile, 2-deck vibratory screening plant. The bullets and soil were reportedly excavated from each impact berm face to a depth of approximately 2 Sir Walter Gun Club/23068-19-092/14Nov2022 12 inches, from the toe of the berm slope to a height of 6 feet above the range floor. Above the 6-foot level, the soil was excavated to a depth of approximately 8 inches. No field observations or laboratory analytical results were provided in the report to explain the choice of excavation depths. The screened soil (i.e., material passing the mesh screen) was reportedly transported to the Sir Walter Gun Club facility in Creedmoor, North Carolina for beneficial reuse as impact -berm material. Reportedly, nineteen 55- gallon drums containing mixed bullets and gravel recovered from the soil were shipped to Master Metals, Inc. (USEPA facility ID Bo. OHD097613871) in Cleveland, Ohio for recycling. A total of 11,992.8 pounds of lead was reportedly recovered and smelted. Additional environmental assessment activities were conducted at the former Gun Club in 2010 (S&ME, Inc.), 2011(S&ME, Inc.), 2013 (AMEC Environment & Infrastructure, Inc.), and 2020 (S&ME, Inc.). Assessment did not identify any impacts to on -site surface water, sediment, or groundwater. Soil was identified at the site with lead concentrations greater than NCDEQ's Industrial Preliminary Soil Remediation Goal (PSRG) for lead of 800 milligrams per kilogram (mg/kg). Soil in the shooting range impact berms was analyzed for Toxicity Characteristic Leaching Procedure (TCLP) for lead and was found to exceed the federal regulatory threshold of five milligrams per liter (mg/L) for disposal of solid waste as non -hazardous (40 CFR § 261.24). During the months of July 2021 and August 2021, remedial action was completed in accordance with the approved Environmental Management Plan (January 15, 2021) and the approved Remedial Action Plan (January 15, 2021). These remedial activities were documented in the Remedial Action Completion Report (S&ME, Inc., December 21, 2021). As a result of the remedial activities, lead -impacted soils with total lead above 400 mg/kg and leachable lead at concentrations greater than 5 milligrams per liter (mg/L) as analyzed by Toxic Characteristic Leaching Potential (TCLP) methods, were blended with a metal stabilization product to regulate pH and form insoluble compounds so lead would not leach from the soil into the environment. The areas of contaminated soil containing lead and PAHs greater than their PSRGs were excavated, blended with a metal stabilization compound called Enviroblend by CCI, and buried under a geotextile fabric at a pre -approved location on the Brownfields Property named the "Soil Management Area", at least five feet below the proposed final grade, in such a way as to minimize contact by soil grading activities, construction activities, or future users of the property. Soil treatment in this way with a metal stabilization product generally rendered the lead non -leachable, but did not reduce the total lead concentrations in soil. The Soil Management Area was covered with a geotextile, at least five feet of engineered demonstrably clean backfill from the site compacted per engineering specifications, and covered with asphalt pavement to be used as a parking lot. The Soil Management Area is identified on the Brownfields Survey Plat. Generally all the soil represented by most of the data on the Brownfields Agreement's Exhibit 2 was managed by this method and placed in the Soil Management Area. See draft map and cross section appended to the end of this Decision Memo. Sir Walter Gun Club/23068-19-092/14Nov2022 Potential receptors: Potential receptors are non-residential workers, construction workers, hotel guests, and trespassers. Contaminated Media: DEQ has evaluated data collected from the following media at the subject property: soil; groundwater, surface water, and sediment from the on -site stream. DEQ relies on the following data to base its conclusions regarding the subject property and its suitability for its intended reuse. Please see the Brownfield Agreement's Exhibit 2 for specific sample locations, dates, and contaminants of concern (COCs). Risk Calculations Risk calculations were performed using the January 2022 DEQ Risk Calculator: hgps:Hdeg.nc. goy/permits-rules/risk-based-remediation/risk-evaluation-resources. For the purposes of looking at the site spatially, the site was divided into two source areas: the Soil Management Area (soil only) and the remainder of the Brownfields Property (post-remediation), that included post-remediation soil, groundwater, surface water, and sediment. Risk Calculator output for Soil Management Area. No data other than soil data is included. Risk for Individual Pathways I I i Version Date: January 2022 Basis: November 2021 EPA RSL Table Site ID: 23068-19-092 Exposure Unit ID: Soil Mana went Area DIRECT CONTACT SOIL AND WATER CALCULATORS Receptor Pathway Carcinogenic Risk Hazardlodex Risk exceeded? Resident Soil 2.4E-04 1.2E+00 YES Groundwater Use* NC NC NC Non -Residential Worker Soil 1.4E-05 9.4E-02 NO Groundwater Use* NC NC NC Construction Worker Soil 1.9E-06 2.4E+00 YES Recreator/Trespasser Soil 1.3E-04 6.7E-01 YES Surface Water* NC NC NC VAPOR INTRUSION CALCULATORS Receptor Pathway Carcinogenic Risk Hazard Index Risk exceeded? Resident Groundwater to Indoor Air NC NC NC Soil Gas to Indoor Air NC NC NC Indoor Air NC NC NC Non -Residential Worker Groundwater to Indoor Air NC NC NC Soil Gas to Indoor Air NC NC NC Indoor Air NC NC NC The risk calculator output for the soil in the Soil Management Area, was based on the highest concentrations of lead, the primary risk driver with a maximum concentration of 4 Sir Walter Gun Club/23068-19-092/14Nov2022 11,600 mg/kg in these soils, and PAHs from soil across the site that was placed in the Soil Management Area. Based on the risk calculator output, for the soil in the Soil Management Area, residential, construction worker, and recreator/trespasser exposure scenarios exceed both the acceptable regulatory carcinogenic risk range maximum of lE- 4 and the threshold non -cancer hazard index of 1.0 for direct soil exposure. However, it should be noted that lead concentrations are not incorporated into the risk calculations in the risk calculator and is simply listed in the risk calculator output as greater than screening level (>SL), which for non-residential uses is 800 mg/kg. However, due to the soil management activities including blending with a stabilization agent, a cover, and capping with asphalt pavement, this exposure pathway is rendered incomplete. Consequently, there is no anticipated residential, construction worker, or recreator/trespasser exposure. That and adherence to the institutional controls provided by the Brownfields Agreement should satisfactorily manage environmental risk from lead and PAHs from these site soils. Risk for Individual Pathways IsTrumsi Version Date: January 2022 Basis: November 2021 EPA RSL Table Site ID: 23068-19-092 Ex sureUnit ID: Entire site -excluding Soil Management Area DIRECT CONTACT SOIL AND WATER CALCULATORS Receptor Pathway CarcinogenicHazardlndex Risk Risk exceeded? Resident Soil 2.2E-06 7.5E-03 NO Groundwater Use* 0.0E+00 5.8E-04 NO Non -Residential Worker Soil 1.2E-07 6.0E-04 NO Groundwater Use* 0.0E+00 9.6E-05 NO Construction Worker Soil 1.5E-08 1.7E-02 NO Recreator/Trespasser Soil 1.2E-06 4.2E-03 NO Surface Water* 0.0E+00 2.7E-05 NO VAPOR INTRUSION CALCULATORS Receptor Pathway Carcinogenic Risk Hazardhidex Risk exceeded? Resident Groundwater to Indoor Air 0.0E+00 0.0E+00 NO Soil Gas to Indoor Air NC NC NC Indoor Air NC NC NC Non -Residential Worker Groundwater to Indoor Air 0.0E+00 0.0E+00 NO Soil Gas to Indoor Air NC NC NC Indoor Air NC NC NC The risk calculator output for the remainder of the Brownfields Property that excludes the Soil Management Area is based on in -situ post -excavation soil data, as well as groundwater, surface water, and sediment data. Based on the risk calculator output for the remainder of the Brownfields Property, the acceptable regulatory carcinogenic risk range and the threshold noncancer hazard index of 1.0 are not exceeded for any of the risk scenarios addressed by the risk calculator. 5 Sir Walter Gun Club/23068-19-092/14Nov2022 Groundwater Groundwater is found between 16 and 23 feet below ground surface at the site. Groundwater flow is to the northwest. All wells were sampled during a one-time event, and no compounds were detected above 2L Standards; VOCs were not detected in site groundwater even below 2L standards. There is no ongoing monitoring of groundwater by another NCDEQ program, and there are no known off -site sources of contaminants to groundwater. The groundwater wells onsite were abandoned prior to site redevelopment activities. Surface Water Surface water within the property consists of two unnamed tributaries of Milbumie Creek, which flow from southeast to northwest across the site. A former pond and stream in the southwestern and western areas of the Brownfields Property no longer hold water, presumably due to surface water improvements at the adjacent shopping center. Surface water samples did not exceed NC 2B standards, the EPA National Recommended Water Quality Criteria for aquatic Life & Human Health, nor North Carolina In -Stream Target Values for Surface Waters (July 26, 2021) Exterior Soil Gas No exterior soil gas samples were collected because no source areas pertaining to the presence of volatile organic compounds (VOCs) were identified at the Brownfield Property, and VOCs were not detected in groundwater samples across the Brownfields Property. Sub -Slab Vapor No sub -slab vapor samples were collected because no enclosed buildings, other than small remnant concrete masonry block buildings that were demolished, or remnant slabs existed on the Brownfields Property during the assessment phase. Indoor Air No indoor air samples were collected because no enclosed buildings, other than small remnant concrete masonry block buildings that were demolished were present on the Brownfields Property during the assessment phase. Land Use Restrictions: The Brownfields Agreement for this property will include standard land use restrictions, including, the approved land uses; prohibition of residential, childcare, adult care, and schools; no physical redevelopment without an EMP; redevelopment reporting, restrictions on groundwater and surface water use, soil disturbance and fill/export of soil, known contaminant uses, required final grade sampling; capping of Soil Management Area; notices; access; deed; and land use restriction update provisions. Based on the site -specific data provided to the Brownfields program, the site reuse is suitable for the site as long as the agreed upon land use restrictions in the BFA are abided by. 6 Sir Walter Gun Club/23068-19-092/14Nov2022 Property Management Issues: Construction began in May 2021 under an approved EMP. Soil excavation, blending, and placement of lead -impacted soil in the Soil Management Area occurred during July 2021 and August 2021. The first building (Building B3) of the five buildings planned was completed in August 2022 with construction of two additional buildings expected by the end of 2022. Two more buildings are scheduled to be constructed during 2023 which are north of the first three. Vapor intrusion was not a concern at this Brownfields Property based on known historic uses and groundwater data. An occupancy letter was provided to the PD in May 2022. 7 Sir Walter Gun Club/23068-19-092/14Nov2022 BOUNDARY IPF Og� IPF W/CAP 453 / 3'49�� E / \ CENTERLINE OF CREEK °1 N�$ L100 5, � IS THE PROPERTY LINE SCM-A / 1 38g.6 J % B.M. 2021, PG. 1909 1910 IPF \ 'A-B' L47-L100 / SEE \ L29 0 INSET'A' SCM-B N 1 B.M. 2021, PG. 1909-1910 TOCg m \ rOCB 50' NEUSE co co \ 50' NEUSE RIVER BUFFER SOIL o FROM TOF o FROM TOP OF CREEK BANK MANAGEMENT AREA BC RBF BOTH SIDES 0.131 ACRES r 5,706 S.F. / L182� `1g5 L186�187� A� IPF , 4-e' � �1g1 � L189 L47 PF L178i �g��1g2'L190 A' 119 L180� 19�11.03 L41 IPF � L176\ IPF`(�� L196'' SOIL \A _ �L197-A Ln MANAGEMENT AREA \ ' ' �1gg1�E 114L171 L170 L169 0.164 ACRES J L173 540 7,143 S.F. S 87°22'14" W 255.55' L26' 30' CITY OF RALEIGH L�23\ SANITARY SEWER LL24 L21\ \ \ EASEMENT— L19`,B.M. 2021, PG. 1909-1910 ` \l N 7 L22 L20 ` IPF 50' 2 \ CENTERLINE OF CREEK 2 L18 ; IS THE PROPERTY LINE L7-L26 SB HA-12 50' FR ��n AFT AMSL IL- 2 qo 2-70 Si CZ V) A -it 2 CS t ej C Lw3 I"'I . <- �As Q�14 aj, f . / e, re, / 4( G.S. As kat+ r Ali GC*4-e)culi, I I w I ca n qq I I I � I I I I I A' Cift 4vv.�I,