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HomeMy WebLinkAboutFA-29833_48935_CA_IAR_20230321INITIAL ABATEMENT REPORT 200 HAWKINS AVE SANFORD, NC 27330 PROPERTY OWNER: KPS PROPERTY GROUP, LLC 101 WOLVERINE RD CARY, NC 27513 MARCH 13, 2023 PREPARED FOR: KPS PROPERTY GROUP, LLC 101 WOLVERINE RD CARY, NC 27513 AND COHESION, INC. 5216 YATES MILL POND ROAD RALEIGH, NC 27606-8921 PREPARED BY: JOHN SHERRILL, LG 3326 RUGBY RD DURHAM, NC 27707 SHERRILL@NC.RR.COM PHONE: 919-418-3894 2 TABLE OF CONTENTS ABSTRACT 3 SITE INFORMATION 4 Site Identification 4 Property Owner Information 4 RELEASE INFORMATION 4 SITE HISTORY AND CHARACTERIZATION 4 INITIAL RESPONSE AND ABATEMENT ACTIVITIES 4 Quantity of Regulated Substance Removed from USTs 4 Source Control Actions 5 Contaminant Migration Control Measures 5 Measures taken to Mitigate Fire/Safety Hazards 5 Contaminated Soil Storage, Treatment and/or Disposal 5 Status of Free Product Investigation and Associated Removal 5 SOURCE INVESTIGATION 5 TABLE 7 FIGURES 9 APPENDIX A - FLUID DISPOSAL MANIFEST 14 APPENDIX B - TANK DISPOSAL MANIFEST 16 APPENDIX C - QED SOIL ANALYSIS 18 3 ABSTRACT Cohesion, Inc. was contracted to remove a heating oil underground storage tank. The property is located in a commercial area in downtown Sanford, NC. Lee County records indicate the building was constructed in 1955. The building was constructed for use as funeral services. The building is currently under renovation to be used for office space. On February 8, 2023, Cohesion initiated field activities by removing the concrete floor covering the underground storage tank (UST). On February 9, 2023, a fluid removal contractor pumped and cleaned the tank. On February 16, 2023, Cohesion personnel excavated the overburden and removed the UST. Soil retrieved from beneath the UST exhibited a petroleum odor. Laboratory analysis of retrieved soil detected heating oil type petroleum hydrocarbons exceeding the NCDENR action level of 100 mg/kg, indicating there had been a release from the UST. A soil boring conducted in the pit indicated soil contamination above action levels at a depth of 13.5 feet below ground surface. The former UST was located beneath the concrete floor of the site building. The property owner will likely seek to record a notice of residual petroleum (NRP) due to the location of the contamination. This report was prepared and reviewed under the supervision of John Sherrill, LG of Sherrill Environmental. Sampling and testing procedures were conducted in accordance with the standards of care associated with the equipment and testing methods. Field and lab procedures are regularly monitored for quality assurance. The analytical results contained in this report were generated using a QED Hydrocarbon Analyzer from QROS, Ltd. The QED UVF method is the only NCDEQ approved method for replacement of Gas Chromatography (Method 8015). The system is limited to 1 mg/kg detection limits in soil and 0.05 mg/l in water for most petroleum fuels and oils, which is well within the limits required to perform the analysis herein. 4 SITE INFORMATION Site Identification Report Date: March 13, 2023 Facility I.D. No.: Non-regulated UST Incident No.: TBD Site Name: KPS Property 200 Hawkins Avenue Sanford, NC 27330 Latitude: N 35.48343° Longitude: W -79.17776° Property Owner Information Property Owner: KPS Property Group, LLC 101 Wolverine Road Cary, NC 27513 Property Occupant: Unknown Contractor/Land Specialist: Cohesion, Inc. 5216 Yates Mill Pond Road Raleigh, NC 27601 Engineer/Geologist: John (Jack) Sherrill, LG 1459 3326 Ruby Rd Durham, NC 27707 Analytical: QED – UVF Hydrocarbon Analyzer Geo Support, Inc. 919-345-9920 RELEASE INFORMATION Date Discovered: 02/16/2023 Est. Quantity of Release: unknown Cause of Release: unknown Source of Release: Heating oil UST Size / Content of UST System(s): 1,061 gallons, heating oil SITE HISTORY AND CHARACTERIZATION The property is located in a commercial area in downtown Sanford, NC (Figure 1). Lee County records indicate the building was constructed in 1955. The building was constructed for use as funeral services. The building is currently under renovation to be used for office space. INITIAL RESPONSE AND ABATEMENT ACTIVITIES Quantity of Regulated Substance Removed from USTs On February 9, 2023, Red Star Oil Company removed 204 gallons of residual fluid. The fluid disposal receipt is attached in Appendix A. 5 Source Control Actions The tank was removed on February 16, 2023. The tank disposal manifest is attached in Appendix B. Contaminant Migration Control Measures The tank was removed in accordance with industry accepted standards. Measures taken to Mitigate Fire/Safety Hazards The tank was removed in accordance with industry accepted standards. Contaminated Soil Storage, Treatment and/or Disposal No impacted soil was removed. Status of Free Product Investigation and Associated Removal No free product was encountered in the soil. SOURCE INVESTIGATION On February 8, 2023, field activities were initiated by removing the concrete floor covering the underground storage tank (UST). On February 9, 2023, Cohesion met with the fluid removal contractor at the tank site. Residual fluid was removed from the tank. The interior of the tank was cleaned, and rinse-water was removed. A total of 204 gallons of fluid were removed and transported for offsite disposal. The fluid disposal manifest is attached in Appendix A. On February 16, 2023 the tank was removed, loaded and transported off site for proper disposal. The tank disposal manifest is attached in Appendix B. After the tank was removed, soil samples B-1 and B-2 were collected on opposite ends from the bottom of the pit (approximately six feet below land surface). A strong petroleum odor was observed in the soil samples. The samples were analyzed for total petroleum hydrocarbons (TPH) using a QED analyzer. Analysis of sample B-1 detected a TPH diesel range organics (DRO) concentration of 35,624 mg/kg and TPH gasoline range organics (GRO) concentration of 3,990 mg/kg. Sample B-2 analysis detected a TPH-DRO concentration of 33,633 mg/kg and TPH-GRO concentration of 2,861 mg/kg. The detected TPH concentrations of both samples exceeds the North Carolina Department of Environmental Quality’s (NCDEQ’s) TPH cleanup limits for TPH-DRO of 100 mg/kg and TPH-GRO of 50 mg/kg. In an attempt to determine the depth of the release, four soil samples (S1-A, S1-B, S1-C and S1-D) were collected from a single boring starting at the bottom of the pit. S1-A was collected from a depth of eight (8) feet below land surface (bls), S1-B from ten (10) feet bls, S1-C from 12 feet bls and S1-D at 13.5 feet bls. Another soil sample (SW-1) was collected from the sidewall to determine the lateral extent in that direction. Sample locations are indicated in Figure 4. TPH analysis detected concentrations in all the boring samples exceeding NCDEQ’s TPH cleanup limits for TPH-DRO of 100 mg/kg and TPH-GRO of 50 mg/kg. The analytical 6 results are summarized on Table 1, and the analytical reports are included in Appendix C. No impacted soil was removed for off-site disposal. While a receptor survey was not conducted, it is believed no water supply wells are present within 150 feet of the source area. A Notice of Residual Petroleum (NRP) will be required by NCDEQ; unless all petroleum impacted soil exceeding NCDEQ applicable standards is removed. 7 TABLE 8 9 FIGURES 10 11 12 13 14 APPENDIX A - FLUID DISPOSAL MANIFEST 15 16 APPENDIX B - TANK DISPOSAL MANIFEST 17 18 APPENDIX C - QED SOIL ANALYSIS 19 20