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Profile Information

Former Car Dealership
Government
256956
320 Walnut Street, 15480 and 15522 Rankin Avenue DUNLAP, TN 37327
2.41
048E H 007.00, 048E H 006.02, 048E H 006.01
35.369890981992 / -85.390757036112
4
Perry, Olga
Perry.Olga@epa.gov
404-562-8534


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Property Location



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Property Progress


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CAs Associated with this Property

CA NameCA #StateTypeAnnouncement Year
City of DunlapBF02D06521TNAssessment2021


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Assessment Activities at this Property

ActivityEPA FundingStart DateCompletion DateCAAccomplishment Counted?Counted When?
Cleanup Planning$14,540.0010/27/202311/02/2023City of DunlapN
Phase I Environmental Assessment11/11/202112/02/2021City of DunlapN
Phase II Environmental Assessment$44,785.0009/12/202210/31/2022City of DunlapYFY24
Supplemental Assessment$3,500.0009/12/202210/31/2022City of DunlapN


Is Cleanup Necessary? Yes
EPA Assessment Funding: $62,825.00
Leveraged Funding: $3,000.00
Total Funding: $65,825.00


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Climate Adaption and Mitigation - Planning or Assessment

Selected Strategy(ies)Explanatory Text
Adoption of building codes that consider impacts from extreme weather events and natural disastersBuilding codes can encourage implementation of mitigation and adaptation techniques for extreme weather events and natural disasters. Codes may require that infrastructure be planned and built to avoid or minimize future damage or costly repairs from increased frequency and intensity of flooding, drought, wildfires, and other projected extreme weather/disaster events. Codes may also lead to energy savings for commercial and residential buildings by specifying minimum requirements for building components such as insulation, water use, heating and cooling systems, lighting, windows, and ventilation systems. Effective building code requirements may vary regionally due to differences in natural hazards.


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Contaminants and Media


Asbestos
Lead
VOCs
NOT Cleaned up
NOT Cleaned up
NOT Cleaned up
Building Materials
Ground Water
NOT Cleaned up
NOT Cleaned up

Cleanup Activities

There are no current cleanup activities.


Cleanup/Treatment Implemented: N
Cleanup/Treatement Categories:
Addl Cleanup/Treatment info: The scope of work for the additional VI assessment consisted of the installation of six permanent sub-slab active soil gas sampling points (PSS-6 through PSS-11) to delineate the extent of soil gas impact identified at SS-1. The sub-slab soil gas samples were analyzed for VOCs by TO-15 Volatile Organics in Air Method. The sub-slab soil gas samples collected at the subject property indicate that target analytes are present beneath the building at concentrations exceeding the VISLs for Residential Receptors. Based on the TDEC VI Guidance, the results of the VI risk evaluation indicate that risk thresholds for a Residential scenario are exceeded and represent an unacceptable exposure risk to future building occupants. At a minimum, passive VI mitigation will be required for this property under the TDEC Voluntary Cleanup Oversight and Assistance Program (VOAP). Additionally, it is noted that the proposed future use of the subject building is as a fire hall. Although workers would be present at the fire hall overnight, the default residential exposure scenario utilized in the EPA VISL Calculator (24 hours/day, 350 days/year, 26 years) is unlikely based on the proposed future use. As such, commercial worker exposure factors in the EPA VISL Calculator were adjusted to reflect an exposure scenario between that of a resident and typical commercial worker (8 hours/day, 250 days/year, 25 years). Based on this modified commercial exposure scenario, the calculated cumulative carcinogenic risk value for the site was still more than twice the mitigation threshold presented in the TDEC VI Guidance. Based on the results of the soil, groundwater, and soil gas sampling, the source area appears to be localized beneath the main on-site building slab. Source removal is not practical given the reuse plans for the Subject Property, and mitigation that addresses potentially complete exposure pathways is appropriate. It is PM's professional opinion that vapor mitigation should be incorporated into future redevelopment plans in accordance with the TDEC VI Guidance. Asbestos Containing Materials Due to the combination of issues requiring cleanup action, the recommended cleanup option is Alternative #2: Abatement and Disposal. Alternative #1: "No Action" does not address the site risks. Without cleanup or removal of the asbestos the subject property will always contain asbestos containing materials inhibiting redevelopment of the site. The long-term solution of removal and proper disposal of ACM from the subject property is the only alternative that allows the property owner to move forward with the proposed redevelopment of the property. Vapor Intrusion Due to the combination of issues requiring cleanup action, the recommended cleanup option is Alternative #3: Passive Vapor Intrusion Mitigation System. Alternative #1: "No Action" does not address the site risks. Without mitigation of sub-slab vapor, the subject property will pose as a vapor intrusion concern for future occupants which will inhibit redevelopment of the site. Alternative #2: Active Sub-Slab Depressurization System would effectively mitigate sub-slab vapor, but continuing obligations, operation, and maintenance of an active system will result in significant long-term costs and presents long-term effectiveness concerns related to system failure. The long-term solution of installing a passive VIMS on the subject property is the best alternative that allows the property owner to move forward with the cleanup and redevelopment of the property, as proposed.
Address of Data Source:
Total ACRES Cleaned Up: 2.41
Number of Cleanup Jobs Leveraged:
EPA Cleanup Funding:
Leveraged Funding:
Cost Share Funding:
Total Funding:


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Climate Adaption and Mitigation - Demolition or Cleanup

Selected Strategy(ies)Explanatory Text
Selection and design of cleanup considered the site's vulnerabilities to extreme weather events and natural disastersVulnerability describes the degree to which natural, built, and human systems are at risk of exposure to impacts from extreme weather events and natural disasters.
Design of cleanup allowed for siting of weather-related and disaster-related resiliency measures in site reuseThe capacity of a system to maintain function in the face of stresses imposed by extreme weather events and natural disasters and to adapt the system to be better prepared for future related impacts.


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Institutional and Engineering Controls

No
Yes
Other SSD system is in place
No


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Redevelopment and Other Leveraged Accomplishments

There are no current redevelopment activities.


Number of Redevelopment Jobs Leveraged:
Actual Acreage of Greenspace Created:
Leveraged Funding:


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Climate Adaption and Mitigation - Redevelopment

Selected Strategy(ies)Explanatory Text
N/AThis property does not incorporate redevelopment activities to address impacts from extreme weather events and natural disasters. If no activities were incorporated, select this option.


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Additional Property Attributes

PM completed a geophysical survey at the subject property to investigate the presence of potential orphan underground storage tanks (USTs) associated with the unidentified piping protruding from the surface along the southern perimeter of the former automotive service center observed during the December 2021 Phase I ESA and clear the boring location of subsurface utilities. No anomalies consistent with the presence of an orphaned UST(s) were identified during the completion of the geophysical survey investigation.

No concentrations of VOCs and PAHs were identified in the groundwater samples analyzed from the subject property above the laboratory MDLs and/or applicable criteria. However, lead was detected in one groundwater sample (TMW-6 at 31.5 micrograms per liter [�/L]) above the corresponding EPA Primary Drinking Water Maximum Contaminant Level (MCL) of 15 �/L. Although the MCL for lead was exceeded in TMW-6, the subject property is connected to municipal water and no water supply wells exist on the property; therefore, the exposure pathway for groundwater ingestion is incomplete.

PM completed a soil gas survey to evaluate the vapor intrusion (VI) risk at the site. The soil gas survey consisted of the installation of five temporary sub-slab soil gas monitoring points (SS-1 through SS-5), and the collection of soil gas samples for laboratory analysis of VOCs.

A preliminary evaluation of the soil gas survey results indicates that a vapor intrusion exposure risk may be present at the site. The predicted indoor air cancer risk and hazard index calculations were completed with the EPA Vapor Intrusion Screening Level (VISL) Calculator and used default exposure variables and a conservative default sub-slab to indoor air attenuation factor of 0.03. A review of the calculated risk indicates that the cumulative cancer risk at the site exceeds allowable risk levels presented in the TDEC VI Guidance primarily due to the concentration of benzene detected in the sample collected from SS-1.

An additional VI assessment was completed. The scope of work consisted of the installation of six permanent sub-slab active soil gas sampling points (PSS-6 through PSS-11) to delineate the extent of soil gas impact identified at SS-1. The sub-slab soil gas samples were analyzed for VOCs by TO-15 Volatile Organics in Air Method.

On August 16, 2023, PM completed assessment activities at the subject property that consisted of the installation of six permanent sub-slab soil gas sampling points (PSS-6 through PSS-11), and the collection of six soil gas samples for laboratory analysis of VOCs to delineate and further evaluate the potential for vapor intrusion identified in PM's October 2022 Phase II ESA.

The sub-slab soil gas samples collected at the subject property indicate that target analytes are present beneath the building at concentrations exceeding the VISLs for Residential Receptors.

Based on TDEC VOAP Guidance, the results of the VI risk evaluation indicate that mitigation risk value thresholds for Residential scenario are exceeded and represent an unacceptable exposure risk to future building occupants. VI mitigation (active or passive systems) would likely be required for this property under the TDEC VOAP.

Additionally, it is noted that the proposed future use of the subject building is as a fire hall. Although workers would be present at the fire hall overnight, the default residential exposure scenario utilized in the EPA VISL Calculator (24 hours/day, 350 days/year, 26 years) is unlikely based on the proposed future use. As such, commercial worker exposure factors in the EPA VISL Calculator were adjusted to reflect an exposure scenario between that of a resident and typical commercial worker (8 hours/day, 250 days/year, 25 years). Based on this modified commercial exposure scenario, the calculated cumulative carcinogenic risk value for the site was still more than twice the mitigation risk value threshold in the
Commercial (2.41)


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