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Profile Information

Private
209282
1832 Kimball Rd. SE CANTON, OH 44707
1.08
246763
40.778367 / -81.382351
13
Auker, Karla
auker.karla@epa.gov
440-250-1741


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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
Stark County Regional Planning CommissionBF00E01377OHAssessment2014


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Assessment Activities at this Property

ActivityEPA FundingStart DateCompletion DateCAAccomplishment Counted?Counted When?
Phase II Environmental Assessment$14,969.0001/19/201603/02/2016Stark County Regional Planning CommissionYFY16


Is Cleanup Necessary? No
EPA Assessment Funding: $14,969.00
Leveraged Funding:
Total Funding: $14,969.00


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Climate Adaption and Mitigation - Planning or Assessment

There is no data for Climate Adaption and Mitigation - Planning or Assessment.


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Contaminants and Media


Chromium (Cr)
Lead
Other Contaminants
Other Metals
PAHS
Petroleum Products
VOCs
NOT Cleaned up
NOT Cleaned up
NOT Cleaned up
NOT Cleaned up
NOT Cleaned up
NOT Cleaned up
NOT Cleaned up
Unknown

Cleanup Activities

There are no current cleanup activities.


Cleanup/Treatment Implemented:
Cleanup/Treatement Categories:
Addl Cleanup/Treatment info:
Address of Data Source:
Total ACRES Cleaned Up: 1.08
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

There is no data for Climate Adaption and Mitigation - Demolition or Cleanup.


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Institutional and Engineering Controls

No
No
No
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

There is no data for Climate Adaption and Mitigation – Redevelopment


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Additional Property Attributes

Based on the analytical results obtained, it does not appear that soil or ground water in close proximity to the RECs determined on the subject Property have been significantly impacted by former site activities or former and current off-Property operations. Benzo(a)pyrene was detected at one surface soil location slightly above its applicable DCSS; however, the concentration of benzo(a)pyrene identified above DCSS does not appear to be indicative of widespread or significant contamination. Benzo(a)pyrene at the level found is typical in surface soils (i.e., 0-2 feet) at properties historically used for commercial/industrial purposes. Benzo(a)pyrene characteristically originates from heavy-ended petroleum, and, at this Property, likely sources would be cinders, asphalt, or swept industrial debris deposited in this area of the site. For example, a small piece of asphalt mixed in with the soil sample analyzed could easily be the cause of the benzo(a)pyrene concentration found at the site. Analyses of chromium in soil yielded total chromium analytical results, which did not distinguish between the different speciations of chromium (i.e., hexavalent vs. trivalent chromium). The VAP provides generic DCSS for hexavalent and trivalent chromium, but does not consider a standard for total chromium. Therefore, total chromium results obtained were compared against the more conservative hexavalent chromium DCSS. Total chromium results evaluated against the hexavalent chromium standard determined that near surface soil at one location (B-7) potentially exceeds hexavalent chromium DCSS for C/I workers. Hexavalent chromium is typically used for industrial purposes in textile dyes, wood preservation, and added as an anti-corrosive agent to metals (e.g.,electroplating) and other surface coatings. Trivalent chromium is much more prevalent at commercial/industrial sites and is the more likely source of the total chromium concentrations encountered. Additional soil analyses can be performed at the affected sampling location to determine the specific speciation of chromium if further characterization is desired. None of the soil or ground water concentrations detected indicate a vapor intrusion risk to the existing building or any future planned structures.

Former Use: Based on information provided in the recent Phase I ESA, the subject site consists of approximately an acre of commercially developed land located in a predominantly commercial area, with areas of residential land use south of the Property along Kimball Road. According to the previous Phase I ESA (2015), the subject Property was agricultural land prior to 1950 and was then utilized as a portion of the Stark Auto Wrecking Company. Automobile wrecking, salvage, and storage occurred on the Property through approximately 1976. Subsequent to auto salvage operations, the Property was occupied by a concrete contractor, a bus garage, and, most recently, a commercial sweeping company. It is reported that sweeping debris/waste from commercial parking lots, industrial facilities, and municipal streets has been deposited on the eastern portion of the Property (REC-1).
Industry (1.08)
Hazardous


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