State Coalition for Remediation of Drycleaners Site Profiles
Pro Cleaners #920001, Raleigh, North Carolina
Description
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A former "Perc" facility that operated until 1998 located in a tenant space of a single-story strip shopping center built slab on grade with multiple adjacent commercial tenants. No previous incidents were reported at the site prior to discovery date. Site was discovered in June 1995 by property owner during Phase II assessment for a property transaction. Probable source of contamination is unknown but is most likely related to historical daily operations and use in solvent storage, handling, and waste management practices prior to establishment of state release prevention regulations implemented in 1997. The targeted source area is the subsurface soils and groundwater immediately underneath the shopping center tenant spaces below and directly behind the dry cleaning facility and along the sanitary sewer system. Remediation Status: In active remediation |
Contaminants
Contaminants present and the highest amount
detected in both soil and groundwater.
Contaminant | Media | Concentration (ppb) | Nondetect |
---|---|---|---|
Benzene | groundwater | ||
chloroform | groundwater | ||
cis-1,2-Dichloroethene | groundwater | ||
1,2-Dichloroethane | groundwater | ||
methylene chloride | groundwater | ||
Tetrachloroethene (PCE) | groundwater | ||
Tetrachloroethene (PCE) | soil | ||
Trichloroethene (TCE) | groundwater | ||
Vinyl Chloride | groundwater |
Site Hydrology
Deepest Significant Groundwater Contamination: | 148ft bgs | |
Plume Size: | Plume Length: 780ft Plume Width: 280ft Plume Thickness: 148ft |
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Average Depth to Groundwater: | 32.51ft |
Lithology and Subsurface Geology
Silty sand Depth: 0-10ft bgs 10ft thick Conductivity: 1.89ft/day Gradient: 0.02ft/ft |
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partially weathered rock at a range Depth: 10-92ft bgs 82ft thick |
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Crabtree Creek gneiss Depth: 92ft bgs |
Pathways and DNAPL Presence
Groundwater Sediments Soil Presumptive Evidence of DNAPL |
Vapor Intrusion Pathway
Has the potential for vapor intrusion (VI) been evaluated? |
Yes |
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How was the site evaluated? |
Soil vapor and/or Sub-slab vapor sampling,Indoor air sampling,Groundwater sampling,Compared sample concentration to screening criteria,Used an exposure screening model |
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Results of VI evaluation: |
The VI pathway was ruled out (or does not exist) | |
Has a vapor mitigation system been installed? |
No | |
Additional VI Information: |
Previous interim actions were conducted beneath the tenant space to remove sub-slab soils when the tenant space was unoccuiped to mitigate the potential vapor intrusion pathway which was confirmed by post corrective action indoor air sampling. |
Remediation Scenario
Cleanup
Goals: |
To reduce contaminant concentrations so that the site risks do not exceed a cumulative cancer risk of 1E10-5 and a hazard index below 1.0 by reduction of groundwater plume size and concentrations to protect downgradient private water supply well users. |
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Remedy Level: |
Interim Action |
Technologies
In Situ Bioremediation |
Why the technology was selected: Date implemented: Final remediation design: Other technologies used: Results to date: Next Steps: Cost to Design and Implement: |
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In Situ Zero Valent Iron |
Why the technology was selected: Date implemented: Final remediation design: Other technologies used: Results to date: Next Steps: Cost to Design and Implement: |
Costs
Cost
for Assessment: |
$219,914.82 - Includes approved reimbursed assessment costs submitted by owner prior to entry into the Program. | |
Cost
for Operation and Maintenance: |
Not applicable. | |
Total
Costs for Cleanup: |
Not applicable. |
Lessons Learned
Injection was found to pose a significant challenge at this site due to the complex site hydrogeology and groundwater chemistry. Furthermore, the injection technology used was selected based on low price and perhaps was not as effective as other available technologies. A lab bench-scale test may have assited with identifying the limitations of using the selected technology and possibly identification of other better technologies available. |
Contacts
Al Chapman, L.G. Project Manager NCDENR - Division of Waste Managment DSCA Program 1646 Mail Service Center Raleigh, NC 27699-1646 Phone: (919) 707-8368 Fax: (919) 707-8368 Email: Al.Chapman@ncdenr.gov Website: www.ncdsca.org |
Site Specific References
The site reports are available on the NCDENR document portal system located at https://edm.nc.gov/DENR-Portal/ |