State Coalition for Remediation of Drycleaners Site Profiles
Former Alpine Cleaners, Friendswood, Texas
Description
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Alpine Cleaners operated as a PCE drycleaner from 1989 to 1998. A sewer line break was reportedly one of the pathways for contaminant migration into the subsurface. Spills at the facility and discharges to a storm sewer were also identified as possible source areas. Remediation Status: In groundwater monitoring |
Contaminants
Contaminants present and the highest amount
detected in both soil and groundwater.
Contaminant | Media | Concentration (ppb) | Nondetect |
---|---|---|---|
Benzene | groundwater | ||
cis-1,2-Dichloroethene | groundwater | ||
1,1-Dichloroethene | groundwater | ||
Tetrachloroethene (PCE) | groundwater | ||
Trichloroethene (TCE) | groundwater | ||
trans-1,2-Dichloroethene | groundwater | ||
Vinyl Chloride | groundwater |
Site Hydrology
Deepest Significant Groundwater Contamination: | 16ft bgs | |
Plume Size: | Plume Length: 160ft Plume Width: 80ft |
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Average Depth to Groundwater: | 10ft |
Lithology and Subsurface Geology
silty clay Depth: 0-10ft bgs 10ft thick Conductivity: 0.283ft/day Gradient: 0.0055ft/ft |
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fine-grained clayey sand Depth: 10-15ft bgs 5ft thick |
Pathways and DNAPL Presence
Groundwater Sediments Soil Presumptive Evidence of DNAPL |
Vapor Intrusion Pathway
Has the potential for vapor intrusion (VI) been evaluated? |
No |
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Has a vapor mitigation system been installed? |
No | |
Additional VI Information: |
None as of present. |
Remediation Scenario
Cleanup
Goals: |
*Shallow Groundwater zone: PCE = 5 µg/l TCE = 5 µg/l cis 1,2-DCE = 70 µg/l vinyl chloride = 2 µg/l *2nd Groundwater zone: PCE = 500 µg/l TCE = 500 µg/l cis 1,2-DCE = 7,000 µg/l vinyl chloride = 200 µg/l |
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Remedy Level: |
Interim Action |
Technologies
In Situ Chemical Oxidation |
Why the technology was selected: Date implemented: Final remediation design: Results to date: Next Steps: |
Costs
Cost
for Assessment: |
Costs for the 1999-2001 Remediation is not available | |
Cost
for Operation and Maintenance: |
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Total
Costs for Cleanup: |
Lessons Learned
*Source area should be fully characterized before conducting remediation. *A review of data results from the October 1999 response action showed concentration reductions, with later site data showing a return of concentration levels. Based on soil types at the site (silty clay to silty sand), it appeared that the delivery system may not have been adequate to provide a sufficient radius of coverage. In addition, hydrogen peroxide based oxidants are fast acting oxidants, reducing the overall area of influence, that require a lower pH concentration, which is not typical of the site. Although a pH adjustor was included, the site pH is not generally compatible with the oxidant and the overall effectiveness may have been reduced. |
Contacts
Richard Scharlach Texas Commission on Environmental Quality (TCEQ) Voluntary Clean-up Program 12100 Park Circle, Bldg. D Austin, Texas 78753 ERM Southwest, Inc. Paul Stefan 15810 Park Ten Place, Suite 300 Houston, Texas 77084 Phone: 281-600-1000 |