CLU-IN Home

U.S. EPA Contaminated Site Cleanup Information (CLU-IN)


This content is being minimally managed and was last updated in July 2021. EPA recognizes that this content is relevant to site remediation stakeholders and will continue streamlined review and maintenance of this content.
U.S. Environmental Protection Agency
U.S. EPA Technology Innovation and Field Services Division

State Coalition for Remediation of Drycleaners Site Profiles

Parisian Cleaners, Orlando, Florida

Description
Historical activity that resulted in contamination.

Active drycleaning facility since 1954. Commercial property. Used petroleum-operated drycleaning machine. No information regarding historic waste generation, management practices, or haulers before 1994.

Contaminants
Contaminants present and the highest amount detected in both soil and groundwater.


Contaminant Media Concentration (ppb) Nondetect
Tetrachloroethene (PCE) groundwater 320 ppb
Tetrachloroethene (PCE) soil 130 ppb
1,2,4-trimethylbenzene groundwater 365 ppb
1,2,4-trimethylbenzene soil 410 ppb
1,3,5-trimethylbenzene groundwater 120 ppb
naphthalene soil 570 ppb
Trichloroethene (TCE) groundwater 4.4 ppb
xylenes soil 188 ppb

Site Hydrology

Deepest Significant Groundwater Contamination:   68ft bgs
Plume Size:  
Average Depth to Groundwater:   12.5ft

Lithology and Subsurface Geology

 
  Tan to white, very fine-grained sands
Depth: 0-34ft bgs
34ft thick
Gradient: 0.0035ft/ft
 
  Inter-bedded layers of gray to dark gray silts and clays
Depth: 34-62ft bgs
28ft thick

Pathways and DNAPL Presence

checkGroundwater
Sediments
checkSoil
DNAPL Present

Remediation Scenario

Cleanup Goals:
  PCE--GW = 3 µg/L; Soil = .03 mg/kg(leachability);
TCE-- GW = 3 µg/L; Soil = .03 mg/kg(leachability);
Napthalene-- GW = 20 µg/L; Soil = 1.7mg/kg (leachability);
1,2,4 TMB-- GW = 10 µg/L; Soil = .3mg/kg (leachability);
1,3,5 TMB-- GW = 10 µg/L; Soil = .3mg/kg (leachability)

Technologies

In Situ Soil Vapor Extraction
 

Why the technology was selected:
Significant PCE soil contamination amendable to SVE technology.

Date implemented:
Start-up began-July 9, 2002 Construction begain in February 2002

Final remediation design:
Two vertical SVE wells. One was placed inside building; the other well placed next to building.

Results to date:
No Futher Action (NFA) for both soils and groundwater. Site Rehabilitation Completion Order(SRCO)issued on 4/27/04.

Cost to Design and Implement:
$72,458

Costs

Cost for Assessment:
  $92,120.30
Cost for Operation and Maintenance:
  $29,264 = O&M $8,689 = Monitoring
Total Costs for Cleanup:
  $202,531

Lessons Learned

1. Good soil sampling under the building providing good design of SVE system.

Contacts

Aaron Cohen
Florida Dept. of Environmental Protection
Bureau of Waste Cleanup, MS 4500
2600 Blair Stone Road
Tallahassee, Florida 32399
850-245-8974
Aaron.Cohen@dep.state.fl.us

 

Top of Page