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Site Number: |
A72Q |
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Contract Number: |
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D.O. Number: |
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Action Memo Date: |
5/15/2015 |
Response Authority: |
CERCLA |
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Response Type: |
Time-Critical |
Response Lead: |
EPA |
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Incident Category: |
Removal Action |
NPL Status: |
Non NPL |
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Operable Unit: |
00 |
Mobilization Date: |
5/26/2015 |
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Start Date: |
5/26/2015 |
Demob Date: |
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Completion Date: |
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CERCLIS ID: |
IAD039954300 |
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RCRIS ID: |
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ERNS No.: |
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State Notification: |
IDNR |
FPN#: |
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Reimbursable Account #: |
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1.1.1 Incident Category
CERCLA incident category: Inactive Production Facility
1.1.2 Site Description
1.1.2.1 Site Location
The Site is located at, and in the area of, 1205 East 7th Street, Atlantic, Cass County, Iowa. The approximate coordinates of the Site are latitude 41.403718° north and longitude 94.995763° west. The Site is a former dry cleaning facility, which has since been turned into a parking lot for an adjacent commercial building.
The City of Atlantic has a population of 7,008 (U.S. Census Bureau 2012) and is located in Cass County, Iowa, approximately 45 miles northeast of Council Bluffs and 75 miles west of Des Moines. Land use in the area of the Site is a mixture of commercial and residential. The City of Atlantic Municipal Utility well field is located adjacent to Troublesome Creek.
1.1.2.2 Description of Threat
Analytical results from samples collected by the U.S. Environmental Protection Agency indicate that hazardous substances have been released into the environment at the Site. Tetrachloroethene (PCE) and its degradation products are hazardous substances as defined in CERCLA section 101(14), 42 U.S.C. § 9601(14), and as designated in 40 CFR § 302.4. PCE and trichloroethene (TCE) have been detected in soil, groundwater, subslab, and indoor air samples at levels that exceed the EPA's removal action levels (RALs) and screening levels. Site screening and RALs for indoor air and subslab soil vapor can be found in the action memorandum, a copy of which is located in the document section.
Concentrations of PCE as high as 3,400,000 micrograms per kilogram (µg/kg) have been found in soil at the source area. Concentrations of PCE as high as 260 micrograms per liter (µg/L) have been found in groundwater at the Site. Subslab soil vapor concentrations of PCE detected at a nearby business were as high as 2,261 micrograms per cubic meter (µg/m3). Screening levels for subslab soil vapor for a business are 1,800 µg/m3. The owners of the business with subslab soil vapor concentrations above the screening level have voluntarily installed a vapor mitigation system.
Vapor intrusion occurs when vapors emanating from contaminated soil and/or groundwater migrate through the vadose zone into overlying structures and into the indoor air. When chemicals are spilled on the ground, they frequently seep into the soil and make their way into the groundwater. Volatile organic compounds (VOCs), including PCE and TCE, produce vapors that travel through soil. These vapors can enter buildings through cracks in the foundation, or a basement with a dirt floor or concrete slab or crawl space.
PCE is a man-made chemical that is widely used for dry cleaning clothes and for metal degreasing. It evaporates easily into the air and has a sharp, sweet odor. Exposure to PCE vapors at very high concentrations (particularly in closed, poorly ventilated areas) can cause dizziness, headaches, drowsiness, confusion, nausea, difficulty in speaking and walking, unconsciousness, and death. PCE has been shown to cause liver tumors in mice and kidney tumors in rats. It has been determined that PCE is a Class 2A carcinogen via inhalation based on long-term exposure.
TCE is defined as a hazardous substance in section 101(14) of CERCLA, and is designated as a hazardous substance in 40 C.F.R. § 302.4. The Agency for Toxic Substances and Disease Registry (ATSDR) reports that inhalation exposure to TCE at very high concentrations may affect the central nervous system, with symptoms such as dizziness, headaches, confusion, euphoria, facial numbness, and weakness. Recent studies have linked TCE with fetal structural heart malformations associated with exposure during the prenatal period.
1.1.3 Removal Preliminary Assessment/Removal Site Inspection Results
Concentrations of PCE-contaminated soil as high as 3,400,000 µg/kg have been found at the Site. The contamination in the soil has leached to the groundwater, and has impacted the City of Atlantic’s (City) well field located approximately 1 mile downgradient of the Site. The City’s municipal water supply well field, which supplies the City’s drinking water, has been impacted by PCE at concentrations exceeding the EPA maximum contaminant level (MCL) for PCE. Concentrations of PCE as high as 260 µg/L have been found in these municipal wells. Lesser concentrations of breakdown products such as trichloroethene (TCE) and 1,2-dichloroethene (DCE) have been reported sporadically in one or more wells. One of Atlantic Municipal Utilities (AMU) city water wells (AMU-7) has been disconnected from the system and is currently being pumped continually to the City public-owned treatment works (POTW) to provide hydraulic control and protect the nine other municipal wells from contamination. However, AMU-7 has deteriorated over time; the gravel pack is falling into the well, and the pump has had to be replaced twice. At this time, AMU-7 is no longer providing hydraulic control of the PCE contamination. AMU-6 is located downgradient of AMU-7 and is now showing PCE contamination as high as 17 µg/L. All the City’s well water is dumped into the clear well before it is distributed into the drinking water system. The clear well is sampled monthly for PCE and TCE contamination.
At the source, which was formerly occupied by a dry cleaners and an Iowa Department of Transportation (IDOT) materials testing laboratory, approximately 40 feet of silts and clays overlie the fine- to coarse-grained friable Dakota sandstone. The silt and clay soils at the source have been contaminated with PCE at depths too deep for physical removal or conventional remediation. Currently a parking lot and commercial building reside where the dry cleaning and material testing lab used to be. Based on data collected, it appears that PCE contamination at the source continues to vertically migrate down into the Dakota sandstone aquifer and travel horizontally to the City’s municipal well field. The EPA has collected indoor air and subslab samples in the businesses and homes adjacent to and nearby the source area, as well as downgradient of the source area. Subslab sample results were as high as 2,261 µg/m3. Indoor air sample results were found at concentrations of 76 µg/m3. The subslab sample results were above EPA screening levels at one business. The owner of the business has voluntarily installed a vapor mitigation system inside the business.
The groundwater flows north-northwest from the source area toward the municipal well field, and the plume of contamination follows the groundwater gradient.
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AMU Atlantic Municipal Utilities
ATSDR Agency for Toxic Substance Disease Registry
CFR code of federal registration
CERCLA Comprehensive Environmental Response, Compensation, and Liability Act of 1980
DCE dichloroethene
EC electric conductivity
EPA Environmental Protection Agency
ERRS Emergency and Rapid Response Services
ERT Environmental Response Team
fbgs feet below grade surface
HRS Hazard Ranking Score
IDNR Iowa Department of Natural Resources
IDOT Iowa Department of Transportation
MCL Maximum Contaminate Level
MIP membrane interface probe
MW monitoring well
NPL National Priorities List
OSC On Scene Coordinator
PCE Tetrachloroethene
PDB passive diffusion bags
PID photoionization detector
POTW Public Owned Treatment Works
ppm parts per million
PRB Permeable Reactive Barrier
PRP Potential Responsible Party
RAL removal action level
REAC Response Engineering and Analytical Contract
SB soil boring
START Superfund Technical Assessment & Response Team
TCE Trichloroethene
TOC total organic carbon
µg/L Micrograms per Liter
µg/kg micrograms per kilogram
µg/m3 micrograms per cubic meter
VOCs volatile organic compounds
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