Site Number: |
A872 |
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Contract Number: |
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D.O. Number: |
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Action Memo Date: |
7/24/2015 |
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: |
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Mobilization Date: |
5/9/2016 |
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Start Date: |
5/10/2016 |
Demob Date: |
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Completion Date: |
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CERCLIS ID: |
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RCRIS ID: |
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ERNS No.: |
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State Notification: |
State referral |
FPN#: |
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Reimbursable Account #: |
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1.1.1 Incident Category
Time-Critical Removal Action
1.1.2 Site Description
The Site is an operating wood treatment
facility and sawmill; however, the proposed scope of this removal action is
focused on portions of the property that contain unused and essentially
abandoned wood treatment structures. Current treatment processes utilize copper
naphthenate and fuel oil, a process not a regulated by RCRA. The current
treatment process is done in areas that have not been utilized for
the PCP-diesel fuel oil process used at the Site. This time-critical removal action
is the first federal removal action on the Site.
1.1.2.1 Location
The Site is located at 91 Hwy 31, Manderson, Wyoming, at: Latitude 44.2839069 / Longitude -107.9603291. The property surrounding the Site is primarily agricultural land. The Site sits on a bluff above the Bighorn River.
1.1.2.2 Description of Threat
EPA has considered all the factors described in 40 CFR §300.415(b)(2) of the NCP and determined that the following factors apply at the Site:
Documented levels of PCP in the surface and subsurface soils exceed Wyoming’s promulgated groundwater protection standards. There is no data available to positively conclude that the shallow groundwater on the Site is completely isolated from the groundwater plane associated with the Bighorn River or from the drinking water aquifer utilized by the residents immediately to the south of the Site. Additionally, as noted in Attachment 3 and the START 4 report, the contaminated layers identified in soil boring numbers 3 and 4, at 24 and 29/38 feet below ground surface respectively, indicate a significant downward migration of PCP in less than a tenth of a mile of horizontal distance. If the EPA does not take a response action, all available data indicate potential contamination of deeper aquifer(s) used for drinking water by nearby residents. A summary table of notable PCP detections is provided as Attachment 3, with a more detailed narrative explaining the results available in the START 3 and START 4 reports in the administrative record for the Site.
“(vii) The availability of other appropriate federal or state response mechanisms to respond to the release”
As discussed in the Site action memorandum, there are no other federal or state mechanisms available to respond to this release.
1.1.3 Preliminary Removal Assessment/Removal Site Inspection Results
The Wyoming Department of Environmental
Quality (WDEQ) Hazardous Waste Division discovered suspected contamination at
the Site during a routine inspection in 2011. Due to health issues of the
current owner, subsequent inspections and other enforcement activities were
delayed. The inspector notified the OSC of the suspected contamination in the
spring of 2013, at which point the On-Scene Coordinator (OSC) started a removal
site evaluation.
The Site started operations in the 1920s as a
small natural gas refinery, reportedly drying the gas by removing natural gas
liquids and removing sulfur bearing compounds. Very little information is
available at this time as to facility construction or gas throughput. In the 1950s,
the facility was purchased by a wood treating company, which started treating
posts using a pentachlorophenol (PCP)/diesel fuel mixture. This practice
continued through the 1990s, and there is an extensive Resource Conservation
and Recovery Act (RCRA) file on the facility.
Investigation by the START contractor yielded
surface and subsurface PCP contamination and revealed that the contamination
had impacted a shallow groundwater formation. The initial investigation effort
was centered on the primary drip pad, where trenches were excavated to allow
visual and olfactory assessment and subsequent sampling of suspect soils. The
initial sampling event indicated that contamination extended below the depth
accessible by the excavator – a depth of 14 feet below ground
surface. Details of this sampling event are available in the START 3 Sampling
Activities Report in the administrative record for the Site.
A second event was conducted to assess contamination
at depth in order to attempt to quantify the depth of contamination in areas
where the previous assessment was unable to do so. This effort identified a
thin contaminated strata approximately 30 feet below ground surface, indicating
significant downward migration. Details of this sampling event are available in
the START 4 Trip Report in the administrative record for the Site.
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