U.S. ENVIRONMENTAL PROTECTION AGENCY
POLLUTION/SITUATION REPORT
McDermitt and Cordero Mercury Mine Sites - Removal Polrep

UNITED STATES ENVIRONMENTAL PROTECTION AGENCY
Region IX
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Subject:
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POLREP #2
POLREP 02 - Work Continues
McDermitt and Cordero Mercury Mine Sites
NVN000909006
McDermitt, NV
Latitude: 41.9135613 Longitude: -117.7081702
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To:
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Harry Allen, EPA Region 9
Daniel Meer, EPA Region 9
Enrique Manzanilla, EPA
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From:
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Tom Dunkelman, OSC
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Date:
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5/1/2013
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Reporting Period:
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4/19-27/2013
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1. Introduction
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1.1 Background
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Site Number: |
NVN000909006 |
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Contract Number: |
EP-S9-12-01 |
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D.O. Number: |
9027 |
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Action Memo Date: |
10/16/2012 |
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Response Authority: |
CERCLA |
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Response Type: |
Time-Critical |
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Response Lead: |
EPA |
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Incident Category: |
Removal Action |
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NPL Status: |
Non NPL |
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Operable Unit: |
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Mobilization Date: |
4/15/2013 |
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Start Date: |
4/15/2013 |
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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: |
Yes |
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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 McDermitt and Cordero Mercury Mine sites consist of several non-contiguous locations: the McDermitt Mine, the Cordero Mine, areas within the town of McDermitt where apparent mine waste has been used as fill, and areas of the Fort McDermitt Pauite Shoshone Reservation (the Reservation) where apparent mine waste has also been used as fill. The Cordero Mine operated from the 1930s until 1970, and is located on land managed by the BLM and on private land. The adjacent McDermitt Mine was operated from 1973 until the late 1980s. The McDermitt Mine is located on private land. The McDermitt Mine was closed under a permit from the Nevada Division of Environmental Protection (NDEP), and a final closure report was submitted in December, 1994.
The EPA Site Assessment program conducted a Site Inspection in 1988 which recommended no further action. Upon request from the Fort McDermitt Pauite Shoshone Tribe, EPA Emergency Response conducted an additional site visit in November 2009. At that time, EPA was notified of the possibility that mine waste had been used as fill at locations within the town of McDermitt and on the Fort McDermitt Paiute Shoshone Reservation.
In September and October of 2010, EPA conducted sampling of areas of red-colored fill located in the town of McDermitt and on the Reservation. The town of McDermitt straddles the Nevada/Oregon border and numerous areas were identified which contained mercury and arsenic in soil at concentrations which exceeded the EPA Region 9 residential Soil Remediation Goals (SRGs). Two areas were identified on the Reservation which contained mercury and arsenic in soil at concentrations which exceeded the residential SRGs.
In June 2011, EPA conducted additional sampling of the mine waste present at the mine site and present in the town and on the Reservation. The goal of this sampling effort was to evaluate the bioavailability and mineral speciation of the mercury and arsenic. The USGS provided technical and analytical support to EPA in this effort.
On October 16, 2012, EPA signed an Action Memorandum describing removal activities to be performed. EPA also issued a Unilateral Order to both Sunoco and Barrick Gold requiring these companies to participate in the cleanup process. To date, both companies have declined to participate in work under these Orders.
1.1.2.1 Location
The town of McDrmitt is located roughly 70 miles north of Winnemucca, NV, along Highway 95. The town straddles the Nevada/Oregon state line. The Fort McDermitt Pauite Shoshone Indian Reservation is located 3.5 southeast of the town of McDermitt and the McDermitt and Cordero Mines are located 7.2 miles southwest of the town of McDermitt.
1.1.2.2 Description of Threat
Mercury and arsenic are present in calcine material located on school property and on residential property in excess of site specific cleanup standards of 60 mg/kg arsenic and 80 mg/kg mercury.
1.1.3 Preliminary Removal Assessment/Removal Site Inspection Results
Removal assessment results are presented in Removal Assessment reports produced by the START contractor. These reports are available on the epaosc web page. The removal assessment documented the presence of mercury and arsenic at levels in excess of the site specific cleanup levels at approximately 40 residential properties.
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2. Current Activities
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2.1 Operations Section
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2.1.1 Narrative
2.1.2 Response Actions to Date
During this reporting period, the following actions were completed.
Borrow Pit. Continue to screen and crush rock and transport this material to town for use as backfill. To date, approximately 8,000 tons of backfill have been produced.
School Parking Lot and area on east side of football field. ERRS crews neared completion of work in these areas. Calcine material from the area on the east side of the football field was excavated and clean cover was placed. Clean cover was placed over the large parking lot west of the football field.
Residential Properties. Work (excvation of calcines, transport of calcines to repository and placement of clean cover) was completed at the following residential properties:
480 South Road and 620 South Road (Fort McDermitt Paiute Shoshone Indian Reservation), 520 Lasa Drive.
2.1.3 Enforcement Activities, Identity of Potentially Responsible Parties (PRPs)
EPA has identified two PRPs for this Site - Sunco and Barrick Gold. EPA issued a Unilateral Order to both companies requiring that they perform cleanup activities at the site. Both companies declined to perform work under the Unilateral Order.
2.1.4 Progress Metrics
Number of acres remediated this reporting period: 1.3
Total number of acres remediated to date: 1.3
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2.2 Planning Section
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2.2.1 Anticipated Activities
2.2.1.1 Planned Response Activities
Produce crushed rock at borrow source and transport to town;
Prepare school parking lot for capping;
Place cap material at school parking lot and at other select locations;
Remove calcine material from residential properties;
Transport excavated calcine material to borrow source;
Place backfill material at excavated areas;
Transport calcine material to repository;
Demobilize from site.
2.2.1.2 Next Steps
Continue to produce crushed rock and transport to town.
Continue remediation of residential properties.
2.2.2 Issues
BLM signed an Action Memo authorizing transport of calcine material to the Cordero calcines pile.
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2.3 Logistics Section
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No information available at this time.
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2.4 Finance Section
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Budgeted |
Total To Date |
Remaining |
% Remaining |
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Extramural Costs
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| ERRS - Cleanup Contractor |
$1,200,000.00 |
$725,000.00 |
$475,000.00 |
39.58% |
| TAT/START |
$150,000.00 |
$55,000.00 |
$95,000.00 |
63.33% |
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Intramural Costs
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| USEPA - Direct |
$50,000.00 |
$16,588.00 |
$33,412.00 |
66.82% |
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| Total Site Costs |
$1,400,000.00 |
$796,588.00 |
$603,412.00 |
43.10% |
* The above accounting of expenditures is an estimate based on figures known to the OSC at the time this report was written. The OSC does not necessarily receive specific figures on final payments made to any contractor(s). Other financial data which the OSC must rely upon may not be entirely up-to-date. The cost accounting provided in this report does not necessarily represent an exact monetary figure which the government may include in any claim for cost recovery.
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2.5 Other Command Staff
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No information available at this time.
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3. Participating Entities
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No information available at this time.
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4. Personnel On Site
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No information available at this time.
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5. Definition of Terms
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No information available at this time.
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6. Additional sources of information
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No information available at this time.
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7. Situational Reference Materials
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No information available at this time.
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POLREP #2 Last Updated 5/4/2013
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