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The Luckey site is located at 21200 Luckey Road in Luckey, Ohio,
approximately 35 kilometers (22 miles) southwest of Toledo. Structures at
the site include large production, warehouse, and related buildings;
transportation systems; and utility buildings. Several active and inactive
lagoons and spoil areas are also present. Numerous open areas are vegetated,
mostly with grasses and brush. The site encompasses approximately 16 hectares
(40 acres).
LOCALITY MAP
Estimated Site Total
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(Thousands of Current Year Dollars)
|
| |
|
|
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| Environmental Restoration
|
112
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2,288
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9,662
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11,765
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10,832
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Grey shaded area reflects annual cost
estimates for the first five years of the site BEMR Base Case (as of October
1995) and includes 3% annual inflation, see Readers' Guide.
|
| 1996 Appropriation
|
682 |
|
|
These levels reflect the current estimates for
compliance with applicable statutes and agreements (as of March 1996), see
Readers' Guide.
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| 1997 Congressional Request
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3,858
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|
|
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
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| |
2015
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2020
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2025
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2030
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| Environmental Restoration
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6,366
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6,046
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123 |
|
|
|
|
62,677
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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FACILITY MISSION
Chemical and low-level radioactive contamination at the Luckey site consists of
beryllium ore and production residues and traces of uranium. The estimated
total waste volume is 26,400 cubic meters (34,500 cubic yards). The plants
of the Magnesium Reduction Corporation, the Diamond Magnesium Company, and the
Brush Beryllium Company formerly occupied the site. Contamination originated
from beryllium and uranium processing operations conducted by Brush Beryllium
under contract to the Atomic Energy Commission from 1942 to 1959.
SITE MAP
According to estimates, the plant produced between 18,000 and 65,000 kilograms
(40,000 and 144,000 pounds) of beryllium. Waste solutions and precipitated
sludges from beryllium processing were impounded in three lagoons, formed by
excavating the top layer of soil and using the soil to construct dikes. The
Diamond Magnesium Company used the site to process magnesium and received
approximately 900 metric tons (1,000 tons) of scrap steel contaminated
with fission products. After the plant closed in 1959, hazardous sludge and
contaminated soils from the lagoons were moved to a 3.4-hectare (8.5acre)
dike-enclosed landfill that was later capped, graded, and seeded. The facility
changed ownership several times before it was transferred to the present owner,
Urekch International Corporation. The site was designated for cleanup under
FUSRAP in 1992.
The primary contaminants at the site (uranium, radium, and beryllium) have been
detected in site soils at concentrations exceeding current background levels
for the area. Current building and land use at the Luckey site presents no
immediate shortterm risk to site workers and the general public. The area
surrounding the site consists of open farmland, and quarries are located south
of the site. If future site use requires workers or members of the public to be
present in contaminated areas for extended periods, the risk to these receptors
could increase. Potential exposure pathways include inhalation and ingestion.
The northern part of the property is currently leased for farming; extensive
disturbance of the surface and subsurface soils for agricultural or industrial
purposes could result in offsite migration of contaminants and could pose a
risk to workers and the general public. However, the property owners currently
have no plans to disturb the site other than to demolish a production building
that was previously found to be uncontaminated.
FUTURE USE
After remediation, the site will be released for unrestricted use. This report
assumes that use of the property will be Industrial.
ENVIRONMENTAL RESTORATION
Environmental restoration of the Luckey site will include disposition of
approximately 26,400 cubic meters (34,500 cubic yards) of contaminated
residues. The baseline assumes that cleanup will be conducted under the
Comprehensive Environmental Response, Compensation and Liability Act protocol
for remediation of low-level radioactive contamination at FUSRAP sites and the
Atomic Energy Act of 1954, as amended. The environmental regulatory process
will focus on compliance with the Comprehensive Environmental Response,
Compensation, and Liability Act, and its implementing regulations. As required
by the Comprehensive Environmental Response, Compensation, and Liability Act,
the applicable or relevant and appropriate requirements of federal and state
laws are incorporated in the development of remediation goals for the site.
Key regulators are Environmental Protection Agency Region V, the Ohio
Environmental Protection Agency, and local governments, as appropriate. Other
regulatory drivers may include the Clean Air Act, the Safe Drinking Water Act,
and the National Pollutant Discharge Elimination System. Environmental
documentation integrating Comprehensive Environmental Response, Compensation,
and Liability Act and National Environmental Policy Act requirements is
expected to include a Remedial Investigation/Feasibility Study-Environmental
Impact Statement. The schedule for final cleanup depends on the issuance of a
Record of Decision and funding.
Major Environmental Restoration Activity Milestones
| TASK
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COMPLETION DATE
Fiscal Year
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| Assessment (Record of Decision)
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1999
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|
Remedial Action
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2006
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|
Transfer Site to Grand Junction Projects Office Long-Term Surveillance and
Monitoring Program
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2007
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ASSESSMENT
Field investigations at the Luckey site have included radiological surveys and
sampling by the Department of Energy, the Ohio Environmental Protection Agency,
and the Ohio Department of Health. All previous investigations identified
onsite contamination. Preliminary radiological characterization in 1988
included a walkover surface gamma scan over a large portion of the property
outdoors and sampling and analysis of water and surface and subsurface soil.
The results indicated that site soils contain radium226 and
uranium238, as well as high concentrations of beryllium. Because waste
solutions and precipitated sludges from beryllium processing operations were
impounded in the lagoons on the southern side of the plant, high concentrations
of beryllium would be expected at these locations. Beryllium was also detected
at high concentrations in soil samples from the northern side of the plant and
the leased property north of the site. Final characterization to delineate the
boundaries of the contaminated areas will take place immediately before
remedial action begins.
REMEDIAL ACTION
In 1959, when the Atomic Energy Commission contracted Brush Wellman to close
the plant, a 3.4-hectare (8.5acre) dike-enclosed landfill was constructed
in the northeastern corner of the property, and hazardous sludge and
contaminated soil were moved from three lagoons to the landfill. Historical
records indicate that the plant closure plan specified leveling the dikes on
the empty lagoons and filling the lagoons with sufficient clay to bring the
areas to ground level. The landfill area was then capped, graded, and seeded.
Site remediation under Department of Energy FUSRAP is in its initial planning
stages. The scope of work for FY 1995 and FY 1996 consists of a
preliminary characterization phase including analysis of historical records,
site drawings, and site photographs to characterize site topography, drainage
patterns, vegetation, and relationships to adjoining areas, and also to
determine the focus of final characterization. Before remedial action begins,
detailed radiological characterization of the surface and subsurface is
recommended to define more precisely the extent of contamination.
Cleanup alternatives will be developed and evaluated as required under the
Comprehensive Environmental Response, Compensation, and Liability Act and the
National Environmental Policy Act. Interim removal actions will be initiated if
needed to address contamination on any portion of the site before the Record of
Decision is finalized, and environmental impacts will be documented in an
Engineering Evaluation/Cost Analysis report and a categorical exclusion report
as required by the National Environmental Policy Act. The selected cleanup
option will be implemented after public review of the Remedial
Investigation/Feasibility StudyEnvironmental Impact Statement and issuance
of a Record of Decision.
The Department of Energy is currently considering an onsite remedy; however,
the Comprehensive Environmental Response, Compensation, and Liability Act
requires the Department to consider other alternatives. The scenario used for
the Baseline Environmental Management Report cost estimate assumes excavation
of contaminated soils and disposal by consolidation and onsite capping. The
cost estimate assumes a total volume of 26,400 cubic meters (34,500 cubic
yards) of chemical and lowlevel radioactive waste and transfer of
responsibility for longterm surveillance and monitoring to the Grand
Junction Projects Office in FY 2007. Given that the site has not yet been
characterized, the estimate is based on consolidating all onsite waste
materials on top of already contaminated subsurface pits, landfills, or
lagoons, then adding an impermeable cap to minimize water infiltration. The
size, number, and configuration of the onsite disposal cell(s) have not yet
been determined.
Environmental Restoration Activities Cost Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2015
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2020
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2025
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2030
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| FUSRAP - Luckey Site
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|
|
|
|
|
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|
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| Assessment
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2,786
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|
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|
|
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13,930
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| Remedial Action
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3,580
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6,046
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123
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|
|
|
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48,747
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| Total
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6,366
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6,046
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123
|
|
|
|
|
62,677
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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FUNDING ESTIMATE
The following table presents estimated funding information for the Luckey site.
Nondefense Funding Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2015
|
2020
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2025
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2030
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| Environmental Restoration
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6,366
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6,046
|
123 |
|
|
|
|
62,677
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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