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The Painesville site (formerly the Diamond Magnesium Company) is located at
720 FairportNursery Road in Painesville, Ohio, approximately
35 kilometers (22 miles) northeast of Cleveland. About a third of the
site was originally covered by large buildings and rail lines. Some of the
original buildings have been removed, but others are still in use by the
current owner, the Uniroyal Chemical Company. The property also contains a
waste lake west of the buildings and several lagoons formerly used for sludge
and equalization. The site covers approximately 60 hectares
(150 acres).
LOCALITY MAP
Estimated Site Total
| (Thousands of Current Year Dollars)
|
| |
|
|
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| Environmental Restoration
|
98
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2,271
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5,884
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6,478
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4,887
|
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.
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| 1996 Appropriation
|
231 |
|
|
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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4,779
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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
|
3,624
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7,651
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6,328
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|
|
|
|
88,012
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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
Lowlevel radioactive contamination at the Painesville site consists of
uraniumcontaminated material; the estimated total waste volume is 53,000
cubic meters (69,000 cubic yards). Contamination originated from
approximately 725 metric tons (800 tons) of radioactively contaminated
scrap steel that the Atomic Energy Commission shipped from the Lake Ontario
Storage Area to the Diamond Magnesium Company for use in magnesium production
processes. Scrap steel that was not used immediately was stored in an area on
the western side of the property, near the railroad tracks, and possibly at
other onsite locations. The radioactive contamination was incidental to the use
of the scrap metal, which was generated from discarded iron drums previously
used to store uranium compounds associated with pitchblende operations. The
site was included in FUSRAP in 1992. The Department of Energy's present
objective at the site is to eliminate or reduce the potential for exposure to
radioactive contaminants.
SITE MAP
Based on current use, the Painesville site has a low priority for cleanup
because it poses no immediate health risk to the public, the environment, or
individuals who access the area. Although the site is currently operating as an
industrial facility, it would be highly unlikely that an individual working in
or frequenting the contaminated areas would sustain significant radiation
exposure.
FUTURE USE
The site will be released for use with no radiological restrictions after
completion of remedial action. This baseline assumes that use of the site will
continue to be Industrial/Commercial.
ENVIRONMENTAL RESTORATION
This report assumes that environmental restoration of the Painesville site will
include disposition of approximately 53,000 cubic meters (69,000 cubic
yards) of contaminated soil. This baseline assumes that remediation 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. As required by
the Comprehensive Environmental Response, Compensation and Liability Act, the
development of remediation goals for the site incorporates the applicable or
relevant and appropriate requirements of federal and state laws.
Key regulators are Environmental Protection Agency Region V, the Ohio
Environmental Protection Agency, the Ohio Department of Health, and local
governments as appropriate. Other potential regulatory drivers 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 consist of a
Remedial Investigation/Feasibility Study-Environmental Impact Statement. The
schedule for final cleanup depends on funding and the issuance of a Record of
Decision, as required by the Comprehensive Environmental Response,
Compensation, and Liability Act/National Environmental Policy Act process.
Major Environmental Restoration Activity Milestones
| Assessment (Record of Decision)
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2001
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Remedial Action
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2010
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Transfer Site to Grand Junction Projects Office Long-Term Surveillance and
Monitoring Program
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2011
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ASSESSMENT
A radiological survey of surface and subsurface areas in 1990 detected the
primary contaminants at the site (uranium238 and radium226) at
concentrations exceeding current guidelines. Widespread radioactive
contamination was found outdoors within facility property boundaries, and
elevated radionuclide concentrations were discovered in a small area on the
nearby Lonza Chemical Company property. Relatively high concentrations of lead
were found in a soil sample that also contained elevated levels of
radium226; this observation is typical of residues from pitchblende
operations. In 1988, a preliminary radiological survey identified
uranium238 and radium226 at concentrations above guidelines in soil
samples from the area west of the buildings near the railroad car spill
containment basin.
Previous field investigations at the Painesville site included radiological
surveys in 1988 and 1990. The preliminary survey in 1988 included a gamma scan
of selected portions of the property and collection of surface and subsurface
soil samples. No indoor survey measurements were performed. The 1990
investigation included a gamma scan of the ground surface in accessible areas
throughout the Uniroyal property and over a 15-meter (50foot) wide strip
of land on the Lonza property adjacent to the property line; gamma radiation
measurements; collection and radiological analysis of systematic and biased
samples of surface and subsurface soils; collection and analysis of soil
samples from auger holes and gamma logging of the holes; direct gamma radiation
measurements within three buildings formerly used for magnesium reduction
processing; and analysis of a radioactive rock sample by thermal emission mass
spectrometry.
The radiological characterization identified widespread radioactive
contamination outdoors on the Uniroyal property and elevated radionuclide
concentrations in a small area on the Lonza property. The contamination on the
Uniroyal property was found in two large areas reportedly used for storage of
scrap metal and in numerous smaller areas and isolated spots throughout the
site. Elevated radium226 and thorium230 concentrations were found in
both surface and subsurface soil on both properties. Detailed characterization,
including drilling and sampling, will be conducted before cleanup begins.
REMEDIAL ACTION
The Department of Energy has not yet conducted any remedial action at the
Painesville site. The selection of a preferred cleanup option will depend on
results from the upcoming characterization, which will provide further
information about the nature and extent of contamination and sitespecific
waste management requirements. The scenario used for the Baseline Environmental
Management Report cost estimate assumes excavation of contaminated soils and
disposal by consolidation and onsite capping. Responsibility for longterm
surveillance and monitoring of an assumed total volume of 53,000 cubic
meters (69,000 cubic yards) of lowlevel waste would transfer to the
Grand Junction Projects Office in FY 2011.
In the very near future, Uniroyal plans to install a new above-ground storage
tank in or near the contaminated area. This construction effort will involve
soil disturbance. The soils that are excavated for a concrete foundation pad
will be consolidated, surrounded with a berm to reduce potential runoff, kept
covered to prevent spread of contaminants, and monitored. This lowlevel
waste will remain covered until completion of the onsite cap.
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 - Painesville Site
|
|
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|
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|
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| Assessment
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3,624
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634 |
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|
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21,289
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| Remedial Action
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|
7,017
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6,328
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66,723
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| Total
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3,624
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7,651
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6,328
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|
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88,012
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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 Painesville
site.
Nondefense Funding 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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| Environmental Restoration
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3,624
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7,651
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6,328
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|
|
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88,012
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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