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The Colonie Site is located at 1130 Central Avenue in the Town of Colonie
in Albany County, New York, approximately 6.5 kilometers (4 miles)
northwest of downtown Albany. The site comprises about 4.5 hectares
(11.2 acres) and consists of five buildings of varying sizes,
approximately 1.6 hectares (4 acres) of paved surface, and approximately
1.6 hectares (4 acres) of grassland.
LOCALITY MAP
Estimated Site Total
| (Thousands of Current Year Dollars)
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|
|
|
|
| Environmental Restoration
|
9,474
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21,578 |
13,046
|
8,599
|
662
|
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
|
9,463
|
|
|
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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|
19,756
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|
|
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
|
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| Environmental Restoration
|
10,236 |
101
|
|
|
|
|
|
51,682
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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FACILITY MISSION
From 1937 to 1984, National Lead Industries owned and operated the Colonie
site, first as a foundry and later as a site for manufacturing components using
uranium and thorium. During the manufacturing operations, the plant released
radioactive materials from its exhaust stacks. As a result, radioactive
constituents were spread to 56 commercial and residential properties near
the site. Fifty-three of these properties have been cleaned up. The other three
properties are adjacent to the site and will be cleaned up during grounds
remediation.
SITE MAP
National Lead also buried manufacturing waste onsite in a former lake bed.
Radiological and chemical characterization has indicated large areas where
radionuclides, hazardous chemicals, and heavy metals are present at levels
above guidelines. The National Lead building contains radioactive and chemical
constituents at levels exceeding guidelines. Chemicals above Environmental
Protection Agency guidelines include metals and inorganic compounds that were
used during plant operations.
In 1984, Congress authorized the transfer of ownership of the Colonie Site from
National Lead, Inc. to the Federal Government. Congress also authorized the
cleanup of residual radioactive waste from the site and nearby private
properties. Congress assigned the work to the Department of Energy, to be
performed under FUSRAP. FUSRAP began work almost immediately in 1984 by taking
actions to put the facility in a safe shutdown mode. Radiological surveys
identified 56 vicinity properties with residual radioactivity above guidelines.
Between 1985 and 1988, FUSRAP removed approximately 920 cubic meters
(1,200 cubic yards) of materials (including soils and roofing) containing
low levels of radioactivity from 53 vicinity properties and stored them inside
the main building at Colonie for future disposition. FUSRAP also stored drums
containing radioactive waste and radioactive mixed waste as defined by the
Resource Conservation and Recovery Act. Areas of residual radioactivity on the
final three adjacent properties will be remediated with the Colonie Site
grounds. An environmental surveillance program was initiated to determine the
effect of site activities on public health and the environment. Other
activities included characterization of the site grounds and caretaker
maintenance of the main production facility, an 11,200square meter
(120,000square foot) building, and four smaller outbuildings.
Before the Department of Energy assumed ownership, waste regulated under the
Resource Conservation and Recovery Act was stored onsite at Colonie. As a
result, a Resource Conservation and Recovery Act Part A interim status permit
application was on file with the New York State Department of Environmental
Conservation. On November 8, 1992, that agency terminated Resource
Conservation and Recovery Act interim status for all facilities; as a result,
the Department of Energy submitted a Resource Conservation and Recovery Act
facility closure plan to the state. On January 5, 1993, New York State
Department of Environmental Conservation approved the closure plan, and closure
activities were initiated.
Historical investigations have identified four primary sources of radioactive
and chemical constituents at the site: constituents in surface and subsurface
soil within the former Patroon Lake; structures, equipment, and other materials
within the building, such as waste drums; radioactivity in asphalt and building
surfaces; and possibly pyrophoric uranium buried beneath a loading dock on the
eastern side of the main building.
No health risks are associated with soil chemicals at the site. Because the
three vicinity properties that have yet to be cleaned up are uninhabited, the
contamination poses little or no risk to the public. Since 1984, when
environmental surveillance at the site began, analytical results have
consistently shown that Colonie is not contributing significantly to
radioactivity in the environment. The additional radiation dose to the offsite
population attributable to the site is very close to zero.
FUTURE USE
The selection of a remedy for cleanup of the Colonie site is likely to be based
on the release of the land back to the community. The cost estimate assumes
light industrial/commercial, or recreational use after remediation. This is
consistent with current land use in the surrounding area.
ENVIRONMENTAL RESTORATION
National Lead's previous operations resulted in the introduction of radioactive
and chemical constituents into the onsite soils. The radioactive constituents
found in the Colonie building, grounds, and vicinity property soils resulted
from the production of items manufactured from uranium and thorium from 1958 to
1984, under license from the Atomic Energy Commission. Chemical constituents
resulted from brass foundry operations at the site from 1927 through 1960.
Products manufactured during the lead foundry operations consisted of brass
bearing housings from babbitt metal (an alloy of lead, copper, and antimony)
and other brass products. These operations have left the surface and subsurface
soil with radioactive constituents and metals above federal and state
guidelines for unrestricted use of the property. The ground water within the
Colonie property contains radioactive constituents, metals, and volatile
organic compounds at levels above federal and state drinking water standards,
but these materials are not migrating beyond the site boundaries. The primary
contaminants of concern at Colonie are uranium238, thorium232,
copper, and lead.
The Colonie Site is being cleaned up under authority granted to the Department
of Energy under the Comprehensive Environmental Response, Compensation, and
Liability Act. Key regulators for the site are the New York State Department of
Environmental Conservation and the Environmental Protection Agency
Region II. Cleanup includes two Comprehensive Environmental Response,
Compensation, and Liability Act removal actions, one for the site buildings and
one for the site grounds. Two Engineering Evaluations/Cost Analyses constitute
the compliance documentation to support these removal actions. The Engineering
Evaluation/Cost Analysis for the site buildings was approved and is being
implemented. The site grounds Engineering Evaluation/Cost Analysis is expected
to be finalized in November 1996.
Major Environmental Restoration Activity Milestones
| Remedial Action |
2001
|
ASSESSMENT
This report assumes that all assessment activities are complete at this site.
National Lead and the Department of Energy have performed numerous site
characterization activities at Colonie, including surface feature
investigations, walkover surveys to detect gamma radiation, and sampling of
environmental media such as surface and subsurface soil, sediment, surface
water, ground water, and air. In 1978, National Lead performed a radiological
survey to assess the conditions of the plant and make recommendations regarding
corrective measures. In 1980 and 1981 National Lead conducted additional
radiological characterization to determine the extent of surface soil
contamination at the site and its vicinity properties as a result of stack
emissions and to determine the extent of subsurface contamination. In 1981, the
Department of Energy performed investigations to define soil and sediment
background activity levels.
The Department of Energy conducted a preliminary geological investigation of
the site after its transfer in 1984 and began a routine environmental
monitoring program, which is still in place. In 1988, the Department conducted
a radiological designation survey of the Conrail vicinity property. More
recently, additional Department of Energy characterization studies have
involved soil-gas, soil, sediment, surface-water, and ground-water sampling, in
addition to estimating the volume of soil containing radioactive and chemical
constituents.
An environmental surveillance program has been in place at the site since 1984.
The Department of Energy periodically samples air, ground water, and soil to
detect the presence of radiological and chemical constituents at levels above
background. An annual report presents a compilation and interpretation of the
previous year's monitoring and sampling data. During activities such as
building dismantlement or residential excavations, the Department conducts
additional monitoring to prevent the spread of radioactive and chemical
constituents.
REMEDIAL ACTION
The scenario used for the Baseline Environmental Management Report cost
estimate assumes building remediation [limitedscope decontamination and
full dismantlement of the 11,200square meter (120,000square foot)
building and demolition of four smaller outbuildings], soil excavation, and
disposal at an existing outofstate commercial disposal facility.
Cleanup of the site includes two Comprehensive Environmental Response,
Compensation, and Liability Act removal actions to address the former National
Lead buildings and the site property. The first removal action addresses the
main plant building; the second will involve remediation of the site property
and the remaining three vicinity properties.
The volume of waste to be addressed under FUSRAP is estimated at
41,300 cubic meters (53,900 cubic yards) of soils and building
rubble. During building remediation, additional disposal of waste and recycled
materials included approximately 1,900 cubic meters (2,500 cubic
yards) of lowlevel radioactive and mixed waste; 23,500 liters
(6,200 gallons) of lowlevel liquid waste and mixed liquids; and
1.1 million kilograms (2.5 million pounds) of steel.
Pollution control activities during building decontamination consisted of using
a 560cubicmeterperminute
(20,000cubicfootperminute) High-Efficiency Particulate Air
filtration ventilation system to exhaust the interior. The Department is using
water misting as a dust suppressant during building dismantlement. Building
materials such as brick and concrete will be reduced in a rock crusher. A
National Emissions Standards for Hazardous Air Pollutants calculation for
radionuclide emissions during building dismantlement activities indicated
concentrations of radionuclides below Environmental Protection Agency
guidelines.
The Department has closed the Resource Conservation and Recovery Act portion of
the site under an approved closure plan in accordance with applicable site
closure regulations; the Department shipped associated waste to an
outofstate commercial disposal facility. Mixed waste treatment at the
site has consisted of lowtemperature thermal desorption, alkaline
chlorination, nitric acid oxidation, reagent oxidation, air stripping, solvent
extraction, and stabilization. After acceptable processing through the above
treatment, the Department shipped the waste to an outofstate disposal
facility via highway transportation. The Department completed this work in
September 1995.
In 1994, the Department shipped all vicinity property soils stored onsite out
of state for disposal. In 1995, site buildings were dismantled in accordance
with supporting environmental documentation, which consists of an Engineering
Evaluation/Cost Analysis. The Department is treating the remaining waste
associated with the Comprehensive Environmental Response, Compensation, and
Liability Act activities and expects to disposition it during FY 1996 and FY
1997.
Environmental Restoration Activities Cost Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
|
|
2010
|
2015
|
2020
|
2025
|
2030
|
| FUSRAP - Colonie Site
|
|
|
|
|
|
|
|
|
| Remedial Action
|
10,236 |
101
|
|
|
|
|
|
51,682
|
| * 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 Colonie
Site.
Nondefense Funding Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
|
|
2010
|
2015
|
2020
|
2025
|
2030
|
| Environmental Restoration
|
10,236 |
101
|
|
|
|
|
|
51,682
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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