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The 52-hectare (128-acre) Salt Lake City site is located about 6.4 kilometers
(four miles) south-southwest of the center of Salt Lake City. An ore-processing
mill and ore storage and transportation facilities were located on 3.2 hectares
(eight acres) on the eastern portion of the site. Tailings occupied the
remaining 49 hectares (120 acres) with piles up to five meters (16 feet) high.
LOCALITY MAP
Estimated Site Total
| (Thousands of Current Year Dollars)
|
| |
|
|
|
| Environmental Restoration
|
285
|
90
|
160
|
222
|
1,731
|
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
|
1,275
|
|
|
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
|
|
545
|
|
|
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2010
|
2015
|
2020
|
2025
|
2030
|
| Environmental Restoration
|
453
|
1,002
|
|
|
|
|
|
7,274
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
FACILITY MISSION
The mission of the Salt Lake City mill site was to provide uranium for the
United States Government. The source of contamination was the residual tailings
that remained after the milling process extracted the uranium. The plant was
originally built during World War II for the production of aluminum from
aluminite. In 1951, Vitro Corporation of America acquired the plant to process
uranium ore. In 1964, the plant was converted to produce vanadium. Production
ceased in 1968 and by 1970, the plant had been dismantled. The site has changed
ownership several times and is now owned by the Central Valley Water Treatment
Facility Board.
SITE MAP
The Environmental Management program is responsible for cleaning up surface-
and ground-water contamination at the UMTRA sites. The Uranium Mill Tailings
Radiation Control Act designated the residual radioactive material found at
this site for cleanup and stabilization. The Act directed the Environmental
Protection Agency to promulgate standards (Code of Federal Regulations, Title
40, Part 192) and the Department of Energy to perform the cleanup. It also
assigned the Nuclear Regulatory Commission to oversee and certify the cleanup,
and license the completed disposal cell.
Pursuant to the Uranium Mill Tailings Radiation Control Act, the Department of
Energy entered into a Cooperative Agreement in 1983 with the State of Utah. The
agreement outlines the roles and responsibilities of each party. It also
delineates the cost sharing arrangement that makes the Department of Energy
responsible for 100 percent of the assessment costs and 90 percent of the
remediation costs, and the State responsible for the remaining 10 percent of
the remediation costs. In addition, the Department of Energy is responsible for
paying 90 percent of the State's 10 percent, and the State is responsible for
the remaining 10 percent of these costs (one percent of the total). The Nuclear
Regulatory Commission concurred on the original agreement and is required to
concur on all major modifications.
FUTURE USE
Residual radioactive materials from the Salt Lake City site were relocated to
the Clive disposal site, which is currently owned by the State of Utah. Upon
Nuclear Regulatory Commission certification, the State will transfer the deed
to the Clive site to the Federal Government, under the custody of the
Department of Energy. It will be monitored and maintained in accordance with
the Long-term Surveillance Plan approved by the Nuclear Regulatory Commission.
Under the provisions of the Uranium Mill Tailings Radiation Control Act, public
access to the disposal site will be restricted. Remedial action at the Vitro
processing site was performed under a Remedial Action Agreement with Central
Valley Water Reclamation Facility. Under the terms of the Remedial Action
Agreement, the site will be returned to private ownership for beneficial use
upon certification of compliance with Subpart B of the Environmental Protection
Agency ground-water protection standards. Some restricted use will be allowed
following certification of the surface cleanup. The near-term future use is
Recreational, and the long-term future use is Industrial/Commercial.
ENVIRONMENTAL RESTORATION
Surface remedial action has been completed, and the source of contamination has
been stabilized. However, residual milling-related contaminated ground water
remains.
Environmental Restoration Activities Cost Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2010
|
2015
|
2020
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2025
|
2030
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| UMTRA Surface
|
|
|
|
|
|
|
|
|
| Assessment
|
10
|
|
|
|
|
|
|
49
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| UMTRA Ground water
|
|
|
|
|
|
|
|
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| Assessment
|
104
|
215
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|
|
|
|
|
1,596
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| Remedial Action
|
2
|
28
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|
|
|
|
|
149
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| Direct Program Management/Support
|
337
|
759
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|
|
|
|
|
5,480
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| Total |
453
|
1,002
|
|
|
|
|
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7,274
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
Surface Project
Remedial action was completed in May 1989 and involved relocating the residual
radioactive material from the former processing site to the disposal site at
Clive, Utah, located 137 kilometers (85 miles) west of Salt Lake City. A total
of approximately 2,059,600 cubic meters (2,710,000 cubic yards) of contaminated
materials was remediated. Concurrent with site remediation activities, 118
vicinity properties were remediated. Nuclear Regulatory Commission
certification of the disposal site is scheduled for August 1997, with Nuclear
Regulatory Commission licensing expected in January 1998.
Major Surface Project Milestones
| Nuclear Regulatory Commission Issues General License
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1998
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|
Transfer Site to Grand Junction Projects Office's Long-Term Surveillance and
Maintenance Program
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1998
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The Salt Lake City Remedial Action Plan outlined the contaminant distribution
and remediation needed. The Remedial Action Plan, which requires concurrence by
the Nuclear Regulatory Commission, was published in March 1993.
The UMTRA Surface Project will conduct surveillance and maintenance of the
disposal cell after completion of remedial action and prior to its transfer to
the Grand Junction Projects Office's Long-Term Surveillance and Maintenance
program in FY 1998.
Ground-Water Compliance Project
The Department is developing a Programmatic Environmental Impact Statement
pertaining to all 24 UMTRA sites. For a discussion of the Programmatic
Environmental Impact Statement, see the UMTRA program narrative in the New
Mexico section of this report. Site-specific National Environmental Policy Act
documentation will be developed to propose an appropriate ground-water
compliance strategy and reasonable alternatives for the Salt Lake City site
once the Programmatic Environmental Impact Statement is completed.
This report assumes a demonstrated compliance strategy with additional
characterization and the application of supplemental standards. This compliance
strategy is based on the evaluation of the existing conceptual model. For all
types of ground-water compliance strategies, once the Nuclear Regulatory
Commission determines the site to be in compliance with Subpart B of the
Environmental Protection Agency Standards and the site is certified, no
additional long-term surveillance or monitoring will be conducted.
The total volume of contaminated ground water is estimated to be 2.6 billion
liters (700 million gallons), and the contaminant plume extends offsite. The
ground-water contaminants of potential concern are chloride, fluoride,
magnesium, manganese, molybdenum, radium-226, sodium, sulfate, and uranium.
The following milestone dates have been established for planning purposes.
Major Ground-Water Compliance Project Milestones
| Site Observational Work Plan
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2003
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Publish Environmental Assessment/Finding of No Significant Impact
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2004
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Publish Remedial Action Plan
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2005
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Licensing
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2005
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Ground water in the shallow unconfined aquifer is contaminated as a result of
uranium processing activities. Sampling of the lower, confined aquifer system
does not indicate site-related contamination of the ground water. Limited
sediment sampling indicates that the South Vitro Ditch, an irrigation ditch
traversing the site, may have high levels of molybdenum, while the remaining
samples show no adverse effects from site-related contamination.
Contaminant migration in ground water in the unconfined aquifer west and
northwest of the processing site may be occurring, but the full extent of
contamination is not known because monitoring wells were not established at
downgradient, offsite locations. Increased concentrations of sulfate and the
other indicator parameters in wells on the south and east boundaries of the
site indicate that contamination of the shallow aquifer is extending into these
areas of the processing site.
Direct Program Management/Support
Program management supports management efforts for the National Environmental
Policy Act process, site characterization and licensing, public
information/participation, applicable state and federal regulator costs,
quality assurance audits, program and management support for the technical
assistance contractor, special studies, document control, technical assistance
contractor site and technical management, cost and schedule controls, planning
and preparation of the federal budget, and the Environmental Management
Progress Tracking System.
FUNDING ESTIMATE
The following table presents estimated funding information for the Salt Lake
City site.
Nondefense Funding Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2010
|
2015
|
2020
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2025
|
2030
|
| Environmental Restoration
|
453
|
1,002
|
|
|
|
|
|
7,274
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
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