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The Bowman site is located in southwestern North Dakota, 11 kilometers (seven
miles) west of the Town of Bowman, near a railroad and close to the head of
Spring Creek, a part of the Grand River drainage basin. Bowman is approximately
105 kilometers (65 miles) southwest of the Belfield site. An unpaved road
separates the five-hectare (12-acre) site into two tracts and the site is
overgrown with nonnative grasses. Structures and equipment used at the site
have been removed; only a small amount of concrete rubble and a few pieces of
piping remain. Wind-blown materials have contaminated an additional 21 hectares
(53 acres) of land.
LOCALITY MAP
Estimated Site Total
| (Thousands of Current Year Dollars)
|
| |
|
| Environmental Restoration
|
308
|
376
|
329
|
381
|
583
|
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
|
0
|
|
|
These levels reflect the current estimates for
compliance with applicable statutes and agreements (as of March 1996), see
Readers' Guide.
|
| 1997 Congressional Request
|
|
0
|
|
|
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2010
| 2015
|
2020
|
2025
|
2030
|
| Environmental Restoration
|
370
|
633
|
|
|
|
|
|
5,017
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
FACILITY MISSION
The mission of the Bowman site was to provide uraniferous ash for processing at
the Ambrosia Lake, New Mexico and Rifle, Colorado mill sites for the United
States Government. The source of contamination was the residual radioactive
material that remained after a lignite coal ashing process concentrated the
uranium that was found in the coal. The ash from this process is different than
the usual mill tailings found at the other UMTRA sites. Kermac Nuclear Fuels
Corporation produced the ash from 1963 until 1967, when it was shipped to
Grants, New Mexico for further processing. Currently, this site has
unrestricted access; it has been planted with natural grass as a source of hay.
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.
FUTURE USE
Prior to the start of site remedial action, the State of North Dakota will
acquire the Bowman former processing site. Upon completion of remedial action
and Nuclear Regulatory Commission site certification, the State of North Dakota
will transfer the deed for the disposal site (Bowman) 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. Public access to the disposal site will be
controlled. Upon Nuclear Regulatory Commission certification of compliance with
the Environmental Protection Agency ground-water protection standards,
ownership of the portion of the property not used for the disposal cell will be
returned to the private landowners. The future use of the former processing
site is likely to be Agricultural.
ENVIRONMENTAL RESTORATION
Contaminated soil, gravel, and rubble from the site are the only residual
radioactive materials that require surface project remediation. Residual
milling-related contaminated ground water is also present. See the
Environmental Restoration Projects Cost Estimate table in the Belfield
narrative. Belfield and Bowman restoration activities will be combined to
reduce costs.
Environmental Restoration Activities Cost Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
| UMTRA Surface
|
|
|
|
|
|
|
|
|
| Assessment
|
95
|
|
|
|
|
|
|
476
|
| UMTRA Ground water
|
|
|
|
|
|
|
|
|
| Assessment
|
58
|
98
|
|
|
|
|
|
781
|
| Remedial Action
|
|
12
|
|
|
|
|
|
58
|
| Direct Program Management/Support
|
217
|
523
|
|
|
|
|
|
3,702
|
| Total
|
370
|
633
|
|
|
|
|
|
5,017
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
Surface Project
The Remedial Action Plan involves stabilizing the residual radioactive
materials onsite. The residual radioactive materials at the Belfield site will
be relocated to the disposal cell at Bowman. Remedial action under the Surface
Project at the former Bowman processing site will be performed under a Remedial
Action Agreement between the Department of Energy, State of North Dakota, and
the private land owners.
Approximately 97,280 cubic meters (128,400 cubic yards) of ash-contaminated
soils require remediation. The ash-contaminated soils have slightly elevated
concentrations of molybdenum, arsenic, and radium226. In the proposed
surface remedial action, scheduled to start in FY 1996, all residual
radioactive material from both the Belfield and the Bowman sites will be
consolidated and stabilized in a single disposal cell on the Bowman site. The
disposal cell will be covered with a low-permeability infiltration/radon
barrier and erosion protection cover to ensure long-term stability of the cell,
retard infiltration, reduce seepage of tailings fluids to ground water, and
prevent radon emanation. The site is currently privately owned. Acquisition by
the State is pending.
Approximately 44,080 cubic meters (58,000 cubic yards) of contaminated
materials from the Belfield site are scheduled to be transported to the Bowman
disposal cell, where they will be stabilized to meet 40 Code of Federal
Regulations 192 requirements. Approximately 76,000 cubic meters (100,000 cubic
yards) of contaminated materials from the Bowman site will be stabilized
onsite. Concurrent with site remediation, five vicinity properties will be
remediated. There are no transportation issues at this site since the tailings
will be stabilized in place. Remedial action is scheduled to begin in FY 1996
and end in FY 1997. Nuclear Regulatory Commission certification and licensing
of the disposal cell will take place in FY 1998, with transfer to the Grand
Junction Projects Office's Long-Term Surveillance and Maintenance Program in
late FY 1998.
Major Surface Project Milestones (On Hold)
| Finalize Environmental Assessment and Publish
Findings of No Significant Impact
|
1996
|
|
Publish Remedial Action Plan
|
1996
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| Site and Vicinity Property Remedial Action
|
1997 |
| Nuclear Regulatory Commission Issues General
License
|
1998
|
| Transfer to Grand Junction Projects Office's
Long-Term Surveillance and Maintenance Program
|
1998
|
The site has been fully characterized, and no further monitoring of any media
is occurring. The Belfield/Bowman, North Dakota Remedial Action Plan outlines
the necessary contaminant distribution and remediation. The Remedial Action
Plan, which requires Nuclear Regulatory Commission concurrence, will be
published in March 1996.
The Long-term Surveillance Plan, which describes how the disposal site will be
managed, will be written concurrently with the site Completion Report and final
Audit Report. These two documents will be included in the Department of
Energy's site Certification Report, which states that the processing site has
been cleaned up according to the provisions of the Remedial Action Plan. The
site Certification Report and the Long-term Surveillance Plan will be submitted
to the Nuclear Regulatory Commission for concurrence as the first step towards
licensing the disposal cell.
Between completing site remedial action and transferring the licensed site's
surveillance activities to the Long-Term Surveillance and Maintenance Program,
annual site inspections and custodial maintenance will be conducted under the
UMTRA Surface Project's Prelicensing Custodial Care activities. The prime
objective will be to maintain cell integrity.
Ground-Water Compliance Project
A Programmatic Environmental Impact Statement pertaining to all 24 UMTRA sites
is being developed. 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 Bowman site once the Programmatic Environmental
Impact Statement is completed.
This report assumes a No Further Action compliance demonstration with the
application of supplemental standards for the Bowman site. Because there is
extensive ambient contamination in the upper aquifer (zone), the ground water
classifies as a limited use resource and supports the application of
supplemental standards. 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 it is
certified, no additional long-term surveillance or monitoring will be
conducted.
Some constituents of concern (such as antimony, chromium, lead, molybdenum,
selenium, uranium, and vanadium) occur naturally at elevated concentrations in
shallow ground water adjacent to lignite zones in this region of North Dakota.
This has made it difficult to distinguish between potential ground-water
contamination related to the former uranium processing activities at the site
and the impact of naturally occurring concentrations of these constituents.
Possible sources of nitrate are fertilizer applied to crop areas, farmyard
waste, and septic tank effluent.
The following milestone dates have been established for planning purposes.
Major Ground-Water Compliance Project Milestones (On Hold)
| Baseline Risk Assessment
|
1994 |
| Site Observational Work Plan
|
2002
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| Publish Environmental Assessment/Finding of No
Significant Impact
|
2003
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| Publish Remedial Action Plan
|
2004
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| Licensing
|
2005
|
Water quality sampling was conducted at the Bowman site from 1986 until 1993. A
comprehensive list of constituents was analyzed during screening monitoring to
determine background and baseline ground-water quality in the zones of interest
beneath the site.
Ground-water samples collected from onsite and downgradient monitor wells at
the Bowman processing site were analyzed to determine the extent and magnitude
of ground-water contamination related to the uranium processing activities. In
the upper zone, average concentrations of molybdenum, selenium, and uranium in
ground water exceeded the Environmental Protection Agency maximum concentration
limits. Nitrate concentrations were approximately two times higher than the
Environmental Protection Agency maximum concentration limits in one monitor
well. It is probable that they are the result of agricultural activities.
Contaminants in ground water that exceed background concentrations do not form
a discrete plume in the upper zone downgradient from the processing site.
The extent of ground-water contamination in the lignite zone is less than
ground-water contamination in the fine-grained sediments of the upper zone.
Concentrations of selenium and activities of net gross alpha and radium exceed
the Environmental Protection Agency maximum concentration limits in ground
water. In the lower zone, the concentrations of all constituents considered in
the proposed Environmental Protection Agency ground-water standards were below
maximum concentration limits.
Uranium in shallow ground water downgradient from the site does not appear to
be related to site contamination but instead represents natural concentrations.
Site-related contamination has not impacted ground water in the lower zone.
Water sampling activities were not conducted in 1994 because the ground-water
conditions at the site are relatively stable. The next water sampling event is
scheduled before the start of surface remedial action activities and will
include sampling selected monitor wells at the sites and several domestic wells
in the vicinity.
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 Bowman site.
Nondefense Funding Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2010
|
2015
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2020
|
2025
|
2030
|
| Environmental Restoration
|
370
|
633
|
|
|
|
|
|
5,017
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| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
|