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The Department established the Environmental Management program in 1989 to
address the environmental legacy of nuclear weapons production and other
sources of potential pollutants such as nuclear research. The Environmental
Management program encompasses six major functional areas: (1) environmental
restoration, (2) waste management, (3) nuclear material and facility
stabilization, (4) science and technology development (5) landlord, and (6)
national program planning and management. These six areas are all interrelated.
Figure 2.1 graphically depicts the scope of the Environmental Management
program and the key interrelationships of the six major areas. Waste management
involves the safe treatment, storage, and disposal of existing waste and waste
yet to be generated. Environmental restoration activities address remediation
of contaminated soil and water as well as decommissioning of contaminated
surplus facilities. Nuclear material and facility stabilization involves
stabilizing and consolidating special nuclear materials such as plutonium and
highly enriched uranium and deactivating surplus facilities to a safe, low
maintenance condition while awaiting final decommissioning. Science and
technology development refers to a variety of basic and applied research
activities that explore more effective and less expensive remedies to address
the environmental and safety problems of the Environmental Management program.
Landlord functions represent crosscutting site-wide support activities such as
road maintenance and fire and ambulance services. National program planning and
management encompasses Headquarters functions. The following subsections
describe each major area.
Figure 2.1. Overview of Environmental Management Activities
The U.S. Department of Energy requires management of its sites and facilities
in compliance with applicable federal, state, and local regulations. The Base
Case described in this report is a "compliance case" (that is, based on
compliance with all applicable provisions of laws, permits, regulations,
orders, and agreements) in effect throughout the Department of Energy complex.
The following box provides a list of the major federal laws that directly
influence the functional area strategies outlined in this chapter.
LEGAL REQUIREMENTS DRIVING THE ENVIRONMENTAL MANAGEMENT PROGRAM
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Resource Conservation and Recovery Act, as amended
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Comprehensive Environmental Response, Compensation, and Liability Act, as
amended
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National Environmental Policy Act
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Federal Facility Compliance Act
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Clean Air Act, as amended
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Clean Water Act, as amended
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Safe Drinking Water Act, as amended
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Toxic Substances Control Act, as amended
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Atomic Energy Act, as amended
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Uranium Mill Tailings Radiation Control Act
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Low-level Waste Policy Act, as amended
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2.1 ENVIRONMENTAL RESTORATION
Mission
The Environmental Restoration program's overall mission is to protect human
health and the environment from risks posed by inactive, surplus facilities and
contaminated areas. The program is accomplishing this mission by remediating
sites and facilities in the most cost-efficient and responsible manner possible
to provide for future beneficial use while complying with applicable
environmental regulations. Environmental restoration activities are prioritized
based upon various factors, including the goals of reducing risks at all sites
and compliance with existing laws, regulations, and agreements. Most actions
are designed to either clean up or contain contamination in the environment
(including soil, ground water, and surface water) or to decommission
contaminated buildings (including reactors and chemical processing buildings).
Related activities conducted to support these actions may include immediate
treatment of contaminated soils or ground water, packaging of waste for
commercial treatment and/or disposal, and onsite disposal of consolidated
contaminated media such as soils or building rubble.
Cleanup goals and remedies for each contaminated area are decided through
processes established by federal and state laws and other legal agreements.
These processes involve decisionmakers outside of the Department such as the
states, the U.S. Environmental Protection Agency, and the U.S. Nuclear
Regulatory Commission. The environmental restoration process described below is
a generic approach based primarily on requirements of the Comprehensive
Environmental Response, Compensation, and Liability Act, as amended. Other
statutes that influence the process include the Resource Conservation and
Recovery Act, as amended, and the National Environmental Policy Act.
The Remediation Process
Initially, the Department characterizes a contaminated area to identify
contaminants, determine the extent of contamination, and assess potential
threats to public health and the environment. If a significant contamination
problem is indicated, and a fast and limited cleanup or containment action
could mitigate this problem, the Department may conduct an expedited response
action or interim action. To date, the Department has completed over 500 such
limited actions, avoiding larger contamination problems that could have
resulted from delay.
Upon completion of characterization, the Department performs a detailed
analysis to quantify existing risks and evaluate remedial alternatives. The
analysis is followed by a formal decision process, including public meetings
and a formal comment period. If the results of the analysis indicate that a
contaminated area does not pose a threat to public health or the environment,
or that a previously completed limited action adequately remediated the
contamination, the Department makes a decision to take "No Further Action," in
conjunction with the regulators, the U.S. Environmental Protection Agency, and
the host state. If, however, a threat is deemed to be present, the Department
identifies and implements the appropriate remedial action.
The Department of Energy reviews potential activities to determine how much
waste will be generated in the cleanup and makes provisions for its storage,
treatment, and/or disposal. If actual cleanup (for example, a removal action)
is not practical, or not required because of decisions regarding future land
use, the Department may take steps to stop or slow the spread of contamination
by implementing containment technologies. Actions depend on the contaminants
and the medium (for example, soil and ground water) in which they are found.
Contaminants such as hazardous organic chemicals or fuel oil are often highly
mobile but can be effectively removed from the media and destroyed. Heavy
metals and radioactive materials are often less mobile but cannot be destroyed,
even when it is possible to remove them from the media.
Radioactivity will decay naturally over time, but it can take from a few days
to tens of thousands of years to become less harmful. During this time, heavy
metal contaminated soils and radioactive waste that pose threats to public
health and the environment must be contained, stabilized, or moved to a safer
place. Containment structures associated with contamination that has not been
fully remediated or that has been stabilized in place must be continuously
monitored and maintained.
To date, the Department has completed 119 remedial action projects. Another 111
projects are under way. These projects have included cleanup of contaminated
soils, construction of ground-water treatment facilities, and retrieval of
buried waste. The Department is positioned to accomplish even more cleanup in
the near term as many characterization activities are complete or nearing
completion, and many formal cleanup decisions will be made over the next few
years.
The Decommissioning Process
Decommissioning of surplus facilities involves a decisionmaking process similar
to the process used for environmental remediation: characterization followed by
detailed analysis of alternatives and formal remedy selection. Based on a joint
policy between the Environmental Protection Agency and the Department of
Energy, provisions of the Comprehensive Environmental Response, Compensation,
and Liability Act generally govern decommissioning activities, which are
conducted as "non-time critical removal actions."
Decommissioning activities, which occur after facilities have been stabilized
and deactivated, address contamination that is already contained within
buildings. Building deterioration, however, may pose a substantial hazard to
surveillance and decommissioning workers, and the recurring costs associated
with maintaining surplus facilities absorb resources that could be better spent
on remediation. These issues raise important policy and planning questions.
Of the 3,500 contaminated facilities that are surplus, or projected to be
surplus within the next ten years, the Department has decommissioned 100
facilities to date. In spite of its modest beginnings, the program has placed a
priority on minimizing secondary waste and has recycled 7.24 million kilograms
(16 million pounds) of scrap metal from dismantled facilities and equipment.
2.2 WASTE MANAGEMENT
Mission
The Waste Management program's mission is to treat, store, and dispose of waste
generated during past and future Department of Energy activities. This includes
managing large volumes of "backlog" waste that currently exist at various
facilities throughout the United States. For example, at the end of 1995,
approximately 600,000 cubic meters (786,000 cubic yards) of radioactive waste
were stored in facilities at various Department of Energy installations.
Additional waste is expected from environmental restoration and nuclear
material and facility stabilization activities and from other ongoing
activities within the Department.
Based on definitions contained in regulations, waste is divided into categories
that include high-level, transuranic, mixed transuranic, low-level, low-level
mixed, uranium mill tailings, hazardous, sanitary, and special case waste. See
the following box for a brief description of each waste type. Because they have
specific requirements for treatment, storage, and disposal, each waste type
requires a different management strategy.
Strategies
Even more than environmental restoration processes, waste management strategies
depend on following detailed regulatory requirements. These include the
Resource Conservation and Recovery Act, as implemented through permits,
compliance agreements, and consent orders into which the Department has entered
with host states and the U.S. Environmental Protection Agency. For example, the
Federal Facility Compliance Act of 1992, which amended the Resource
Conservation and Recovery Act, waives sovereign immunity for all federal
agencies and specifically requires the Department to submit Site Treatment
Plans and enter into compliance agreements with the states specifying treatment
plans and schedules for mixed waste (including high-level, transuranic, and
low-level mixed waste). As a result of this Act, the Department has entered
into negotiated compliance orders between state regulators and/or the U.S.
Environmental Protection Agency for 29 states and is currently negotiating
orders for six sites.
High-Level Waste
Approximately 350,000 cubic meters (459,000 cubic yards) of high-level waste is
currently stored at four sites: Hanford Site, Idaho National Engineering
Laboratory, Savannah River Site, and West Valley Demonstration Project. The
Department has ended production operations involving special nuclear materials
and is phasing out chemical processing of spent nuclear fuel. As a result, the
Department does not expect large volumes of high-level waste to be generated in
the future. Small amounts, however, will be generated during nuclear material
and facility stabilization activities.
Two statutes provide the principal regulatory basis for high-level waste. The
Atomic Energy Act governs the radioactive constituents of high-level waste and
Subtitle C of the Resource Conservation and Recovery Act governs the hazardous
constituents. Based on regulatory requirements, liquid high-level waste must be
converted to a durable, stable, solid form for disposal. The preferred
treatment for most high-level waste is vitrification (that is, mixing liquid
high-level waste with glass frit and heating it to create glass that is
solidified inside steel canisters). A vitrification facility at the Savannah
River Site in South Carolina recently began operations, and a facility at the
West Valley Demonstration Project in western New York plans to begin operating
in 1996.
Presently, no disposal facility for high-level waste is available. The
Department will oversee the placement of high-level waste in a national
geologic repository developed by the Department of Energy's Office of Civilian
Radioactive Waste Management. This office currently plans to have a repository
available for high-level waste shipments by 2015. However, based on site
scheduling assumptions, this report assumes that a high-level waste repository
will be available to accept Department of Energy waste in approximately 2016.
| DESCRIPTIONS OF WASTE TYPES
High-level waste: highly radioactive material resulting from
reprocessing spent nuclear fuel and irradiated targets, including liquid waste
produced directly in reprocessing and any solid material derived from such
liquid waste that contains fission products in sufficient concentrations. Most
of the Department's high-level waste came from the production of plutonium. A
smaller fraction is related to recovering enriched uranium from naval reactor
fuel. This waste typically contains highly radioactive, short-lived fission
products as well as long-lived isotopes, hazardous chemicals, and heavy metals.
It must be isolated from the environment for thousands of years. Liquid
high-level waste is typically stored in large tanks, while waste in powdered
form is stored in bins. All high-level waste is managed as mixed waste.
Transuranic and mixed transuranic waste: waste generated during nuclear
weapons production, fuel reprocessing, and other activities involving
long-lived transuranic elements. It contains plutonium, americium, and other
elements with atomic numbers higher than that of uranium. Some of these
isotopes have half-lives of tens of thousands of years, and therefore require
long-term isolation. Since 1970, transuranic waste has been stored temporarily
in drums at sites throughout the complex. Mixed transuranic waste contains both
radioactive and hazardous waste.
Low-level waste: any radioactive waste that is not classified as
high-level waste, transuranic waste, spent nuclear fuel or byproduct tailings
containing uranium or thorium from processed ore. It is produced by every
process involving radioactive materials. Low-level waste has a wide range of
characteristics, but most of it contains small amounts of radioactivity in
large volumes of materials. Some waste in this category (for example,
irradiated metal parts from reactors) can have more radioactivity per unit
volume than the average high-level waste from nuclear weapons production. Most
low-level waste has been buried in shallow trenches. A limited inventory
remains stored in boxes and drums.
Low-level mixed waste: low-level radioactive waste that also contains
hazardous waste. A significant portion of the Department's mixed waste is
low-level mixed waste.
Uranium mill tailings: large volumes of material left from uranium
mining and milling. While this material is not categorized as waste, tailings
are of concern because they emit radon and because they are usually
contaminated with toxic heavy metals, including lead, vanadium, and molybdenum.
Hazardous waste: waste that is regulated under Subtitle C of the
Resource Conservation and Recovery Act. It contains hazardous constituents but
no radionuclides. Hazardous waste is generated at most Department of Energy
installations in a variety of quantities and forms (for example, laboratory
solutions, acids, bases, and degreasing agents).
Sanitary waste: waste that includes solid sanitary waste (for example,
garbage, rubble, or debris) regulated under Subtitle D of the Resource
Conservation and Recovery Act and liquid sanitary waste regulated under the
Clean Water Act.
Special case waste: waste that is not high-level or transuranic, but
requires greater confinement than shallow land burial.
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Transuranic and Mixed Transuranic Waste
Pending the availability of a geologic repository, many sites store transuranic
waste, including the Hanford Site, Idaho National Engineering Laboratory, Los
Alamos National Laboratory, Nevada Test Site, Oak Ridge Reservation, Rocky
Flats Environmental Technology Site, and Savannah River Site. Storage
facilities for transuranic waste are upgraded or built to comply with
requirements under Subtitle C of the Resource Conservation and Recovery Act.
Before 1970, this waste was buried in shallow trenches, mostly at the Idaho
National Engineering Laboratory and the Hanford Site. Some burial site
retrieval actions are now determined by the Environmental Restoration program
through a process that is specified by the Comprehensive Environmental
Response, Compensation, and Liability Act.
Treatment of mixed transuranic waste (radioactive and hazardous) to remove, or
reduce to acceptable levels, the constituents in the waste restricted by land
disposal restrictions, may be required under the Resource Conservation and
Recovery Act. Mixed transuranic waste treatment requirements are being assessed
as part of the Waste Isolation Pilot Plant test phase. The Waste Isolation
Pilot Plant is a deep geologic repository that the Department excavated in the
1980s for disposal of transuranic waste. The Plant is located in a salt bed 640
meters (2,100 feet) below the surface in southern New Mexico. The Department
plans to use this facility to dispose of transuranic waste beginning in 1998,
pending completion of regulatory compliance demonstrations.
Low-Level Waste
Low-level waste ranges from low-activity waste that can be disposed of by
shallow land disposal techniques to high-activity waste that requires disposal
techniques providing greater confinement. Over 30 installations currently
generate low-level waste. The Hanford Site, Idaho National Engineering
Laboratory, Los Alamos National Laboratory, Nevada Test Site, Oak Ridge
Reservation, and Savannah River Site store low-level waste on a long-term
basis.
Low-level waste generally undergoes minimum treatment (that is, volume
reduction, solidification of liquids, and packaging) before transportation and
disposal. Low-level waste storage is kept to a minimum because disposal
operations are ongoing at six installations. Waste radioactivity levels
(low-level waste can have high or low levels of radioactivity) and
geohydrological conditions influence disposal methods (for example, shallow
land burial or engineered vaults).
In response to a recommendation from the Defense Facilities Nuclear Safety
Board, the Department is taking steps to integrate low-level waste management
and determine the future disposal configuration.
Low-Level Mixed Waste
Until the late 1980s, most low-level mixed waste was routinely disposed of by
shallow land burial. However, enactment of the Resource Conservation and
Recovery Act limited land disposal of low-level mixed waste, which is subject
to land disposal restrictions, unless treatment standards are met or a variance
is granted. As a result, the Department currently plans to treat most low-level
mixed waste at Department of Energy sites.
Treatment strategies for low-level mixed waste have been developed through
interactions between the Department, states, and stakeholders. Disposal
locations will be determined in conjunction with the Waste Management
Programmatic Environmental Impact Statement; site-specific Environmental Impact
Statements; state regulators; and local stakeholders. For purposes of this
analysis, the Department assumed that mixed low-level waste will be disposed of
at the existing low-level waste sites: Hanford Site, Idaho National Engineering
Laboratory, Los Alamos National Laboratory, Nevada Test Site, Oak Ridge
Reservation, Savannah River Site, and commercial facilities.
Hazardous Waste
Hazardous waste includes materials identified as hazardous or requiring
regulatory control as stipulated by Subtitle C of the Resource Conservation and
Recovery Act. For purposes of this report, the definition of hazarious waste
includes Toxic Substances Control Act-regulated material, such as asbestos and
polychlorinated biphenyls. Land disposal restrictions under the Resource
Conservation and Recovery Act require treatment of the hazardous constituents
of waste to specific concentration levels before disposal. These regulations
are implemented by the states and the Environmental Protection Agency regions
and apply to local Department of Energy operations. All waste management
facilities must meet stringent waste acceptance criteria.
In general, hazardous waste generated by the Environmental Management program
is sent to commercial treatment and disposal facilities. Permitted commercial
facilities manage approximately 10,000 cubic meters (13,100 cubic yards) of the
Department's hazardous waste annually. Small amounts of hazardous waste await
treatment and disposal, except for waste being accumulated for shipment to
commercial facilities.
Sanitary Waste
Sanitary waste includes materials that are not hazardous or radioactive.
There are essentially two types of sanitary waste: solid and liquid. Solid
sanitary waste includes garbage, rubble, and other nonhazardous debris
routinely generated by construction or other activities. It is regulated under
Subtitle D of the Resource Conservation and Recovery Act and is typically
disposed of in onsite sanitary landfills or shipped offsite to municipal
landfills. Liquid sanitary waste includes sewage and industrial wastewater that
is regulated by the Clean Water Act and the National Pollutant Discharge
Elimination System. Treatment of liquid sanitary waste is usually accomplished
at onsite or municipally-owned facilities. Industrial wastewater undergoes
pretreatment processes before being discharged.
Special Case Waste
Special case waste is waste that is not high-level or transuranic, but
requires greater confinement than shallow land burial. This waste is similar to
Greater-Than-Class C waste regulated by the Nuclear Regulatory Commission. Only
a few sites contain special case waste. These sites include the Hanford Site,
Idaho National Engineering Laboratory and Grand Junction Projects Office. A
decision has not been made regarding disposal of special case waste. However,
the Department is considering several disposal options, including disposal
onsite and in a national repository.
Spent Nuclear Fuel
Spent nuclear fuel is not regulated as a waste material. It consists of nuclear
materials or heavy metals such as uranium, plutonium, or thorium withdrawn from
a nuclear reactor or another neutron irradiation facility. Spent nuclear fuel
exists primarily in solid form as metal-clad rods that require no treatment for
near-term storage. However, broken or punctured rods must be overpacked to
contain the radioactive material. Most spent fuel is stored in water pools (for
example, at Hanford Site, Idaho National Engineering Laboratory, and Savannah
River Site). This traditional storage method requires constant maintenance,
such as water purification, to prevent corrosion of the fuel rods. Some spent
fuel is stored in dry casks (for example, at Oak Ridge Reservation). The
Department is developing dry above-ground facilities to provide safer and more
efficient storage. Some treatment of spent nuclear fuel may be required before
final disposal in a geologic repository. Until a repository is available, the
Department will provide for the management of spent nuclear fuel and related
facilities, including interim activities necessary to ensure safe storage.
Spent nuclear fuel includes all nuclear fuel generated by Department of
Energy production reactors, university and government research reactors,
foreign research reactors that use fuel of U.S. origin, and naval nuclear
propulsion reactors (including training, prototype, and service reactors).
Except for a few special cases (for example, Three Mile Island), the
Environmental Management program is not responsible for managing spent nuclear
fuel from commercial reactors.
In January 1996, the Environmental Management program transferred management of
spent nuclear fuel from the Waste Management program to the Nuclear Material
and Facility Stabilization program. This shift occurred because spent nuclear
fuel is closely related to the special nuclear materials already managed by the
Nuclear Material and Facility Stabilization program. For purposes of the 1996
Baseline Report, spent nuclear fuel is included in the Waste Management
program's cost estimates and functional element discussion. Future reports will
address spent nuclear fuel with the Nuclear Material and Facility Stabilization
program.
| WASTE MINIMIZATION AND POLLUTION PREVENTION
The Department of Energy has instituted a waste minimization program,
administered by the Environmental Management program, at all of its facilities.
Waste minimization and pollution prevention means preventing or reducing the
generation of pollutants, contaminants, hazardous substances, or waste at its
source or reducing the amount of waste requiring treatment, storage, and/or
disposal through recycling. These objectives are achievable by administrative
and procedural changes, design features incorporated into new facilities,
modifications to existing facilities, increased use of existing technologies,
and expanded technology development efforts. For example, wastewater treatment
has been improved by replacing antiquated equipment and processes and site-wide
programs have begun to recycle materials such as aluminum, paper, lead, oil,
tires, and excess chemicals. Chapter 4 and Appendix G provide additional
information on the Department's pollution prevention program and the results of
an analysis of pollution prevention efforts on the Base Case estimate.
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2.3 NUCLEAR MATERIAL AND FACILITY STABILIZATION
Mission
The mission of the Nuclear Material and Facility Stabilization program consists
of three primary elements: stabilizing and storing nuclear materials prior to
final disposition, deactivating surplus facilities, and managing spent nuclear
fuel treatment and storage. Integral within each element is a surveillance and
maintenance function. Surveillance and maintenance encompasses all actions
required to ensure that adequate material and facility safety and security
requirements are met.
The program is responsible for a large number of geographically dispersed sites
and facilities; large quantities of radioactive, hazardous, and toxic materials
in a variety of chemical and physical forms and storage configurations; and an
aging complex of processing and production facilities historically used for
chemical and physical processing of many different types of nuclear material.
The following summary of major facilities and materials that are under the
purview of the Nuclear Material and Facility Stabilization program illustrates
the breadth and complexity of the program's mission:
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13 nuclear reactors;
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41 radioactive processing facilities;
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approximately 3,000 surplus buildings contaminated with and generally
containing radioactive, hazardous, and toxic materials;
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39 million liters (10.1 million gallons) of acids containing radioactive
contaminants;
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nearly 3,000 metric tons (3,300 tons)of spent nuclear fuel;
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several thousand kilograms of plutonium in various forms and locations;
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37,000 packages of plutonium materials and related waste products;
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75 million curies of cesium and strontium; and
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a large inventory of nuclear materials awaiting long-term storage and final
disposition decisions.
Strategy
Nuclear material and facility stabilization activities manage and mitigate many
of the urgent risks facing the Department. These risks are associated with a
wide variety of materials and facilities, including various forms of plutonium,
uranium and spent fuel; high-activity cesium capsules; aging facilities;
hazardous chemicals; and special isotopes. The broad scope and potential
impacts on the public and workers associated with these risks reinforce the
need for risk-based planning to address the risks posed by the material and
facilities.
Nuclear material and facility stabilization activities are also instrumental in
reducing the overall scope of materials and facilities that the Environmental
Management program must address. Because many special nuclear materials and
surplus facilities require significant resource expenditures for maintenance in
a safe and secure condition, the program's stabilization, consolidation, and
material removal activities are essential to reduce the need for major facility
systems and to reduce security perimeters (and other surveillance and
maintenance requirements). These actions significantly decrease the annual cost
required to maintain materials and facilities in a safe and secure manner,
thereby reducing the estimated life-cycle cost of the Environmental Management
program.
Nuclear Material Stabilization
The end of the Cold War resulted in an abrupt halt to nuclear material
production facilities and reactor operations, leaving nuclear material in a
variety of chemical and physical forms, packaging configurations, and
geographical locations. Stabilization activities reduce near-term risks
associated with current storage configurations by placing these materials in a
condition that is suitable for long-term storage. The principal materials of
concern include plutonium (solutions, metals, oxides, and residues), uranium
(solutions, solids, and gaseous compounds) and special isotopes (americium,
curium, neptunium, and plutonium-242). In some cases, stabilization also
involves long-term storage of nuclear materials prior to their ultimate
disposition.
Facility Deactivation
Upon completion of stabilization activities, the Department undertakes
deactivation activities to remove materials, shut down facility systems, and
remove or de-energize equipment. Deactivation activities reduce physical risks
and hazards to the public, workers, and the environment by placing surplus
facilities in a safe, stable condition. Once hazards associated with surplus
facilities are mitigated, costs for maintaining the facilities can be
significantly reduced.
2.4 SCIENCE AND TECHNOLOGY DEVELOPMENT
Mission
Developing new technologies to address the environmental challenges in the
former nuclear weapons complex is an integral part of the Environmental
Management program. The mission of the technology development program is to
develop new technologies that will allow the Department to reduce risks to
people and the environment, reduce cleanup costs, and address environmental
problems for which no solutions currently exist.
The Department has targeted five major remediation and waste management "focus
areas" for action on the basis of risk, prevalence, or environmental
requirements and regulations. (See the following box). The focus area strategy
is to identify and develop specific technologies to clean up the nuclear
weapons complex and manage waste more quickly, more safely, and at a lower
cost, using the best capabilities available in industry, academia, and
Department laboratories. Focus area management teams include stakeholders and
representatives from across the Environmental Management program.
| TECHNOLOGY DEVELOPMENT FOCUS AREAS
Treat and Dispose of Mixed Waste. The Department is pursuing versatile
treatment methods such as plasma, vitrification, molten metal, and nonthermal
techniques. These activities are being coordinated closely with waste
management activities to meet Federal Facility Compliance Act requirements.
Retrieve and Process Tank Waste. The Department is initiating full-scale
demonstrations of technology systems to retrieve and process high-level tank
waste for permanent disposal safely and efficiently. The Department is also
developing tank structural analysis and waste content analysis methods.
Remediate Contaminated Soils and Ground Water. The Department has
initiated full-scale demonstrations of technology systems to characterize,
contain, and remediate contaminated plumes in soils and ground water. In-place
treatment of dense nonaqueous phase liquids is an example of activities in this
area.
Stabilize Landfills. Containment and in-place treatment methods for
buried waste are being developed. The Department is also pursuing technology
systems for retrieving, characterizing, and treating landfill waste.
Stabilize, Decontaminate, and Decommission Facilities. The Department
will conduct a full-scale demonstration of the development of facility
stabilization and decommissioning technologies that emphasize materials
recycling.
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In 1996, the Department initiated an Environmental Management Science program
to develop a targeted long-term basic research agenda for environmental
problems. One of the goals of the program is to ensure that "transformational"
or breakthrough approaches lead to significantly reduced cleanup costs and
risks to workers and the public. The program will "bridge the gap" between
broad fundamental research performed in the Department of Energy's Office of
Energy Research, and needs-driven applied technology development historically
conducted by the Environmental Management program. This effort will stimulate
the nation's science infrastructure to focus on critical national environmental
management problems. Also included in the Office of Science and Technology is
the Risk Policy program. The goal of this program is to conduct and integrate
risk management and analysis activities into the Environmental Management
decisionmaking process.
2.5 LANDLORD FUNCTIONS
In addition to the four major functional areas discussed above, the
Environmental Management program must perform landlord (infrastructure support)
activities that are both directly and indirectly related to its mission.
Landlord functions include cross-cutting, site-wide activities such as managing
electrical systems, laboratory support, road maintenance and upgrades, fire
protection, quality assurance, safety and environmental monitoring, sanitary
sewer systems, laundry services (for contaminated clothing and other
materials), utilities, roadways, and security reviews. Landlord functions are
required to keep communication, transportation, and security systems
operational at environmental management sites and, in many cases, to meet
environmental regulatory requirements.
Some of the sites under the purview of the Environmental Management program
cover hundreds of miles of land, and contain hundreds of buildings and
facilities. For example, the 1,450-square kilometer (560-square mile) Hanford
Site in Washington State has its own fire department, security force, and
medical center. The program maintains a utility infrastructure at Hanford that
provides steam and sewage treatment, maintains grounds and roads, and provides
onsite mass transit.
In some instances, the Environmental Management program has landlord
responsibilities for entire sites. In general, infrastructure-related costs are
typical at large sites where the majority of program costs are incurred. For
example, Hanford Site, Idaho National Engineering Laboratory, Oak Ridge K-25
Site, Rocky Flats Environmental Technology Site, and the Savannah River Site
have large landlord programs.
2.6 NATIONAL PROGRAM PLANNING AND MANAGEMENT
In addition to its presence at Department of Energy sites, the Environmental
Management program performs several functions at Headquarters. These functions
are primarily focused on planning, management, and oversight. Specific roles of
Headquarters personnel include establishing policy and conducting program
reviews to ensure adherence to policy; preparing program-wide budgets based
upon field input; coordinating with Congress and other federal agencies;
coordinating with national stakeholder organizations; managing national
initiatives; overseeing site safety programs; establishing and tracking program
performance measures; preparing national reports; and developing program
strategic plans.
Construction of the first high-level waste tanks at Hanford
Site, Washington, 1944. Designed for a useful life of 25 years, these
tanks contain intensely radioactive acids and solvents resulting from
reprocessing spent nuclear reactor fuel elements to extract plutonium and
uranium. Approximately half of the 177 tanks were a "single shell", such as
these, while others were "double shell" tanks. Because workers during the Cold
War typically filled the tanks without sampling the waste and without
recordkeeping that would meet today's standards, the Department is now
undertaking a complex and hazardous effort to characterize the waste already in
the tanks.
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Installing a mixing pump in tank 101-SY at Hanford Site,
Washington, 1993. This custom-built pump was critical in controlling the
buildup of explosive gases in the tank, which was identified as one of the most
urgent safety risks in the former nuclear weapons complex at the time. The
ongoing cost for simply averting serious safety problems in these tanks is
approximately $300 million per year. Beyond this routine safety operation, the
Department is planning to remove the waste from the tank, which is the focus of
a top-priority multibillion dollar, multidecade effort. The cost and complexity
of dealing with these tanks provides excellent examples of the benefits of
life-cycle planning and cost estimation. Characterizing the waste and treating
it for disposal, after many years of storage, is significantly more expensive,
complex, and hazardous than if the work was done as part of the production
process.
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-8-
Appendix -A2- / -B- /
-C- / -D- / -E1-
/ -E2- / -F- /
-G- / -H-
/ Glossary
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