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Sandia National Laboratories/New Mexico is located in Bernalillo County, 10.4
kilometers (6.5 miles) east of downtown Albuquerque. The laboratories consist
of five technical areas and several remote areas covering 1,128 hectares (2,820
acres) in the eastern half of the 306.8-square kilometer (118-square mile)
Kirtland Air Force Base. The base has a mean elevation of 1,642 meters (5,385
feet). It is situated on two broad mesas bisected by the Tijeras Arroyo and
bound by the Manzano Mountains to the east and the Rio Grande to the west.
LOCALITY MAP
Estimated Site Total
| (Thousands of Current Year Dollars)
|
| |
|
|
|
| Nuclear Material and Facility Stabilization
|
|
|
|
|
|
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.
|
| Environmental Restoration
|
27,132
|
18,038
|
17,664
|
16,929
|
15,127
|
|
| Waste Management
|
14,848
|
13,252
|
9,688
|
9,685
|
9,644
|
|
| Total |
41,980
|
31,290
|
27,352
|
26,613
|
24,771
|
|
| 1996 Appropriation
|
45,905
|
|
|
These levels reflect the current estimates for
compliance with applicable statutes and agreements (as of March 1996), see
Readers' Guide.
|
| 1997 Congressional Request
|
|
33,091
|
|
|
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
|
| Nuclear Material and Facility Stabilization
|
|
4,241
|
2,934
|
1,355
|
569
|
|
|
|
| Environmental Restoration
|
18,045
|
25,000
|
|
831
|
2,359
|
|
|
|
| Waste Management
|
10,856
|
16,117
|
18,413
|
17,934
|
19,636
|
18,227
|
17,934
|
|
| Total |
28,901
|
45,359
|
21,346
|
20,120
|
22,563
|
18,227
|
17,934
|
|
| |
|
| Nuclear Material and Facility Stabilization
|
|
|
|
|
|
|
|
|
| Environmental Restoration
|
|
|
|
|
|
|
|
|
| Waste Management
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
|
| Total |
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
|
| |
2075
|
2080
|
2085
|
2090
|
2095
|
2100
|
| Nuclear Material and Facility Stabilization
|
|
|
|
|
|
|
|
45,493
|
| Environmental Restoration
|
|
|
|
|
|
|
|
231,178
|
| Waste Management
|
18,227
|
|
|
|
|
|
|
1,314,403
|
| Total |
18,227
|
|
|
|
|
|
|
1,591,074
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
FACILITY MISSION
Sandia National Laboratories, which is part of the Department of Energy' s
national laboratory complex, was established in the 1940s as the engineering
arm of the nuclear weapon development program. In 1945, it represented a small
part of Los Alamos Laboratory, called Z-Division, providing technical support
to the U.S. Army. Sandia also operates a test range on the island of Kauai,
Hawaii.
SITE MAP
Sandia/New Mexico has evolved into one of the country's largest technical
resources. It is a multiprogram national laboratory with research and
development programs in a broad range of scientific and technical fields,
including fundamental energy research, energy conservation and renewable
energy, nuclear reactor safety and reliability, nuclear waste management, and
magnetic-confinement fusion. Recent mission changes have resulted in a decline
in weapons research and development and an increase in work on nuclear
safeguards and security, environmental sciences, biomedical systems
engineering, advanced manufacturing technology, electronics, information and
computational technology, transportation infrastructure and energy technology,
and technology transfer to private industry in support of U.S. industrial
competitiveness. New activities include the Medical Isotope Production Program
and the Neutron Generator Production Facility.
The Office of Defense Programs is the landlord of Sandia National
Laboratories/New Mexico and is expected to continue to use the property in
support of its missions. The Environmental Restoration program is responsible
for assessing and remediating environmental contamination at Sandia that has
occurred from a wide variety of past or historical activities. All treatment,
storage, and disposal costs are included with Environmental Restoration program
estimates. Sandia's Waste Management Program conducts fully functioning waste
operations for hazardous, radioactive, and mixed waste in support of
Environmental Management and Office of Defense Programs activities.
FUTURE USE
Sandia assumes its mission will continue for the foreseeable future and current
institutional controls will remain in place. Therefore, the Future Land-Use
Working Group, in collaboration with all major stakeholders (U.S. Air Force,
U.S. Forest Service, regulatory authorities, and the Citizens Advisory Board),
has proposed future land-use designations for Sandia be Industrial for high
density building/worker areas and Recreational for more remote areas. These
designations are being used to establish risk-based cleanup standards and do
not necessarily reflect actual current usage (e.g., Recreational use does not
mean the land is presently available to the public. It means that it could
reasonably be made available for such use in the future). If land uses are
significantly changed, it may be necessary for the Federal Government to
include deed restrictions for certain sites if they do not meet acceptable
risk-based standards for the proposed use(s).
FUTURE USE MAP
NUCLEAR MATERIAL AND FACILITY STABILIZATION
The facility stabilization and maintenance process began at the Sandia National
Laboratories in 1995. The Office of Defense Programs provides current funding
for stabilization and maintenance. This report assumes that facilities will be
transferred to the Environmental Management program in FY 2002. Twelve Sandia
facilities are currently slated to undergo this process. Eleven facilities,
including laboratories and storage facilities, have already begun
stabilization. This report assumes the remaining facility, which is a
corrugated burn structure, will begin stabilization and maintenance activities
in FY 1996 and the cost is not included in this estimate. The Department
expects the resulting waste types will include hazardous, transuranic,
low-level, and low-level mixed waste. All waste generated by the Nuclear
Material and Facility Stabilization program will be managed by the Waste
Management program, and costs for treatment, storage, and disposal are included
in the Waste Management section of this site narrative. This report assumes the
stabilization and maintenance process at Sandia will be completed by FY 2018.
Funding profiles and facility activities were generated through parametric
modeling, using data from other Department of Energy facilities.
Nuclear Material and Facility Stabilization Activities Cost Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
FY 1996-2000
|
2025
|
2030
|
| Nuclear Material and Facility Stabilization
|
|
4,241
|
2,934
|
1,355
|
569
|
|
|
45,493
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
ENVIRONMENTAL RESTORATION
The Environmental Restoration program is responsible for assessing and cleaning
up environmental contamination at Sandia that has occurred from a wide variety
of historical activities. The principal contamination sources include firings
conducted over many years to test weapons and weapons components; discharges of
radioactive liquids and hazardous chemicals; oil spills; disposal of
radioactive waste and hazardous chemicals in landfills; rocket launches; and
burning of certain wastes, such as high explosives. The wide range of
contaminated facilities includes reactors, artillery ranges, and scrap yards.
Based on current knowledge, these contaminated or potentially contaminated
sites identified for assessment and possible remediation pose no known
immediate threat to either workers or the local public. See the site map for
environmental restoration activity locations. See the Site Map for
Environmental Restoration program activity locations.
Environmental restoration activities at Sandia began formally in 1984. The
Department identified 117 sites with potential contamination. The U.S.
Environmental Protection Agency conducted a similar investigation in 1987.
These programs ultimately defined a working inventory of potential "solid waste
management units" that are included in Sandia's Part B operating permit issued
by the Environmental Protection Agency under the Hazardous and Solid Waste
Amendments of the Resource Conservation and Recovery Act. The Region VI Office
of the Environmental Protection Agency presently regulates the Sandia
Environmental Restoration Project. This report expects Hazardous and Solid
Waste Amendments authority will be granted to the Environment Department of the
State of New Mexico in FY 1996.
Current investigations are intended to determine the nature and extent of
hazardous and radioactive contamination and to restore sites where such
contamination poses a threat to human health or the environment. During
FY 1995, Sandia submitted 65 sites for Proposed No Further Action
status, had 13 No Further Actions approved as modifications to the Resource
Conservation and Recovery Act Part B permit, and
conducted 37 voluntary corrective measures. A number of new potential release
sites have been identified, including 20 septic systems that are being added to
Sandia's Part B permit.
The cost estimate still assumes 41 sites will be remediated following the full
corrective measures process. It also assumes all other sites require No Further
Action or they can be remediated using the voluntary-corrective-measures
process. All costs associated with treating, storing, and disposing of waste
generated by environmental restoration activities are included in the remedial
action estimates.
The primary treatment, storage, and disposal strategy at Sandia includes
establishing a Temporary Unit (permitted by the Environmental Protection
Agency) in FY 1996 for storing hazardous waste for up to one year, followed by
a Corrective Action Management Unit (also permitted by the Environmental
Protection Agency).
For hazardous waste at excavated sites, which this report assumes to be all but
the mixed waste landfill and certain vadose zone plumes, activities will
include site preparation (clearing and grubbing), followed by excavation and
landfill disposal. Toxic metals will be immobilized prior to landfill disposal
in the permitted Corrective Action Management Unit.
For radionuclides and metals, activities will include site preparation,
followed by excavation. Soil washing to remove metals and reduce volumes will
be performed when practicable before landfill disposal, which this report
assumes will be done at the Nevada Test Site.
For mixed radionuclides and organics or radionuclides with metals and organics,
activities will include site preparation, followed by excavation. The waste
will be treated, using low-temperature thermal desorption and soil washing
(when practicable), and then disposed as hazardous waste in the onsite
Corrective Action Management Unit or as low-level waste at the Nevada Test
Site.
The Department plans to dispose of treatment concentrate residues offsite in
commercial disposal facilities. It will dispose of "clean" nonregulated
residues onsite, probably as fill material. It will ship low-level radioactive
waste offsite to the Nevada Test Site or to an approved commercial facility.
Other waste, such as polychlorinated biphenyls, will be treated and disposed
offsite.
During FY 1995, Sandia implemented a site-based Environmental Restoration
program, effectively eliminating artificial geographic segregations of sites
into operable units. Consequently, Sandia no longer uses any geographic
subgroupings. However, to maintain consistency with last year's report, this
report delineates cost by operable unit.
Major Environmental Restoration Activity Milestones
| North Technical Area Landfill Corrective Measure
|
1997
|
|
Firing Range Remediation
|
2001
|
|
Thunder Range Remediation
|
2003
|
|
South Technical Area Remediation
|
2005
|
North Technical Areas
ASSESSMENT
The North Technical Areas include Technical Areas I and II and seven buildings
that require decommissioning. Technical Area I, which contains office buildings
and laboratories and houses most of Sandia's staff, has been in existence since
1945. It contains 15 environmental restoration sites, including a motor pool, a
tank farm, a waste oil tank, a reclamation yard, a wastewater treatment plant,
an acid-waste sewer line, and miles of sanitary sewer lines. Potential
contaminants include petroleum hydrocarbons, polychlorinated biphenyls, heavy
metals, radionuclides, and organic compounds. Initial soil sampling indicates
contaminants such as petroleum-fuel hydrocarbons and heavy metals are
restricted to the soils above the water table. The depth to ground water is
approximately 146 meters (480 feet).
Technical Area II is an active 17-hectare (43-acre) explosives testing
facility. Potential sources of contamination include a chemical disposal pit, a
radioactive waste landfill, a classified waste landfill, seven septic systems,
a storage yard for radioactive materials, a decommissioning site, uranium
calibration pits, firing sites, and an explosives burn pit. Sampling to date
indicates contamination with volatile and semivolatile organic compounds, high
explosive compounds, polychlorinated biphenyls, and radionuclides.
Contamination is mainly confined to the surface soils, but trace
trichloroethylene (a chlorinated solvent) was found recently in perched ground
water. The contamination is well below risk-based action levels, but bears
additional evaluation to identify its source. The depth to ground water is
approximately 91.5 meters (300 feet).
The Department has conducted preliminary site characterization in both
Technical Areas. In FY 1995, assessment activities focused on completing
characterization (including surface and subsurface geophysical and
environmental investigations); conducting voluntary corrective measures at
Buildings 838 and 839 in Technical Area I and at site 114 in Technical Area II,
and carrying out remediation activities.
The Department will use the one-pass voluntary corrective measure approach to
assess and remediate the remaining sites. In this approach, assessment work
will be limited to sampling in sufficient detail to allow safe remediation.
When necessary, corrective measures will be implemented in concert with the
limited assessment activities. At the conclusion of the combined
assessment/remediation process, verification samples will be taken to ensure
cleanup objectives have been achieved. The Department will then submit a
modified Resource Conservation and Recovery Act Facility Investigation report
that includes voluntary corrective measure results and verification sampling
data to the regulatory authorities, with a request for No Further Action (Class
III Permit Modification).
Eighteen sites will be assessed in 1996. If contaminants are found to be below
levels of regulatory concern, the Department will submit a request for approval
of No Further Action. One landfill will undergo a voluntary corrective measure
that will start in FY 1996 and conclude in FY 1997.
In FY 1995, remediation activities included completing voluntary corrective
measures at Buildings 838 and 839 in Technical Area I and at site 114 in
Technical Area II, and carrying out remediation activities. As described above,
the one-pass assessment and corrective action approach will be implemented for
the 18 remaining sites.
Several buildings and structures have been identified as posing potential,
though not immediate, risk to human health and the environment (e.g., Building
863 in Technical Area I and Buildings 901, 906, 907, 919, 935, and 940 in
Technical Area II). Although the Department will eventually need to
decommission these buildings, current Department of Energy/Environmental
Management funding levels have precluded quantifying the total scope of
stabilization and deactivation.
The estimate assumes Environmental Management program activities in this area
will generate 30 cubic meters (39 cubic yards) of low-level waste, 54 cubic (71
cubic yards) of low-level mixed waste and 5,784 cubic meters (7,565 cubic
yards) of hazardous waste.
South Technical Areas
South Technical Areas include Technical Areas III and V, the chemical waste
landfill, the mixed waste landfill, and the liquid waste disposal system. The
Department has used technical Areas III and V, which consist of about 770
hectares (1,920 acres), to test nuclear and nonnuclear weapons components since
1953. These areas contain 20 active and inactive environmental restoration
sites, including burial sites, oil spills, sump and drain releases, two rocket
sled tracks, storage and salvage yards, and a gas cylinder disposal pit.
Contamination, which includes volatile organic contaminants, semivolatile
organic contaminants, metals, high explosive compounds, polychlorinated
biphenyls, and radionuclides, is mainly restricted to the soils above the water
table.
At the chemical waste landfill, which covers about 0.76 hectares (1.9 acres),
approximately 15,300 cubic meters (20,000 cubic feet) of chemical and hazardous
waste was buried in unlined pits and trenches from 1962 to 1985. The depth to
ground water is approximately 152 meters (500 feet). Trichloroethylene has been
detected in ground water at very low levels, but at levels high enough to
warrant additional assessment and possible remedial action. Chromium has also
been detected, but it may be a natural constituent of the ground water. In FY
1995, a section of the chemical waste landfill was made available for an Office
of Technology Development pilot test for Thermally Enhanced Vapor Extraction
System technology. The test concluded near the end of FY 1995 and results are
still being analyzed.
At the mixed waste landfill, which consists about 1 hectare (2.6 acres),
approximately 2,800 cubic meters (3,700 cubic feet) of low-level radioactive
waste was buried in unlined pits and trenches from 1959 to 1988. The depth to
ground water is approximately 152 meters (500 feet). Contamination from
volatile organic compounds and tritium is restricted to the vadose zone
sediments above the water table.
Between 1963 and 1971, the liquid waste disposal system, which consists of a
below-grade drain field, three holding tanks, and two surface impoundments,
received liquid radioactive discharges from the Sandia Experimental Reactor
Facility. This reactor cooling water included short-lived radioactive elements
from activation products. Extensive sampling of ground water and soils at this
site shows the radiation level is not higher than that of the natural
background. At one of the surface impoundments, polychlorinated biphenyls are
present in sludge. Trichloroethylene has been found in ground water near the
liquid waste disposal system at levels slightly above detection limits.
The remaining sites will undergo assessment and remediation using the one-pass
voluntary corrective measure approach. Assessment work will be limited to
sampling in sufficient detail to allow safe remediation. When necessary,
corrective measures will be implemented in concert with the limited assessment
activities. At the conclusion of the combined assessment/remediation process,
verification samples will be taken to ensure that cleanup objectives have been
achieved. The Department will then submit a modified Resource Conservation and
Recovery Act Facility Investigation report that includes voluntary corrective
measure results and verification sampling data to the regulatory authorities,
with a request for No Further Action (Class III Permit Modification).
Depleted uranium, scattered along both rocket sled tracks, was removed from the
short sled track in October 1994 and the long sled track in early 1995. Also in
FY 1995, a voluntary corrective measure at the gas cylinder disposal pit
involved the removal of gas cylinders, thermal batteries, and various debris.
Future remediation activities in the South Technical Areas will include a
voluntary corrective measure at the chemical waste landfill beginning in mid-FY
1996 to remove the source terms for trichloroethylene and other possible
contaminants. This estimate assumes remediation activities in these areas will
be complete in FY 2005. The estimate also assumes Environmental Restoration
program activities will generate 10 cubic meters (13 cubic yards) of low-level
waste, 847 cubic meters (1,108 cubic yards) of low-level waste, and 34,585
cubic meters (45,234 cubic yards) of hazardous waste.
Firing Ranges
Sites of concern at the Firing Ranges include septic tanks and drain fields and
the Foothills, Canyons, and Central Coyote Test Areas. Twenty-three
environmental restoration sites have been identified for the 42 separate septic
and drainage systems scattered across the Sandia site. These systems were used
mainly for liquid and sanitary waste and are currently being evaluated for
chemical contamination. From 1958 to 1991, they received waters from facilities
conducting weapons components tests. Potential contaminants, most likely
restricted to the vadose zone sediments, include radionuclides, solvents, high
explosive compounds, metals, and photochemicals. The depth to ground water
varies from approximately 15 to 150 meters (50 to 500 feet). It is shallower
toward the mountains in the east.
The Foothills Test Area, which consists of 10 inactive environmental
restoration sites, has been used for field testing since the late 1950s. A wide
range of contaminants, including organic compounds, metals, high explosive
materials, and radionuclides may be present. The depth to ground water across
the area probably varies from 15 to 30 meters (50 to 100 feet).
The Canyons Test Area consists of 14 environmental restoration sites (9 active,
5 inactive) and 4 proposed sites at scattered locations within three large
canyons in the Manzanita Mountains at the eastern end of the Kirtland Air Force
Base, on land withdrawn from the U.S. Forest Service. Potential sources of
contaminants include burn sites, rocket-launch sites, dumps, and a surface
impoundment. Principal contaminants include depleted uranium, metals, jet fuel,
and other organic compounds. The depth to ground water is estimated to vary
across the area from 15 to 30 meters (50 to 100 feet).
The Central Coyote Test Area contains 14 inactive sites that include six test
sites, two burn sites, an artillery range, a trash dump, a borrow pit, two
scrap yards, and an unstaffed seismic observatory. The principal contaminants
include residual high explosive compounds, metals (including depleted uranium),
jet fuel, other volatile organic compounds, and asbestos. The depth to ground
water across the area is estimated to vary from 15 to 30 (50 to 100 feet).
The Department will use the one-pass voluntary corrective measure approach to
assess and remediate the remaining sites. Assessment work will be limited to
sampling in sufficient detail to allow safe remediation. When necessary,
corrective measures will be implemented in concert with the limited assessment
activities. At the conclusion of the combined assessment/remediation process,
verification samples will be taken to ensure that cleanup objectives have been
achieved. A modified Resource Conservation and Recovery Act Facility
Investigation report that includes voluntary corrective measure results and
verification sampling data will then be submitted to the regulatory authorities
with a request for No Further Action (Class III Permit Modification).
Future remediation activities at the firing ranges will include voluntary
corrective measures and remediation. Voluntary corrective measures have been or
will be carried out at the following sites: septic tanks and drain fields;
sites 58 and 8, Building 9990, and the TRUPACT "boneyard" in the Foothills Test
Area (the "boneyard" is a storage area for the remnants of the TRUPACT
transportation casks for transuranic waste that were subjected to various
destructive tests); sites 10 and 60 in the Canyons Test Area; and sites 11, 47,
57B, 68, 21, and 22 in the Central Coyote Test Area. This report assumes
assessments for all areas will be complete in FY 2001 and remediation
activities will be complete in FY 2001. Activities are assumed to generate
3,968 cubic meters (5,200 cubic yards) of hazardous waste, 198 cubic meters
(260 cubic yards) of low-level mixed waste and 318 cubic meters (416 cubic
yards) of low-level waste.
Thunder Range
Thunder Range includes projects in the Tijeras Arroyo and the Southwest Test
Area. The Tijeras Arroyo has 17 environmental restoration sites (7 active, 10
inactive) distributed over several miles of the arroyo and its tributaries that
together drain thousands of hectares of the Kirtland Air Force Base and the
Sandia site. The main channel, which is approximately 30 meters (100 feet) deep
and 1.6 kilometers (1 mile) wide, empties into the Rio Grande River less than
3.2 kilometers (2 miles) from the Sandia site boundary. A wide range of
contaminants, including metals, radionuclides, and organic compounds may be
present in low concentrations. The depth to ground water is estimated to be
about 150 meters (500 feet).
The Southwest Test Area, which has been used for field testing explosives since
the 1960s, contains 24 environmental restoration sites (11 inactive, 13
active). A wide range of contaminants such as metals, high explosive compounds,
radionuclides, and organic compounds may be present. The depth to ground water
is approximately 150 meters (500 feet).
The Department has conducted preliminary site characterization. There are nine
No Further Action sites, and two voluntary corrective measures are planned to
be completed during FY 1996. The estimate assumes all assessments will be
completed in FY 2001 and remediation activities for all sites in this area will
be complete in FY 2003. This report also assumes Environmental Restoration
program activities will generate 35,288 cubic meters (46,153 cubic yards) of
low-level waste, 645 cubic meters (844 cubic yards) of low-level mixed waste
and 1,959 cubic meters (2,562 yards) of hazardous waste.
The Department will use the one-pass voluntary corrective measure approach to
assess and remediate the remaining sites. Assessment work will be limited to
sampling in sufficient detail to allow safe remediation. When necessary,
corrective measures will be implemented in concert with the limited assessment
activities. At the conclusion of the combined assessment/remediation process,
verification samples will be taken to ensure that cleanup objectives have been
achieved. A modified Resource Conservation and Recovery Act Facility
Investigation report that includes voluntary corrective measure results and
verification sampling data will then be submitted to the regulatory authorities
with a request for No Further Action (Class III Permit Modification).
Site-Wide Characterization
This project seeks to integrate regional, rather than site-specific, geologic
and hydrologic information into a sitewide hydrogeologic framework for all the
environmental restoration sites distributed across the Kirtland Air Force Base
and the Sandia site. This project does not include responsibility for
characterizing or remediating individual environmental restoration sites. The
resulting framework will be used as the primary basis on which to evaluate
site-specific information with respect to natural elemental background
concentrations and to complete risk assessments. The estimate assumes this
activity will be complete in 2001.
Temporary Unit/Corrective Action Management Unit
In late FY 1995, the Sandia Environmental Restoration Project added a new
baseline work scope for the permitting, design, construction, and operation of
a Temporary Unit, to be completed in FY 1996, for short-term storage of
waste generated by the Environmental Restoration Project, and a Corrective
Action Management Unit, scheduled to be operational in FY 1997 for long-term
management of Environmental Restoration waste, including treatment of hazardous
waste. The Corrective Action Management Unit will remain active until the
Environmental Restoration Project ends. At that time, if the resulting disposal
cells are built, they will be capped and the surface facilities will be
decommissioned. The Temporary Unit and Corrective Action Management Unit can
only be used for only hazardous waste generated by the Environmental
Restoration Project. The Temporary Unit permit is for one year only. After
that, if it is approved by the regulatory authority, it will be incorporated
into the Corrective Action Management Unit. This unit will close in FY 1996 and
there will be no long-term surveillance and monitoring activities associated
with the unit.
Offsite Areas
Pending approval of No Further Action requests, this estimate assumes no
additional work will be required by Environmental Management at Offsite Areas.
Stabilization, treatment, storage, disposal, and surveillance and monitoring
activities are not applicable to the Offsite Areas project.
Environmental restoration activities at the Tonopah Test Range have been
formally transferred to the Nevada Operations Office and costs for these
activities are included within the Nevada estimate. No further environmental
restoration activities are expected at the Kauai Test Range. However, waste
management activities associated with testing at these two sites are the
responsibility of Sandia.
The Kauai Test Facility is located on the western coast of the island of Kauai
in Hawaii within the Navy's Pacific Missile Range Facility. The 73-hectare
(182-acre) site is operated by Sandia National Laboratories/New Mexico and
supports Department of Energy research and development activities, including
rocket launches of nonnuclear payloads. The Kauai Test Facility has been in
operation since the mid-1970s, conducting an average of three or four tests per
year. The Department suspected contamination in three potential release sites
that include the rocket launch pads, a drum storage area, and a photography
laboratory. In 1994, the Department conducted soil and ground-water sampling to
determine the extent of contamination. Results proved below regulatory concern
and a No Further Action report was submitted to the regulators. Regulators have
verbally agreed to this approach and formal documentation is expected in the
near future. Therefore, this report does not anticipate any further work for
Kauai and includes no costs for further environmental restoration activities.
Salton Sea Test Base, located in Imperial County, California was used for
Atomic Energy Commission/Sandia National Laboratories test activity from the
mid-1940s through the early 1960s. Test activity in these years contributed to
environmental contamination at approximately 23 sites within Salton Sea Test
Base. The test base is a Comprehensive Environmental Resource Compensation and
Liability Act site and is the subject of accelerated base realignment and
closure activity to return properties to local communities. None of these sites
was determined to be related to activities undertaken by Sandia National
Laboratories; therefore, a request has been made to remove Sandia from the list
of potentially responsible parties.
The Sandia Offsite Areas also include one building at Holloman Air Force Base
in southern New Mexico where laboratory activities generated a variety of
waste. The Department plans to turn over this site to the U.S. Air Force for
any future action. Assessment activities are assumed to be complete in FY 1996.
Environmental Restoration Activities Cost Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
2025
|
2030
|
| Offsite - Holloman Air Force Base
|
|
|
|
|
|
|
|
|
| Assessment
|
14
|
|
|
|
|
|
|
71
|
| North Technical Areas
|
|
|
|
|
|
|
|
|
| Assessment
|
195
|
689
|
|
173
|
490
|
|
|
7,731
|
| Remedial Action
|
618
|
11,706
|
|
|
|
|
|
61,621
|
| Facility Decommissioning
|
828
|
122
|
|
575
|
1,633
|
|
|
15,791
|
| Sitewide Characterization
|
|
|
|
|
|
|
|
|
| Assessment
|
574
|
32
|
|
|
|
|
|
3,028
|
| South Technical Areas
|
|
|
|
|
|
|
|
|
| Assessment
|
1,022
|
|
|
|
|
|
|
5,111
|
| Remedial Action
|
1,088
|
5,492
|
|
|
|
|
|
32,897
|
| Thunder Range
|
|
|
|
|
|
|
|
|
| Assessment
|
432
|
18
|
|
|
|
|
|
2,247
|
| Remedial Action
|
674
|
188
|
|
|
|
|
|
4,310
|
| Firing Ranges
|
|
|
|
|
|
|
|
|
| Assessment
|
1,074
|
18
|
|
|
|
|
|
5,459
|
| Remedial Action
|
1,405
|
19
|
|
|
|
|
|
7,117
|
| Corrective Action Management Unit
|
2,295
|
2,657
|
|
|
|
|
|
24,758
|
| Long-Term Surveil. and Monitoring
|
328
|
7
|
|
|
|
|
|
1,677
|
| Direct Program Management/Support
|
7,499
|
4,054
|
|
83
|
236
|
|
|
59,360
|
| Total |
18,045
|
25,000
|
|
831
|
2,359
|
|
|
231,178
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
Current plans call for implementing surveillance and monitoring activities at
sites where potential for future contaminant migration to the water table
cannot be dismissed or mitigated. Examples include historic landfills that are
capped and sites with known releases. Whenever feasible, the source(s) of
released contamination will be removed as part of the remedial action prior to
closure and surveillance and monitoring. Surveillance and monitoring activities
will be conducted in accordance with requirements of the Resource Conservation
and Recovery Act and regulatory agencies, typically for a 30-year period after
the completion of remedial action. However, this estimate includes long-term
surveillance and monitoring costs only to FY 2000.
Direct Program Management/Support
General program support activities are those functions critical but ancillary
to the mission of the Environmental Management programs at Sandia. They include
strategic planning, program management, quality assurance, administrative
support, information services, training, facilities management/engineering and
maintenance, safeguards and security, logistics support, utilities,
procurement, contract management, legal support, and human resources. Specific
program support activities include environmental safety and health, permitting,
regulatory compliance, waste minimization/pollution prevention, technology
development, and stakeholder-related and information/outreach activities.
Most program management support activities for Sandia's Environmental
Restoration program are integrated within the Environmental Operations Center,
an organizational element of the Laboratories Services Division. These support
activities include project management systems (project controls), stakeholder
involvement, information management services (records, technical reference,
computer resources, financial affairs), and compliance assessment/regulatory
support (legal support, audit management). Other centers within the
Laboratories Services Division provide additional program management support
activities. Examples include strategic planning, emergency management, security
and safeguards, facilities planning, facilities construction, health and safety
oversight, and shipping and receiving.
| STAKEHOLDER INTERACTIONS
The Albuquerque Operations Office conducted public participation activities for
the following New Mexico sites: Inhalation Toxicology Research Institute, Los
Alamos National Laboratory, Sandia National Laboratories (and Holloman Air
Force Base), South Valley Site, Albuquerque Operations Office, and the Waste
Isolation Pilot Plant (and National Transuranic Waste Program Office).
Stakeholder activities included a presentation on basic information concerning
costs and activities at the sites at the Quarterly Environmental
Restoration/Waste Management Public Meeting and a briefing to the Sandia
National Laboratory/Department of Energy/Inhalation Toxicology Research
Institute Citizens Advisory Board. No site-specific activities were conducted
at the Waste Isolation Pilot Plant due to that site's pre-disposal status. If
you would like more information about the report or have questions about the
results for these sites, please contact:
|
Albuquerque Operations Office
Public Participation
Chris Houston
(505)8455483
chouston@doeal.gov
|
Technical Liaison
Jim Orr
(505) 845-4734
jorr@doeal.gov
|
Public Affairs
Tami Toops
(505) 845-5264
ttoops@doeal.gov
|
WASTE MANAGEMENT
Sandia produces waste from a variety of sources. As of May 1995, the
laboratories included over 1,000 active waste generators, 902 for hazardous
waste, 105 for radioactive waste, and 25 for mixed waste. Most produce small
quantities of waste associated with ongoing mission-related research and
development activities. Other sources include nuclear material and facility
stabilization waste, historical inventory, and other Department of Energy
facilities (e.g., the Inhalation Toxicology Research Institute and
Sandia/California). Additional radioactive and hazardous waste will be
generated by Sandia's Neutron Generator Production Program and its Medical
Isotope Production Program, which are expected to come on line in FY 1996 and
FY 1997, respectively.
The Offices of Environmental Management and Defense Programs provide funding to
manage Sandia's waste. Defense Programs is responsible for funding Sandia's
solid waste facilities (See site map for location of waste management
facilities). Both Environmental Management and Defense Programs provide
overhead funds to manage waste operations associated with weapons waste,
including neutron generators and solid waste. In addition, the Office of
Nuclear Energy will be responsible for funding the Medical Isotope Production
Program and associated waste Environmental Management is responsible for
funding Sandia's transuranic waste; low-level waste; low-level mixed waste;
hazardous waste, including polychlorinated biphenyls, asbestos, and explosives;
and special case waste. As noted in their respective discussions, all
treatment, storage, and disposal costs for nuclear material and facility
stabilization activities are included in the Waste Management program
estimates. All treatment, storage, and disposal costs associated with cleanup
are contained in the Environmental Restoration estimates.
Sandia has no high-level waste or spent nuclear fuel. Because the Office of
Defense Programs is responsible for solid waste (industrial and commercial
sanitary solid waste), lead/reapplication, medical waste, and other waste (oil,
non-regulated waste, weapons waste) at Sandia, these waste streams are not
included within the scope of this estimate.
In recent years, Sandia has constructed facilities to handle hazardous,
radioactive, and mixed waste; initial operational capability for these
facilities will be achieved during FY 1996. Subsequent full capability is
expected by FY 1999. FY 1996 facilities activities include the startup of
operations at the Radioactive/Mixed Waste Management Facility and the initial
phases of upgrades to this facility to accommodate mobile treatment units to
treat waste in accordance with the Site Treatment Plan Compliance Order. The
Department will maintain and upgrade all waste treatment and storage facilities
to comply with applicable regulations. Equipment for treating industrial
wastewater and low-level waste will also be maintained, and capital equipment
will be purchased as needed. Activities for outyears to FY 2070 will include
pursuing new and existing treatment options for low-level mixed waste, updating
the equipment for the mobile treatment units, and maintaining or upgrading
existing treatment facilities as needed.
To facilitate risk- and cost-reduction within the Waste Management program,
Sandia developed a Waste Minimization/Pollution Prevention Program with the
objectives of eliminating or minimizing the generation of waste through
source-reduction techniques, identifying recycling options for waste materials
that cannot be eliminated or minimized, and identifying treatment options to
reduce volume, toxicity, or waste mobility prior to storage or disposal. Waste
minimization activities include conducting Pollution Prevention Opportunity
Assessments to identify viable pollution reduction alternatives, creating a
Chemical Information System to track the purchase and use of all chemicals,
using a Pollution Prevention Team to enhance employee awareness, promoting
source reduction and recycling initiatives, and establishing a chargeback
system that taxes waste generators to fund pollution prevention implementation.
Major Waste Management Activity Milestones
| Radioactive and Mixed Waste Management Facility
|
1996
|
|
Mixed Waste Sort and Survey Project
|
1996
|
| Low-Level Waste Treatment Development
|
1999
|
|
Begin Low-Level Mixed Waste Treatment
|
2010
|
Transuranic Waste
GENERATION AND HANDLING
Transuranic waste contains radionuclides with an atomic number greater than
uranium, a half-life greater than 20 years, and alpha activity exceeding 100
nanocuries per gram of waste. Sandia manages transuranic waste operations with
support from a commercial subcontractor. The Inhalation Toxicology Research
Institute, operated for the Department of Energy Biomedical and Environmental
Research Institute in Albuquerque, generates most of Sandia' s transuranic
waste. In April 1995, Sandia was directed by the Department of Energy to accept
the Institute's transuranic waste to consolidate storage and reduce redundant
waste management costs. On May 10, 1995, 26 drums containing 5.45 cubic meters
(7.35 cubic yards) were accepted and transported to Sandia. The 26 drums were
transported to the Manzano Bunkers on Kirtland Air Force Base for storage
pending disposal at the Waste Isolation Pilot Plant.
Annual generation of transuranic waste is expected to remain at very low levels
not exceeding one drum (0.2 cubic meter [.27 cubic yards]) per year from the
Research Institute and one drum from ongoing Sandia mission work.
TREATMENT
No sampling or treatment of transuranic waste is scheduled to be performed at
Sandia. However, according to Sandia's Site Treatment Plan for Mixed Waste,
mixed transuranic waste will to be processed and certified to meet the Waste
Isolation Pilot Plant waste acceptance criteria by December 31, 2010.
STORAGE
Currently, Sandia stores approximately 5.5 cubic meters (7.1 cubic yards) of
transuranic waste at the Manzano Facility. Annual additions are expected to
remain low, not exceeding one drum (.2 cubic meter [.3 cubic yards]) per year
from the Institute and one drum from ongoing Sandia work. The Department will
periodically inspect and certify stored waste, as required, until FY 1998 when
the Waste Isolation Pilot Plant near Carlsbad, New Mexico, will begin to
receive transuranic waste.
DISPOSAL
This report assumes Sandia's transuranic waste will be disposed at the Waste
Isolation Pilot Plant near Carlsbad, New Mexico. Stored transuranic waste is
not expected to be disposed until FY 2009. Mixed transuranic waste is scheduled
for disposal by FY 2011. This estimate assumes 5.4 cubic meters (7.0 cubic
yards) of waste will be disposed until the current backlog is worked off.
Transuranic waste from both the Inhalation Toxicology Research Institute and
Sandia activities is packaged in accordance with Department of Transportation
regulations and Department of Energy Orders and transported to the
Manzano Bunkers for storage. Eventually, the Department will use overland truck
transporters to ship transuranic waste to the Waste Isolation Pilot Plant for
deep geologic disposal. The Waste Isolation Pilot Plant estimate includes the
cost for transporting and disposing all transuranic waste. The Sandia estimate
includes costs to characterize and package the waste in order to meet the Waste
Isolation Pilot Plant waste acceptance criteria.
Low-Level Mixed Waste
GENERATION AND HANDLING
Low-level mixed waste is waste that contains both radioactive and hazardous
components as defined by the Atomic Energy Act and the Resource Conservation
and Recovery Act. Sandia manages mixed waste operations with support from a
commercial subcontractor. Waste Operations crews collect the waste, complete
the generator location verification form, and apply bar code labels. The
Disposal Request Forms/Travelers are used for onsite transportation
documentation. The waste is delivered to the High-Bay Waste Storage Facility
for storage, pending treatment in accordance with the Site Treatment Plan
Compliance Order issued on October 4, 1995, by the State of New Mexico.
Mission-related activities generate approximately 4.8 cubic meters (6.3 cubic
yards) of mixed waste each year. Additional volumes will be generated by the
removal of radioactive legacy waste, the decontamination of the Hot Cell
Facility to prepare for startup of the Medical Isotope Production Program in FY
1997, and other decommissioning activities.
Culminating a three-year process in response to the Federal Facility Compliance
Act, the State of New Mexico issued an Order implementing Sandia's Site
Treatment Plan for Mixed Waste
on October 4, 1995. This plan consolidates Sandia's 192 mixed waste streams (as
listed in the Mixed Waste Inventory Report) within 16 treatability groups,
simplifying tracking and reducing reporting time. During FY 1996, Sandia will
complete a Mixed Waste Sort and Survey Project that began in FY 1995 to
validate all historical mixed waste, reduce inventory wherever possible, and
assign waste to approved treatability groups.
| LOW-LEVEL MIXED WASTE SUCCESS STORY
Within the first three months of the Mixed Waste Sort and Survey Project,
Sandia validated 954 batteries as nonradioactive and removed them from the
mixed waste inventory. This activity saved approximately $500,000.
|
As a further cost- and time-reducing measure, Sandia transferred
Sandia/California's mixed waste to its New Mexico site. This transfer avoided
the necessity of a separate California-based Site Treatment Plan and reduced
planning and reporting requirements because Sandia will have to report on only
one site to one state. Sandia/California shipped approximately 15 cubic meters
(20 cubic yards) of mixed waste to Sandia/New Mexico; additional small volumes
will be shipped periodically in the future .
TREATMENT
The Site Treatment Plan provides overall schedules for achieving compliance
with Land Disposal Restriction requirements for treatment and storage of mixed
waste. The plan includes a schedule for the submittal of permit applications,
construction of treatment facilities, technology development, offsite
transportation for treatment, and the treatment of mixed waste. Annual updates
to the plan are due March 31 of each year. Implementation of the plan
incorporates an integrated approach that relies heavily on the treatment
capacity being developed at the Mobile Treatment Units at Sandia and other
Department of Energy sites. Preferred treatment options include deactivation,
macroencapsulation, neutralization followed by stabilization, amalgamation,
incineration, thermal desorption, deactivation followed by stabilization,
evaporative oxidation, oxidation, and hydrothermal processing. All historical
low-level mixed waste at Sandia is scheduled to be treated by May 10, 2002.
After treatment, this waste will become either low-level or hazardous waste for
certification, transportation, and disposal.
Sandia also has approximately 0.4 cubic meters (0.5 cubic yards) of suspect
mixed transuranic waste. For this waste, the Site Treatment Plan provides a
treatment development milestone of June 30, 1999, and a treatment milestone of
December 31, 2010.
The Radioactive and Mixed Waste Management Facility, expected to start
operations in January 1996, will provide the means to open, treat, and
repackage low-level mixed waste. Treatment capacity will vary with the
treatment process, but the facility may accommodate 55 cubic meters (72 cubic
yards) of low-level and low-level mixed waste per year.
| TECHNOLOGY DEVELOPMENT
Because of Sandia's relatively small volumes of waste, it relies primarily on
commercial technologies to meet waste management needs. However, when treatment
methods are unavailable or difficult, Sandia supports technology development.
The site performs treatability studies and participated in the design and
construction of the Department of Energy's packed-bed reactor Mobile Treatment
Unit, which will be moved from site to site to treat low-level mixed waste in
compliance with the Federal Facility Compliance Act of 1992.
|
STORAGE
Over 65 cubic meters (85 cubic yards) of low-level mixed waste are currently in
storage at Sandia. The waste is packaged according to specific mixed waste
requirements, stored, and inspected on a regular basis. Both the High-Bay Waste
Storage Facility (Building 6596) and the Chemical Waste Storage Facility
(Building 920) are used for mixed waste storage.
After assessment, Sandia expects approximately 80 percent of currently
generated mixed waste will be placed into temporary storage and subsequently
certified for transportation to a commercial treatment and disposal facility;
20 percent will be retained onsite for treatment, using methods prescribed in
the Site Treatment Plan.
DISPOSAL
Waste that has been treated and separated into its radioactive and hazardous
components will be disposed according to the methods described under
radioactive (or transuranic) and hazardous waste respectively. Approximately 32
cubic meters (42 cubic yards) will be transferred to the Sandia, New Mexico
facility from Sandia National Laboratory-California with the remaining 1.5
cubic meters (2 cubic yards) assumed by this life-cycle estimate being shipped
to offsite commercial disposal facilities.
Low-Level Waste
GENERATION AND HANDLING
Low-level waste is generated by almost all Sandia activities involving
radioactive material and exists in a variety of forms such as contaminated
paper, plastic, rubber, organic matter, aqueous liquids, and sludges. Sandia
manages low-level waste operations with support from a commercial
subcontractor. The waste is then identified, classified, and collected. If
necessary, it is sampled, and routed as required for radiography at the
Real-Time Radiography Facility or assay at the Waste Assay Facility. It is then
minimally treated and either stored or packaged, certified, and transported to
the Nevada Test Site or other facility for disposal.
Ongoing low-level waste generation has averaged approximately 51 cubic meters
(67 cubic yards) per year over the past six years. In the near future, the
following new production and special generation activities will significantly
increase this annual generation figure.
TREATMENT
Sandia has conducted limited treatment of its low-level waste. The Radioactive
and Mixed Waste Management Facility is expected to start operating in FY 1996
and will provide the means to open, treat, and repackage low-level waste.
Potential treatment processes include screening, crushing, shredding and
baling, compaction, and solidification. Treatment capacity will vary with the
treatment process, but the facility may accommodate 55 cubic meters (72 cubic
yards) of low-level and low-level mixed waste per year.
STORAGE
Currently, low-level waste is transported to an interim storage site. After
Sandia's Radioactive/Mixed Waste Management Facility comes on-line during FY
1996, the Department will transport stored waste, as well as newly generated
waste, to the new facility. Waste is sampled as needed and routed as required
for radiography at the Real-Time Radiography Facility or assay at the Waste
Assay Facility. It is then stored, pending packaging, certification, and
transportation, to the Nevada Test Site or other facility for disposal.
Over 314 cubic meters (411 cubic yards) of low-level waste is currently in
storage at Sandia. Additional storage volumes will be accumulated by Sandia
because no regulatory driver exists and funding reductions preclude treatment
and disposal of low-level waste. Storage volumes will increase significantly,
perhaps by as much as 15,000 cubic meters (19,650 cubic yards) by FY 2000.
DISPOSAL
During FY 1995, permission was given to ship low-level waste to the Nevada Test
Site for disposal, culminating a three-year process to meet the Waste
Acceptance Criteria. Sandia sent the first shipment on September 25, 1995.
Sandia will ship additional waste to the Nevada Test Site during FY 1996 and FY
1997. But from FY 1998 until FY 2009, Sandia will only store low-level waste.
In FY 2009, as funding is shifted from the completed Environmental Restoration
program to the Waste Management program, Sandia will resume disposal of
accumulated waste and complete the process by 2021.
The Sandia disposal estimate includes transportation from collection through
disposal activities. It engages commercial support contractors to conduct these
operations on a daily basis. The estimate assumes 45,134 cubic meters (59,031
cubic yards) of waste will be generated.
Hazardous Waste
GENERATION AND HANDLING
Sandia separates its Environmental Management-funded hazardous waste into four
waste streams: chemical, polychlorinated biphenyls, asbestos, and explosive
waste. Chemical waste refers to regulated solid, liquid, or gaseous chemical
waste regulated by the Resource Conservation and Recovery Act, but does not
include radioactive or low-level mixed waste. Polychlorinated biphenyl waste
and asbestos waste are regulated by the Toxic Substances Control Act and by
Sandia requirements. Explosive waste is regulated by Department of Energy
Orders and by the requirements of the Occupational Safety and Health
Administration, the Resource Conservation and Recovery Act, the Department of
Transportation, and the New Mexico Environment Department.
Research and development activities at Sandia's numerous small laboratories
generate hazardous waste. These activities result in approximately 12,000
unique waste stream identification numbers. Polychlorinated biphenyl waste is
generated by ongoing decontamination and decommissioning activities and by
special projects, including the removal of transformers and ballasts associated
with the site-wide revamping and power modernization efforts, which will
continue through FY 2000. Asbestos waste is generated within two categories:
facilities (waste generated by building abatement and the decontamination
project) and nonfacilities asbestos (waste generated by large, high-volume
articles such as safes, file cabinets, and laboratory furnaces). Explosive
waste includes detonators, bulk explosives and propellants, debris contaminated
with explosives, and rocket motors.
Hazardous waste at Sandia is measured by weight rather than by volume. However,
for consistency, weights for the following waste streams are followed by
estimated equivalent volumes (metric and English). Total projected hazardous
waste generation for FY 1996 is 489,036 kilograms (383 cubic meters [502 cubic
yards]). Included in this total is 124,907 kilograms (114.1 cubic meters [150
cubic yards]) of chemical waste, 18,200 kilograms (16.9 cubic meters [22.1
cubic yards]) of polychlorinated biphenyls, 202,000 kilograms (134.4 cubic
meters [176 cubic yards] of asbestos, 29,429 kilograms (10.7 cubic meters [14
cubic yards]) of explosives, 60,000 kilograms (55.6 cubic meters [73 cubic
yards]) of hazardous waste from the Tonopah Test Range in Nevada, 52,500
kilograms (48.6 cubic meters [64 cubic yards]) from the Neutron Generation
Production Program, and 2,000 kilograms (1.6 cubic meters [12 cubic yards])
from Decontamination and Decommissioning.
Sandia manages waste operations for chemical waste, polychlorinated biphenyls,
and asbestos are managed by Sandia with support from a commercial
subcontractor. Sandia's Explosive Ordnance Division directs waste operations
for explosives, with subcontractor support for treatment, demilitarization, and
sanitization .
TREATMENT
Sandia does not treat its chemical, polychlorinated biphenyl, or asbestos
waste. It does, however, treat some of its explosive waste by means of
incineration at the Thermal Treatment Facility and at a commercial facility.
STORAGE
All waste regulated by the Resource Conservation and Recovery Act must be
disposed within 90 days. Sandia typically disposes of its chemical,
polychlorinated biphenyl, and asbestos waste within 30 days. Hazardous chemical
waste generated by research, development, and testing activities, as well as
polychlorinated biphenyl and nonfacilities asbestos waste, is collected from
generator locations, segregated by hazard class, and transported to the
Hazardous Waste Management Facility for storage. Facilities asbestos is placed
directly into transportation containers at the site.
Sandia also uses offsite storage in bunkers at the Manzano storage complex,
which is owned by the Department of Defense. Sandia uses these bunkers for
rocket motors, other explosives, classified waste, and demilitarized waste.
Approximately 1,100 rocket motors, ranging in weight from less than 50 to over
1000 kilograms, with an estimated total gross volume in excess of 1,052 cubic
meters (1,378 cubic yards), are currently in storage at Sandia facilities.
DISPOSAL
As stated above, Sandia's hazardous, polychlorinated biphenyl, and asbestos
waste is typically disposed within 30 days. Through its subcontractor, Sandia
uses more than a dozen commercial facilities to ensure the wide variety of
hazardous waste types are disposed in a timely, safe, and compliant manner.
Polychlorinated biphenyl waste is packaged into 0.2 cubic meter (55gallon)
drums and disposed at one of three offsite permitted commercial disposal
facilities. Asbestos waste is disposed offsite at a permitted commercial
disposal facility. Rocket motors and associated propellants are treated and
reclaimed/recycled.
During FY 1995, Sandia dispositioned 2,234 HVAR rocket motors and another 220
HAWK motors. In FY 1996, 766 Falcon rocket motors are scheduled for
disposition. Sandia's goal is to disposition all rocket motors before they are
declared waste, at which point they become subject to less-than-90-day Resource
Conservation and Recovery Act regulations. If this occurs, the Department would
have to divert funds earmarked for other waste management activities to cover
these costs. Activities are under way to excess the motors by making them
available for use by other government agencies.
The Sandia disposal estimate includes transportation to transport waste from
collection through disposal activities. It engages commercial support
contractors to conduct these operations on a daily basis .
Waste Management Activities Cost Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
|
| Transuranic Waste
|
|
|
|
|
|
|
|
|
| Storage and Handling
|
63
|
62
|
62
|
62
|
62
|
62
|
62
|
|
| Low-Level Mixed Waste
|
|
|
|
|
|
|
|
|
| Treatment |
240
|
291
|
433
|
646
|
646
|
646
|
646
|
|
| Storage and Handling
|
443
|
604
|
604
|
604
|
604
|
604
|
604
|
|
| Disposal |
102
|
265
|
821
|
|
701
|
120
|
|
|
| Low-Level Waste
|
|
|
|
|
|
|
|
|
| Treatment |
29
|
|
57
|
142
|
142
|
142
|
142
|
|
| Storage and Handling
|
418
|
1,128
|
1,488
|
2,028
|
2,028
|
2,028
|
2,028
|
|
| Disposal |
212
|
37
|
929
|
|
1,001
|
173
|
|
|
| Hazardous Waste
|
|
|
|
|
|
|
|
|
| Treatment |
391
|
570
|
570
|
570
|
570
|
570
|
570
|
|
| Storage and Handling
|
608
|
5,258
|
5,264
|
5,272
|
5,272
|
5,272
|
5,272
|
|
| Disposal |
1,939
|
3,266
|
3,549
|
3,974
|
3,974
|
3,974
|
3,974
|
|
| Direct Program Management/Support
|
6,410
|
4,636
|
4,636
|
4,636
|
4,636
|
4,636
|
4,636
|
|
| Total |
10,856
|
16,117
|
18,413
|
17,934
|
19,636
|
18,227
|
17,934
|
|
| |
|
| Transuranic Waste
|
|
|
|
|
|
|
|
|
| Storage and Handling
|
62
|
62
|
62
|
62
|
62
|
62
|
62
|
|
| Low-Level Mixed Waste
|
|
|
|
|
|
|
|
|
| Treatment |
646
|
646
|
646
|
646
|
646
|
646
|
646
|
|
| Storage and Handling
|
604
|
604
|
604
|
604
|
604
|
604
|
604
|
|
| Disposal |
|
|
|
|
|
|
|
|
| Low-Level Waste
|
|
|
|
|
|
|
|
|
| Treatment |
142
|
142
|
142
|
142
|
142
|
142
|
142
|
|
| Storage and Handling
|
2,028
|
2,028
|
2,028
|
2,028
|
2,028
|
2,028
|
2,028
|
|
| Disposal |
|
|
|
|
|
|
|
|
| Hazardous Waste
|
|
|
|
|
|
|
|
|
| Treatment |
570
|
570
|
570
|
570
|
570
|
570
|
570
|
|
| Storage and Handling
|
5,272
|
5,272
|
5,272
|
5,272
|
5,272
|
5,272
|
5,272
|
|
| Disposal |
3,974
|
3,974
|
3,974
|
3,974
|
3,974
|
3,974
|
3,974
|
|
| Direct Program Management/Support
|
4,636
|
4,636
|
4,636
|
4,636
|
4,636
|
4,636
|
4,636
|
|
| Total |
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
|
| |
2075
|
2080
|
2085
|
2090
|
2095
|
2100
|
| Transuranic Waste
|
|
|
|
|
|
|
|
|
| Storage and Handling
|
62
|
|
|
|
|
|
|
4,655
|
| Low-Level Mixed Waste
|
|
|
|
|
|
|
|
|
| Treatment |
646
|
|
|
|
|
|
|
43,582
|
| Storage and Handling
|
604
|
|
|
|
|
|
|
44,496
|
| Disposal |
120
|
|
|
|
|
|
|
10,635
|
| Low-Level Waste
|
|
|
|
|
|
|
|
|
| Treatment |
142
|
|
|
|
|
|
|
8,950
|
| Storage and Handling
|
2,028
|
|
|
|
|
|
|
136,850
|
| Disposal |
173
|
|
|
|
|
|
|
12,629
|
| Hazardous Waste
|
|
|
|
|
|
|
|
|
| Treatment |
570
|
|
|
|
|
|
|
41,855
|
| Storage and Handling
|
5,272
|
|
|
|
|
|
|
371,969
|
| Disposal |
3,974
|
|
|
|
|
|
|
282,212
|
| Direct Program Management/Support
|
4,636
|
|
|
|
|
|
|
356,570
|
| Total |
18,227
|
|
|
|
|
|
|
1,314,403
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
Direct Program Management/Support
General Program Support activities are those functions that are critical but
ancillary to the mission of the Environmental Management Programs at Sandia.
They include strategic planning, program management, quality assurance,
administrative support, information services, training, facilities
management/engineering and maintenance, safeguards and security, logistics
support, utilities, procurement, contract management, legal support, and human
resources. Specific program support activities include environmental safety and
health, permitting, regulatory compliance, waste minimization/pollution
prevention, technology development, and stakeholder-related and
information/outreach activities.
Most program management support activities for Sandia's Waste Management
Program are integrated within the Environmental Operations Center, an
organizational element of the Laboratories Services Division. These support
activities include project management systems (project controls), stakeholder
involvement, information management services (records, technical reference,
computer resources, financial), and compliance assessment/regulatory support
(legal support, audit management). Other centers within the Laboratories
Services Division provide additional program management support activities.
Examples include strategic planning, emergency management, security and
safeguards, facilities planning, facilities construction, health and safety
oversight, and shipping and receiving.
| WASTE MANAGEMENT COST SAVINGS
In its continuing pursuit of cost savings and program efficiency, Sandia has
successfully employed "Department of Energy partnerships;" that is, it has made
use of program knowledge developed at other Department of Energy sites for
Project Controls and Decontamination and Decommissioning; adopted the Idaho
National Engineering Laboratory Programmatic Waste Acceptance Criteria, and
used various Department of Energy contracts, including the Hazardous Remedial
Action Program Decontamination and Decommissioning contract and a Department of
Energy/Oak Ridge radioactive waste disposal contract. These cost and other
saving initiatives have enabled the Waste Management Program at Sandia to
achieve its mission while undergoing a 39 percent reduction in annual funding
since FY 1993.
|
DESCRIPTION OF PERSONNEL
Current Composition
The site personnel table provides a breakdown of current personnel composition
for Sandia's Environmental Management programs. This mix includes federal,
contractor and subcontractor work force. The federal staff consists of
management, administrative, and engineering support. The contractor and
subcontractor work force is a mix of professionals and labor that plans and
conducts the day-to-day activities at the site.
Full-Time Equivalent Composition Table *
* The Projections for Full-Time Equivalent employees are based on FY 1996
planning baselines (see Reader's Guide).
Site Management Structure
Sandia has established a Waste Management Project Department and an
Environmental Restoration Project Department to oversee Environmental
Management-funded and other activities. These departments provide direction to
the technical support departments that execute the work scope of these
projects.
Sandia's Environmental Management Project relies heavily on subcontractor
support. Contract mechanisms include As-Ordered Agreements, Time and Materials
technical support contracts, waste operations support contracts, and
competitive Task Order contracts. Future contracting mechanisms will further
incorporate competitive bidding approaches, and performance award fees.
Sandia Corporation, a Lockheed Martin subsidiary, is the management and
operating contractor under a five-year cost-plus contract that includes
performance based features. The contract is scheduled to be renewed in FY 1998.
| CONTRACTING OPPORTUNITIES
If you would like more information about performing work for the Department of
Energys Environmental Management program at this site, please contact:
|
Major Procurement
William Meyers
Director Contracts and Procurement Division
United States Department of Energy
Albuquerque Operations Office
P.O. Box 5400
Albuquerque, NM 87185-5400
p: (505) 845-5777
f: (505) 845-4210
|
Small Business Procurement
Greg Gonzales
Contracts and Procurement Division
United States Department of Energy
Albuquerque Operations Office
P.O. Box 5400
Albuquerque, NM 87185-5400
p: (505) 845-6182
f: (505) 845-4210
|
Future Full-Time Equivalent Needs
The Full-Time Equivalent table above provides a breakdown of future personnel
needs for Sandia's Environmental Management programs.
FUNDING ESTIMATE
The following two tables present estimated funding information for the Sandia
National Laboratories/New Mexico .
Defense Funding Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
|
| Nuclear Material and Facility Stabilization
|
|
4,130
|
2,857
|
1,320
|
554
|
|
|
|
| Environmental Restoration
|
18,045
|
25,000
|
|
831
|
2,359
|
|
|
|
| Waste Management
|
10,856
|
16,117
|
18,413
|
17,934
|
19,636
|
18,227
|
17,934
|
|
| Total |
28,901
|
45,248
|
21,269
|
20,085
|
22,548
|
18,227
|
17,934
|
|
|
FY 2035
|
2040
|
2045
|
2050
|
2055
|
2060
|
2065
|
|
| Nuclear Material and Facility Stabilization
|
|
|
|
|
|
|
|
|
| Environmental Restoration
|
|
|
|
|
|
|
|
|
| Waste Management
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
|
| Total |
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
17,934
|
|
| |
2075
|
2080
|
2085
|
2090
|
2095
|
2100
|
| Nuclear Material and Facility Stabilization
|
|
|
|
|
|
|
|
44,301
|
| Environmental Restoration
|
|
|
|
|
|
|
|
231,178
|
| Waste Management
|
18,227
|
|
|
|
|
|
|
1,314,403
|
| Total |
18,227
|
|
|
|
|
|
|
1,589,882
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
Nondefense Funding Estimate
| (Five-Year Averages, Thousands of Constant 1996
Dollars)
|
| |
FY 1996-2000
|
2025
|
2030
|
| Nuclear Material and Facility Stabilization
|
|
111
|
77
|
36
|
15
|
|
|
1,192
|
| * Total Life Cycle is the sum of the annual costs in
constant FY 1996 dollars.
|
COMPARISON WITH PREVIOUS ESTIMATE
Life-cycle cost estimates presented in this 1996 Baseline Environmental
Management Report are significantly different from those presented in the
Baseline Environmental Management Report for 1995. The life-cycle estimate for
the site has increased by 35 percent, or approximately $414 million. The
primary impact may be potential delays in completing environmental restoration
activities.
Comparison Table
|
Thousands of Dollars
|
|
| Nuclear Mat. & Fac. Stab.
|
39,924 |
2,600
|
45,493 |
17,345
|
22 |
| Environmental Restoration
|
242,047 |
23,295
|
231,178 |
73,109
|
6 |
| Waste Management |
703,203
|
12,537 |
1,314,403
|
29,994 |
90
|
| Landlord |
-
|
-
|
-
|
-
|
-
|
| Program Management 2
|
237,971 |
7,780
|
-
|
-
|
-
|
| Site Total |
1,223,145
|
46,212 |
1,591,074
|
414,141 |
35
|
1 The FY 1995 life-cycle and annual costs are provided
to determine the corrected FY 1995 cost.
2 Program Management was reported in an independent cost table last year, but
is reported as a line item in the relevant program (Nuclear Material and
Facility Stabilization, Environmental Restoration, and Waste Management)
activity cost estimate tables for the FY 1996 Baseline Report.
|
Nuclear Material and Facility Stabilization
The estimate for nuclear material and facility stabilization activities is 22
percent higher than the estimate in last year's report, after accounting for FY
1995 expenditures. The principal reason for this increase is the addition of
program management costs. The estimate was calculated using a parametric model.
Environmental Restoration
After accounting for FY 1995 expenditures and program management costs, the
1996 estimate is approximately six percent more than the FY 1995 estimate.
Remediation costs for the North Technical Areas, South Technical Areas, Firing
Ranges, and Thunder Range assume, based on currently available information,
ground-water contamination is limited to one site (requiring treatment) and the
standard for remediation is future Industrial or Recreational land use.
Assumptions about future land use relate to human health risk assessments;
thus, they control the extent of remediation and the volumetric estimate of
contaminated soil. The volumes estimated for hazardous, mixed, and low-level
radioactive waste generated by the Environmental Restoration program have been
significantly modified based on site data obtained during FY 1995 and, to some
extent, on new assumptions regarding the means to remediate some sites.
Overall, the Environmental Restoration waste volume estimates have been
reduced. In addition, the Environmental Restoration program now plans to use a
Temporary Unit for early storage of Environmental Restoration waste and a
Corrective Action Management Unit for disposal of most hazardous waste. This
report expects disposal of radioactive waste will take place at the Nevada Test
Site. In accordance with the site-level Memorandum of Understanding, costs for
managing waste generated by the Environmental Restoration program were included
within the scope of remedial costs.
Waste Management
The life-cycle cost estimate for the Waste Management program has almost
doubled from the value presented in the FY 1995 report. The principal reason
for the increase is that the assumed duration of support to the Office of
Defense Programs almost doubled, from 40 years in the 1995 estimate to 75 years
in the 1996 estimate. Applicable program management costs have also been
included in the Waste Management estimate for the FY 1996 Baseline Report.
|
 |