Amended Record of Decision: Idaho High-Level Waste and Facilities Disposition Final Environmental Impact Statement Revised by State 12/21/09, 137-140 [E9-31151]
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Federal Register / Vol. 75, No. 1 / Monday, January 4, 2010 / Notices
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[FR Doc. E9–31157 Filed 12–31–09; 8:45 am]
BILLING CODE 5001–06–P
DEPARTMENT OF ENERGY
Amended Record of Decision: Idaho
High-Level Waste and Facilities
Disposition Final Environmental
Impact Statement Revised by State
12/21/09
Department of Energy.
Amended Record of Decision.
AGENCY:
ACTION:
RECORD SOURCE CATEGORIES:
SUMMARY: The U.S. Department of
Energy (DOE) is amending its initial
Record of Decision (ROD) published
December 19, 2005 (70 Federal Register
[FR] 75165) (2005 ROD), pursuant to the
Idaho High-Level Waste and Facilities
Disposition Final Environmental Impact
Statement (DOE/EIS–0287), issued in
October 2002 1 (2002 EIS). The State of
Idaho was a cooperating agency in the
preparation of the EIS. The DOE
analyzed two sets of alternatives for
accomplishing its proposed actions
regarding the Idaho Nuclear Technology
and Engineering Center (lNTEC) at the
Idaho National Laboratory (INL,
formerly known as the Idaho National
Environmental and Engineering
Laboratory): (1) Waste processing
alternatives for high-level waste (HLW)
calcine and liquid sodium-bearing waste
(SBW); and (2) Waste management
facility disposition alternatives. Some of
the alternatives contained subalternatives referred to as ‘‘options’’ in
the EIS.
DOE has decided to select hot
isostatic pressing (HIP) as the
technology to treat calcine to provide a
volume reduced monolithic waste form
that is suitable for transport outside
Idaho, with completion of treatment by
a target date of December 31, 2035.
DOE has consulted with the State of
Idaho on the decision described herein.
DOE will continue to consult with the
State on the decisions yet to be made on
closure of calcine-related facilities.
ADDRESSES: Copies of this Amended
ROD will be available on DOE’s
National Environmental Policy Act
(NEPA) Web site at: https://
www.gc.energy.gov/nepa under DOE
NEPA Documents.
FOR FURTHER INFORMATION CONTACT: For
further information on this Amended
Information comes from source
documents such as written
examinations and grade sheets; from
reports by instructors and students; and
from the individual.
1 Pursuant to a phased decision strategy described
in the initial ROD, DOE has issued an amended
ROD on November 28, 2006 (71 FR 68811). This
new amended ROD supplements the decisions in
the two previous RODs.
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Ohio 45433–7765.
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Individuals seeking to determine
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address written inquiries to or visit the
Communications and Information
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Technology, 2950 Hobson Way, WrightPatterson Air Force Base, Ohio 45433–
7765.
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record.
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Individuals seeking access to
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in this system should address written
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and Information Directorate, Air Force
Institute of Technology, 2950 Hobson
Way, Wright-Patterson Air Force Base,
Ohio 45433–7765.
Request should include full name,
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details that will assist in locating the
record.
CONTESTING RECORD PROCEDURES:
RETRIEVABILITY:
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Destroy 30 years after individual
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course. Computer records are destroyed
by erasing, deleting or overwriting.
Paper records are destroyed by
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137
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Federal Register / Vol. 75, No. 1 / Monday, January 4, 2010 / Notices
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ROD and the Idaho Cleanup Project,
contact Nolan R. Jensen, Federal Project
Director, U.S. DOE, Idaho Operations
Office, 1955 Fremont Avenue, MS 1222,
Idaho Falls, ID 83415, telephone: (208)
526–5793.
For general information on DOE’s
NEPA process, please contact: Carol M.
Borgstrom, Director, Office of NEPA
Policy and Compliance (GC–54), U.S.
DOE, 1000 Independence Avenue, SW.,
Washington, DC 20585–0103,
Telephone: (202) 586–4600 or leave a
message at (800) 472–2756.
SUPPLEMENTARY INFORMATION:
I. Background
From 1952 to 1991, DOE and its
predecessor agencies reprocessed spent
nuclear fuel (SNF) at INTEC, known
prior to 1998 as the Idaho Chemical
Processing Plant, on the INL Site.
Reprocessing operations used solvent
extraction systems to remove mostly
uranium-235 from SNF. The waste
product from the first extraction cycle of
the reprocessing operation was liquid
HLW mixed with hazardous materials.
Subsequent extraction cycles, treatment
processes, and follow-on
decontamination activities generated
additional liquid HLW that was
combined to form SBW, which is
generally much less radioactive than
HLW generated from the first extraction
cycle. These liquid wastes were stored
in eleven 300,000-gallon below-grade
storage tanks. The last campaign of SNF
reprocessing at INTEC was in 1991, and
HLW was no longer generated at INTEC
after that time. From 1963 to 1998, DOE
processed HLW and SBW through a
calcination process that converted the
liquid waste into a dry powder referred
to as calcine. Some SBW was processed
by calcination from 1998 to 2000, when
a decision to shut down the New Waste
Calcining Facility was made.
At present, approximately 4,400 cubic
meters of HLW calcine remain stored in
six bin sets (a series of reinforced
concrete vaults, each containing three to
twelve stainless steel storage bins). The
stainless steel in the storage bins is
highly corrosion resistant, and the bins
are designed to be secure for at least 500
years. Based on the analyses
summarized in the EIS, DOE has
concluded that the calcine stored in the
bins poses no significant present hazard
to public health or the environment.
As a result of litigation, DOE and the
State of Idaho reached an agreement in
1995 referred to as the Idaho Settlement
Agreement/Consent Order (Settlement
Agreement) that, among other things,
requires DOE to ‘‘treat all HLW
currently at INEL so that it is ready to
be moved outside of Idaho for disposal
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17:11 Dec 31, 2009
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by a target date of 2035.’’ It further
requires that a ROD be issued no later
than December 31, 2009 establishing a
date for completion of the treatment of
all calcined waste located at the INL
Site by a contemplated target date of
December 31, 2035. The Settlement
Agreement also requires that DOE
submit an application for a RCRA (or
statutory equivalent) Part B Permit to
the State by December 1, 2012.
DOE issued the Idaho High-Level
Waste and Facilities Disposition Final
Environmental Impact Statement in
October 2002, with the State of Idaho as
a cooperating agency. The EIS analyzed
two sets of alternatives for
accomplishing the proposed action
relative to calcine:
1. Waste processing alternatives for
liquid SBW, including newly generated
liquid waste stored in three 300,000
gallon below grade tanks, and solid
calcine stored in bin sets at the INTEC
on the INL Site; and
2. Facility disposition alternatives for
final disposition of facilities directly
related to the HLW and SBW Program
after its missions are complete,
including any new facilities necessary
to implement the waste processing
alternatives.
In DOE’s 2005 ROD, DOE decided to
pursue a phased decision-making
process regarding the proposed actions
in the EIS. DOE also decided, among
other things, to treat the remaining
liquid SBW using the steam reforming
technology and to conduct performancebased RCRA closure of existing facilities
directly related to the HLW program at
INTEC, excluding the INTEC Tank Farm
Facility (TFF) and bin set closure. As a
result, DOE is constructing a facility for
the purpose of treating and packaging
the SBW. This new facility is known as
the Integrated Waste Treatment Unit
(IWTU).
The 2005 ROD also addressed the
plan to issue an Amended ROD in 2006
specifically addressing closure of the
TFF as well as an Amended ROD in
2009 addressing the strategy for calcine
disposition and bin set closure. In the
2006 Amended ROD (71 FR 68811),
DOE decided to conduct performance
based closure of the INTEC TFF.
Decisions made in this ROD consider
the Administration’s intent to terminate
ongoing funding for the Yucca
Mountain program while evaluating
nuclear waste disposal alternatives, as
indicated in the Administration’s fiscal
year 2010 budget request. DOE remains
committed to meeting its obligations to
manage and ultimately dispose of HLW
and spent nuclear fuel. DOE will
convene a Blue Ribbon Commission to
evaluate alternatives for meeting these
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obligations. The commission will
provide the opportunity for a
meaningful dialogue on how best to
address this challenging issue and will
provide recommendations to DOE that
will form the basis for working with the
Congress to revise if appropriate the
statutory framework for managing and
disposing of HLW and spent nuclear
fuel. The ultimate disposition of the
calcine HLW, and the applicable waste
acceptance criteria, may be affected by
the upcoming recommendations of the
anticipated Blue Ribbon Commission.
II. Waste Processing Alternatives
Analyzed in the EIS
The 2002 EIS analyzed six
alternatives for calcine:
• No Action Alternative
Under this alternative, the New Waste
Calcining Facility (NWCF) would
remain in standby and the calcine
would remain in the bin sets
indefinitely.
• Continued Current Operations
Alternative
Under this alternative, the NWCF
would remain in standby pending
receipt of a RCRA permit from the State
of Idaho and upgrades to air emission
controls required by the U.S.
Environmental Protection Agency
(EPA).
• Separations Alternative (with three
treatment options)
This alternative comprises three
treatment options, each of which would
use a chemical separations process,
such as solvent extraction, to divide the
calcine into fractions suitable for
disposition as either: HLW, transuranic
(TRU) waste, or low-level waste,
depending on waste characteristics.
Separating the radionuclides in the
waste into fractions would decrease the
amount of HLW, saving space and
reducing disposition costs. The three
waste treatment options under the
Separations Alternative are described
below:
1. The Full Separations Option would
separate the radioisotopes in the calcine
into high-level and low-level waste
fractions. The HLW fraction would be
vitrified in a new facility at INTEC,
placed in stainless steel canisters, and
stored onsite until shipped to a storage
or disposition facility. DOE would
dispose of the low-level waste fraction
on site, or at an offsite DOE or
commercial low-level waste disposal
facility.
2. The Planning Basis Option reflects
previously announced DOE decisions
and agreements with the State of Idaho
regarding the management of HLW. It is
similar to the Full Separations Option in
that, after separations, the HLW fraction
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would be vitrified in a new facility at
INTEC, placed in stainless steel
canisters, and stored onsite until
shipped to a storage or disposition
facility. DOE would dispose of the lowlevel waste fraction on site, or at an
offsite DOE or commercial low-level
waste disposal facility.
3. The Transuranic Separations
Option would consist of separating the
HLW into two fractions. The resulting
fractions would be managed as TRU
waste and low level waste. The TRU
fraction that meets applicable
requirements, would be solidified,
packaged, and shipped to the Waste
Isolation Pilot Plant for disposal. DOE
would dispose of the low-level waste
fraction on site or at an offsite DOE or
commercial low-level waste disposal
facility.
• Non-Separations Alternative (with
four treatment options)
This alternative includes four
treatment options for solidifying HLW
calcine. The four treatment options are
briefly described below:
1. The Hot Isostatic Pressing (HIP)
Waste Option under which HLW calcine
would be treated in a high pressure,
high temperature process that would
convert the calcine into a glass-ceramic
waste form. The final product would be
packaged for storage, transport, and
disposition.
2. The Direct Cement Waste Option
under which HLW calcine would be
retrieved, mixed with cement, poured in
stainless-steel canisters, and cured at
elevated temperature and pressure. The
canisters would be placed in storage for
transport and subsequent disposition.
3. The Early Vitrification Option
would involve vitrifying the HLW
calcine into a glass-like solid. The
vitrified HLW would be placed in
interim storage pending disposition.
4. The Steam Reforming Option
includes packaging of HLW calcine
without additional treatment for
shipment and disposition.
• Minimum INEEL (now INL)
Processing Alternative
This alternative would minimize the
amount of waste treatment at the INL by
using the vitrification facility (Waste
Treatment Plant) under construction for
the DOE Hanford Site in the State of
Washington. The HLW calcine would be
placed in shipping containers and sent
to the Hanford Site where it would be
vitrified.
• Direct Vitrification Alternative
(with two treatment options)
This alternative includes two
treatment options: Vitrification without
Calcine Separations and Vitrification
with Calcine Separations. The option to
vitrify calcine without separations
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17:11 Dec 31, 2009
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would be similar to the Early
Vitrification Option. The option to
vitrify the HLW fraction from calcine
separations would be similar to the Full
Separations Option. Under the
Vitrification with Calcine Separations
Option, calcine would be retrieved from
the bin sets, and chemically separated
into a HLW fraction to be vitrified and
a low-level waste (LLW) fraction to be
grouted. Under the Vitrification without
Calcine Separations Option, calcine
would be directly vitrified. Under either
option, vitrified HLW would be stored
pending disposition.
III. DOE and the State of Idaho
Preferred Alternatives Identified in the
EIS
The DOE Preferred Alternative
identified in the 2002 EIS for waste
processing (including calcine) was to
implement the proposed action by
selecting from among the action
alternatives, options, and technologies
analyzed in the 2002 EIS. The selection
of any one of, or combination of,
technologies or options used to
implement the proposed action would
be based on the performance criteria of
technical maturity, environmental
health and safety considerations,
consideration of public comment, cost,
schedule, and programmatic risk.
Options excluded from DOE’s preferred
alternative were storage of calcine in bin
sets for an indefinite period of time
(analyzed under the Continued Current
Operation Alternative), shipment of all
calcine to the Hanford Site for treatment
(analyzed under the Minimum INEEL
[now INL] Processing Alternative), and
disposal of mixed LLW at INL (analyzed
under multiple alternatives).
The State of Idaho Preferred
Alternative identified in the 2002 EIS
for waste processing was the Direct
Vitrification Alternative. The State of
Idaho preferred vitrification based on
the belief that it was the treatment
alternative with the lowest technical
and regulatory uncertainty for meeting
waste removal goals and providing a
clear baseline for fulfilling the
objectives of removal of waste from
Idaho within the timelines envisioned
by the Settlement Agreement. The State
of Idaho was willing to consider other
waste treatment options, if they were
comparable or better than the Direct
Vitrification Alternative in terms of
environmental impact, schedule, and/or
cost.
IV. Environmentally Preferable
Alternative
In nine of fourteen environmental
areas analyzed, the 2002 EIS indicates
little or no environmental impact would
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139
occur under all of the action
alternatives. In the remaining five areas
analyzed (air, traffic and transportation,
health and safety, waste and materials,
and facility accidents), the results
indicate that potential short-term
impacts from routine exposures would
be small and would not differ
significantly among action alternatives.
Under normal operations, none of the
waste processing action alternatives
analyzed in the EIS would result in
large short-term or long-term impacts to
human health or the environment. Also,
none of the action alternatives would
result in appreciably different impacts
on historic, cultural and natural
resources.
Any of the waste treatment
alternatives that place the calcine in a
waste form suitable for disposition
outside of the State of Idaho would be
environmentally preferable compared to
the No Action and Continued Current
Operations Alternatives.
V. Decision
DOE has decided to deploy the HIP
technology to cost-effectively treat the
calcine waste. This option also presents
the flexibility to either:
• Treat calcine in a sealed high
temperature and high pressure canning
process including the addition of
treatment additives necessary to
produce a glass-ceramic and volume
reduced monolithic waste form; or
• Treat calcine in a sealed high
temperature and high pressure canning
process without addition of treatment
additives resulting in an even greater
volume reduction.
The HIP technology deployed for the
treatment of HLW calcine also provides
the technological capability to further
treat the SBW steam-reformed carbonate
waste form, should such treatment be
necessary in order for this waste to be
ready to leave Idaho by 2035 as required
by the 1995 Settlement Agreement.
Treatment using the HIP technology
has been demonstrated to generate a
waste form consistent with waste form
requirements that are currently
specified for the performance of singlephase borosilicate glass being produced
at DOE’s Defense Waste Processing
Facility at the Savannah River Site and
to be produced at the Waste Treatment
Plant at DOE’s Hanford Site. The use of
HIP with the addition of treatment
additives will be necessary to eliminate
the RCRA hazardous waste
characteristics should calcine be
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140
Federal Register / Vol. 75, No. 1 / Monday, January 4, 2010 / Notices
dispositioned at a non-RCRA-permitted
site outside the State of Idaho.2
If it is decided to disposition calcine
at a RCRA-permitted facility outside the
State of Idaho, the use of HIP without
addition of treatment additives would
cost-effectively reduce the volume of
waste even further, resulting in fewer
canisters of product to be ultimately
shipped for such disposition outside the
State of Idaho.3
DOE’s decision will allow DOE to
meet the provisions of the Settlement
Agreement for the treatment of all
calcinated waste and, if applicable,
SBW.
To facilitate treatment, DOE has
decided to retrieve and pneumatically
(forced air through piping) transport the
calcine to a surge tank located at the
head end of the IWTU at such time as
the calcine treatment and packaging
process is about to commence. The
IWTU facility, after completion of its
SBW mission and suitable
reconfiguration, will be used to support
treatment of the calcine and other
wastes and meet associated safety and
seismic design basis requirements.
In accordance with the Settlement
Agreement, DOE will submit a request
for a Permit Modification to the
Integrated Waste Treatment Unit RCRA
Part B Permit no later than December 1,
2012, that will address:
• Calcine retrieval and pneumatic
transport of the retrieved calcine to a
designed surge tank to be located at the
head end of the IWTU facility, and
• HIP treatment/processing of all
calcine within a modified IWTU facility.
DOE has consulted with the State of
Idaho on the decisions described herein.
The State of Idaho concurs with DOE’s
selection of HIP technology to treat
calcine (and concurs that it provides the
technological capability to further treat
the SBW steam-reformed carbonate
waste form, should such treatment be
necessary) to produce a glass ceramic
and volume reduced monolithic waste
form. This treatment appears
comparable to single-phase borosilicate
glass resulting from vitrification which
was Idaho’s previous preferred
alternative. Idaho prefers the HIP
technology with the addition of
treatment additives because it is the
most likely form to meet current
regulatory requirements allowing for
disposal outside the State of Idaho.
Idaho does not object to the HIP
2 Under this treatment option (HIP with
additives), an approved delisting petition would be
required and any land disposal restrictions would
also have to be met.
3 Under this treatment option (HIP without
treatment additives), any land disposal restrictions
would also have to be met.
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17:11 Dec 31, 2009
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technology without the addition of
treatment additives provided the final
waste form is eligible for transport
outside the State of Idaho for storage or
disposition. DOE will continue to
consult with the State on the decisions
yet to be made concerning the addition
of treatment additives for the HIP
treatment of the calcine waste.
No environmental impacts resulting
from operations under this decision
would require specific mitigation
measures. DOE will, however, use all
practicable means to avoid or minimize
environmental harm when
implementing the actions described in
this amended ROD. Those measures
include employing engineering design
features to ensure that calcine waste
processing via HIP is conducted safely
and in accordance with all applicable
regulatory requirements. Other
measures include maintaining a
rigorous health and safety program to
protect workers from radiological and
chemical contaminants, monitoring
worker and environmental risk, and
continuing efforts to reduce generation
of wastes. DOE will implement the
comprehensive list of standards and
requirements to protect workers, the
public, and the environment specified
in Chapter 6 of the Final EIS, as
appropriate.
VI. Basis for Decision
DOE is selecting the HIP technology
to treat calcine HLW for a number of
reasons. The HIP technology is
anticipated to cost-effectively treat the
calcine waste, reduce the volume of the
waste, and place the waste in a form
ready to be moved out of the State of
Idaho, consistent with the dates in the
Settlement Agreement.
Issued in Washington, DC, on December
23, 2009.
´
Ines R. Triay,
Assistant Secretary for Environmental
Management.
[FR Doc. E9–31151 Filed 12–31–09; 8:45 am]
BILLING CODE 6450–01–P
DEPARTMENT OF ENERGY
Federal Energy Regulatory
Commission
[Project No. 13328–001]
Cordova Electric Cooperative, Inc.;
Notice of Intent To File License
Application, Filing of Pre-Application
Document, and Approving Use of the
Alternative Licensing Procedures
December 24, 2009.
a. Type of Filing: Notice of Intent to
File License Application, Filing of Pre-
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Application Document, and Approving
Use of the Alternative Licensing
Procedures.
b. Project No.: 13328–001.
c. Dated Filed: October 28, 2009.
d. Submitted by: Cordova Electric
Cooperative, Inc. (Cordova Electric).
e. Name of Project: Snyder Falls Creek
Hydroelectric Project.
f. Location: On Snyder Falls Creek,
near the town of Cordova, Alaska. The
project would occupy lands within the
Chugach National Forest administered
by the U.S. Forest Service.
g. Filed Pursuant to: 18 CFR 5.3 of the
Commission’s regulations.
h. Applicant Contact: Clay Koplin,
CEO, Cordova Electric Cooperative, Inc.,
705 Second Street, Cordova, Alaska
99574; (907) 424–5026; e-mail at
ckoplin@cordovaelectric.com.
i. FERC Contact: Steve Hocking at
(202) 502–8753; or e-mail at
steve.hocking@ferc.gov.
j. Cordova Electric filed a request to
use the Alternative Licensing
Procedures on October 28, 2009.
Cordova Electric issued a public notice
of its request on November 5, 2009. In
a letter dated December 24, 2009, the
Director, Division of Hydropower
Licensing approved Cordova Electric’s
request to use the Alternative Licensing
Procedures.
k. With this notice, we are initiating
informal consultation with: (a) The U.S.
Fish and Wildlife Service and/or NOAA
Fisheries under section 7 of the
Endangered Species Act and the joint
agency regulations thereunder at 50
CFR, Part 402; (b) NOAA Fisheries
under section 305(b) of the MagnusonStevens Fishery Conservation and
Management Act and implementing
regulations at 50 CFR section 600.920;
and (c) the Alaska State Historic
Preservation Officer, as required by
section 106, National Historic
Preservation Act, and the implementing
regulations of the Advisory Council on
Historic Preservation at 36 CFR section
800.2.
l. With this notice, we are designating
Cordova Electric as the Commission’s
non-federal representative for carrying
out informal consultation, pursuant to
section 7 of the Endangered Species Act,
section 305 of the Magnuson-Stevens
Fishery Conservation and Management
Act, and section 106 of the National
Historic Preservation Act.
m. Cordova Electric filed a PreApplication Document (PAD; including
a proposed process plan and schedule)
with the Commission, pursuant to 18
CFR 5.6 of the Commission’s
regulations.
n. A copy of the PAD is available for
review at the Commission in the Public
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Agencies
[Federal Register Volume 75, Number 1 (Monday, January 4, 2010)]
[Notices]
[Pages 137-140]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-31151]
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DEPARTMENT OF ENERGY
Amended Record of Decision: Idaho High-Level Waste and Facilities
Disposition Final Environmental Impact Statement Revised by State 12/
21/09
AGENCY: Department of Energy.
ACTION: Amended Record of Decision.
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SUMMARY: The U.S. Department of Energy (DOE) is amending its initial
Record of Decision (ROD) published December 19, 2005 (70 Federal
Register [FR] 75165) (2005 ROD), pursuant to the Idaho High-Level Waste
and Facilities Disposition Final Environmental Impact Statement (DOE/
EIS-0287), issued in October 2002 \1\ (2002 EIS). The State of Idaho
was a cooperating agency in the preparation of the EIS. The DOE
analyzed two sets of alternatives for accomplishing its proposed
actions regarding the Idaho Nuclear Technology and Engineering Center
(lNTEC) at the Idaho National Laboratory (INL, formerly known as the
Idaho National Environmental and Engineering Laboratory): (1) Waste
processing alternatives for high-level waste (HLW) calcine and liquid
sodium-bearing waste (SBW); and (2) Waste management facility
disposition alternatives. Some of the alternatives contained sub-
alternatives referred to as ``options'' in the EIS.
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\1\ Pursuant to a phased decision strategy described in the
initial ROD, DOE has issued an amended ROD on November 28, 2006 (71
FR 68811). This new amended ROD supplements the decisions in the two
previous RODs.
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DOE has decided to select hot isostatic pressing (HIP) as the
technology to treat calcine to provide a volume reduced monolithic
waste form that is suitable for transport outside Idaho, with
completion of treatment by a target date of December 31, 2035.
DOE has consulted with the State of Idaho on the decision described
herein. DOE will continue to consult with the State on the decisions
yet to be made on closure of calcine-related facilities.
ADDRESSES: Copies of this Amended ROD will be available on DOE's
National Environmental Policy Act (NEPA) Web site at: https://www.gc.energy.gov/nepa under DOE NEPA Documents.
FOR FURTHER INFORMATION CONTACT: For further information on this
Amended
[[Page 138]]
ROD and the Idaho Cleanup Project, contact Nolan R. Jensen, Federal
Project Director, U.S. DOE, Idaho Operations Office, 1955 Fremont
Avenue, MS 1222, Idaho Falls, ID 83415, telephone: (208) 526-5793.
For general information on DOE's NEPA process, please contact:
Carol M. Borgstrom, Director, Office of NEPA Policy and Compliance (GC-
54), U.S. DOE, 1000 Independence Avenue, SW., Washington, DC 20585-
0103, Telephone: (202) 586-4600 or leave a message at (800) 472-2756.
SUPPLEMENTARY INFORMATION:
I. Background
From 1952 to 1991, DOE and its predecessor agencies reprocessed
spent nuclear fuel (SNF) at INTEC, known prior to 1998 as the Idaho
Chemical Processing Plant, on the INL Site. Reprocessing operations
used solvent extraction systems to remove mostly uranium-235 from SNF.
The waste product from the first extraction cycle of the reprocessing
operation was liquid HLW mixed with hazardous materials. Subsequent
extraction cycles, treatment processes, and follow-on decontamination
activities generated additional liquid HLW that was combined to form
SBW, which is generally much less radioactive than HLW generated from
the first extraction cycle. These liquid wastes were stored in eleven
300,000-gallon below-grade storage tanks. The last campaign of SNF
reprocessing at INTEC was in 1991, and HLW was no longer generated at
INTEC after that time. From 1963 to 1998, DOE processed HLW and SBW
through a calcination process that converted the liquid waste into a
dry powder referred to as calcine. Some SBW was processed by
calcination from 1998 to 2000, when a decision to shut down the New
Waste Calcining Facility was made.
At present, approximately 4,400 cubic meters of HLW calcine remain
stored in six bin sets (a series of reinforced concrete vaults, each
containing three to twelve stainless steel storage bins). The stainless
steel in the storage bins is highly corrosion resistant, and the bins
are designed to be secure for at least 500 years. Based on the analyses
summarized in the EIS, DOE has concluded that the calcine stored in the
bins poses no significant present hazard to public health or the
environment.
As a result of litigation, DOE and the State of Idaho reached an
agreement in 1995 referred to as the Idaho Settlement Agreement/Consent
Order (Settlement Agreement) that, among other things, requires DOE to
``treat all HLW currently at INEL so that it is ready to be moved
outside of Idaho for disposal by a target date of 2035.'' It further
requires that a ROD be issued no later than December 31, 2009
establishing a date for completion of the treatment of all calcined
waste located at the INL Site by a contemplated target date of December
31, 2035. The Settlement Agreement also requires that DOE submit an
application for a RCRA (or statutory equivalent) Part B Permit to the
State by December 1, 2012.
DOE issued the Idaho High-Level Waste and Facilities Disposition
Final Environmental Impact Statement in October 2002, with the State of
Idaho as a cooperating agency. The EIS analyzed two sets of
alternatives for accomplishing the proposed action relative to calcine:
1. Waste processing alternatives for liquid SBW, including newly
generated liquid waste stored in three 300,000 gallon below grade
tanks, and solid calcine stored in bin sets at the INTEC on the INL
Site; and
2. Facility disposition alternatives for final disposition of
facilities directly related to the HLW and SBW Program after its
missions are complete, including any new facilities necessary to
implement the waste processing alternatives.
In DOE's 2005 ROD, DOE decided to pursue a phased decision-making
process regarding the proposed actions in the EIS. DOE also decided,
among other things, to treat the remaining liquid SBW using the steam
reforming technology and to conduct performance-based RCRA closure of
existing facilities directly related to the HLW program at INTEC,
excluding the INTEC Tank Farm Facility (TFF) and bin set closure. As a
result, DOE is constructing a facility for the purpose of treating and
packaging the SBW. This new facility is known as the Integrated Waste
Treatment Unit (IWTU).
The 2005 ROD also addressed the plan to issue an Amended ROD in
2006 specifically addressing closure of the TFF as well as an Amended
ROD in 2009 addressing the strategy for calcine disposition and bin set
closure. In the 2006 Amended ROD (71 FR 68811), DOE decided to conduct
performance based closure of the INTEC TFF.
Decisions made in this ROD consider the Administration's intent to
terminate ongoing funding for the Yucca Mountain program while
evaluating nuclear waste disposal alternatives, as indicated in the
Administration's fiscal year 2010 budget request. DOE remains committed
to meeting its obligations to manage and ultimately dispose of HLW and
spent nuclear fuel. DOE will convene a Blue Ribbon Commission to
evaluate alternatives for meeting these obligations. The commission
will provide the opportunity for a meaningful dialogue on how best to
address this challenging issue and will provide recommendations to DOE
that will form the basis for working with the Congress to revise if
appropriate the statutory framework for managing and disposing of HLW
and spent nuclear fuel. The ultimate disposition of the calcine HLW,
and the applicable waste acceptance criteria, may be affected by the
upcoming recommendations of the anticipated Blue Ribbon Commission.
II. Waste Processing Alternatives Analyzed in the EIS
The 2002 EIS analyzed six alternatives for calcine:
No Action Alternative
Under this alternative, the New Waste Calcining Facility (NWCF)
would remain in standby and the calcine would remain in the bin sets
indefinitely.
Continued Current Operations Alternative
Under this alternative, the NWCF would remain in standby pending
receipt of a RCRA permit from the State of Idaho and upgrades to air
emission controls required by the U.S. Environmental Protection Agency
(EPA).
Separations Alternative (with three treatment options)
This alternative comprises three treatment options, each of which
would use a chemical separations process, such as solvent extraction,
to divide the calcine into fractions suitable for disposition as
either: HLW, transuranic (TRU) waste, or low-level waste, depending on
waste characteristics. Separating the radionuclides in the waste into
fractions would decrease the amount of HLW, saving space and reducing
disposition costs. The three waste treatment options under the
Separations Alternative are described below:
1. The Full Separations Option would separate the radioisotopes in
the calcine into high-level and low-level waste fractions. The HLW
fraction would be vitrified in a new facility at INTEC, placed in
stainless steel canisters, and stored onsite until shipped to a storage
or disposition facility. DOE would dispose of the low-level waste
fraction on site, or at an offsite DOE or commercial low-level waste
disposal facility.
2. The Planning Basis Option reflects previously announced DOE
decisions and agreements with the State of Idaho regarding the
management of HLW. It is similar to the Full Separations Option in
that, after separations, the HLW fraction
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would be vitrified in a new facility at INTEC, placed in stainless
steel canisters, and stored onsite until shipped to a storage or
disposition facility. DOE would dispose of the low-level waste fraction
on site, or at an offsite DOE or commercial low-level waste disposal
facility.
3. The Transuranic Separations Option would consist of separating
the HLW into two fractions. The resulting fractions would be managed as
TRU waste and low level waste. The TRU fraction that meets applicable
requirements, would be solidified, packaged, and shipped to the Waste
Isolation Pilot Plant for disposal. DOE would dispose of the low-level
waste fraction on site or at an offsite DOE or commercial low-level
waste disposal facility.
Non-Separations Alternative (with four treatment options)
This alternative includes four treatment options for solidifying
HLW calcine. The four treatment options are briefly described below:
1. The Hot Isostatic Pressing (HIP) Waste Option under which HLW
calcine would be treated in a high pressure, high temperature process
that would convert the calcine into a glass-ceramic waste form. The
final product would be packaged for storage, transport, and
disposition.
2. The Direct Cement Waste Option under which HLW calcine would be
retrieved, mixed with cement, poured in stainless-steel canisters, and
cured at elevated temperature and pressure. The canisters would be
placed in storage for transport and subsequent disposition.
3. The Early Vitrification Option would involve vitrifying the HLW
calcine into a glass-like solid. The vitrified HLW would be placed in
interim storage pending disposition.
4. The Steam Reforming Option includes packaging of HLW calcine
without additional treatment for shipment and disposition.
Minimum INEEL (now INL) Processing Alternative
This alternative would minimize the amount of waste treatment at
the INL by using the vitrification facility (Waste Treatment Plant)
under construction for the DOE Hanford Site in the State of Washington.
The HLW calcine would be placed in shipping containers and sent to the
Hanford Site where it would be vitrified.
Direct Vitrification Alternative (with two treatment
options)
This alternative includes two treatment options: Vitrification
without Calcine Separations and Vitrification with Calcine Separations.
The option to vitrify calcine without separations would be similar to
the Early Vitrification Option. The option to vitrify the HLW fraction
from calcine separations would be similar to the Full Separations
Option. Under the Vitrification with Calcine Separations Option,
calcine would be retrieved from the bin sets, and chemically separated
into a HLW fraction to be vitrified and a low-level waste (LLW)
fraction to be grouted. Under the Vitrification without Calcine
Separations Option, calcine would be directly vitrified. Under either
option, vitrified HLW would be stored pending disposition.
III. DOE and the State of Idaho Preferred Alternatives Identified in
the EIS
The DOE Preferred Alternative identified in the 2002 EIS for waste
processing (including calcine) was to implement the proposed action by
selecting from among the action alternatives, options, and technologies
analyzed in the 2002 EIS. The selection of any one of, or combination
of, technologies or options used to implement the proposed action would
be based on the performance criteria of technical maturity,
environmental health and safety considerations, consideration of public
comment, cost, schedule, and programmatic risk. Options excluded from
DOE's preferred alternative were storage of calcine in bin sets for an
indefinite period of time (analyzed under the Continued Current
Operation Alternative), shipment of all calcine to the Hanford Site for
treatment (analyzed under the Minimum INEEL [now INL] Processing
Alternative), and disposal of mixed LLW at INL (analyzed under multiple
alternatives).
The State of Idaho Preferred Alternative identified in the 2002 EIS
for waste processing was the Direct Vitrification Alternative. The
State of Idaho preferred vitrification based on the belief that it was
the treatment alternative with the lowest technical and regulatory
uncertainty for meeting waste removal goals and providing a clear
baseline for fulfilling the objectives of removal of waste from Idaho
within the timelines envisioned by the Settlement Agreement. The State
of Idaho was willing to consider other waste treatment options, if they
were comparable or better than the Direct Vitrification Alternative in
terms of environmental impact, schedule, and/or cost.
IV. Environmentally Preferable Alternative
In nine of fourteen environmental areas analyzed, the 2002 EIS
indicates little or no environmental impact would occur under all of
the action alternatives. In the remaining five areas analyzed (air,
traffic and transportation, health and safety, waste and materials, and
facility accidents), the results indicate that potential short-term
impacts from routine exposures would be small and would not differ
significantly among action alternatives. Under normal operations, none
of the waste processing action alternatives analyzed in the EIS would
result in large short-term or long-term impacts to human health or the
environment. Also, none of the action alternatives would result in
appreciably different impacts on historic, cultural and natural
resources.
Any of the waste treatment alternatives that place the calcine in a
waste form suitable for disposition outside of the State of Idaho would
be environmentally preferable compared to the No Action and Continued
Current Operations Alternatives.
V. Decision
DOE has decided to deploy the HIP technology to cost-effectively
treat the calcine waste. This option also presents the flexibility to
either:
Treat calcine in a sealed high temperature and high
pressure canning process including the addition of treatment additives
necessary to produce a glass-ceramic and volume reduced monolithic
waste form; or
Treat calcine in a sealed high temperature and high
pressure canning process without addition of treatment additives
resulting in an even greater volume reduction.
The HIP technology deployed for the treatment of HLW calcine also
provides the technological capability to further treat the SBW steam-
reformed carbonate waste form, should such treatment be necessary in
order for this waste to be ready to leave Idaho by 2035 as required by
the 1995 Settlement Agreement.
Treatment using the HIP technology has been demonstrated to
generate a waste form consistent with waste form requirements that are
currently specified for the performance of single-phase borosilicate
glass being produced at DOE's Defense Waste Processing Facility at the
Savannah River Site and to be produced at the Waste Treatment Plant at
DOE's Hanford Site. The use of HIP with the addition of treatment
additives will be necessary to eliminate the RCRA hazardous waste
characteristics should calcine be
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dispositioned at a non-RCRA-permitted site outside the State of
Idaho.\2\
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\2\ Under this treatment option (HIP with additives), an
approved delisting petition would be required and any land disposal
restrictions would also have to be met.
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If it is decided to disposition calcine at a RCRA-permitted
facility outside the State of Idaho, the use of HIP without addition of
treatment additives would cost-effectively reduce the volume of waste
even further, resulting in fewer canisters of product to be ultimately
shipped for such disposition outside the State of Idaho.\3\
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\3\ Under this treatment option (HIP without treatment
additives), any land disposal restrictions would also have to be
met.
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DOE's decision will allow DOE to meet the provisions of the
Settlement Agreement for the treatment of all calcinated waste and, if
applicable, SBW.
To facilitate treatment, DOE has decided to retrieve and
pneumatically (forced air through piping) transport the calcine to a
surge tank located at the head end of the IWTU at such time as the
calcine treatment and packaging process is about to commence. The IWTU
facility, after completion of its SBW mission and suitable
reconfiguration, will be used to support treatment of the calcine and
other wastes and meet associated safety and seismic design basis
requirements.
In accordance with the Settlement Agreement, DOE will submit a
request for a Permit Modification to the Integrated Waste Treatment
Unit RCRA Part B Permit no later than December 1, 2012, that will
address:
Calcine retrieval and pneumatic transport of the retrieved
calcine to a designed surge tank to be located at the head end of the
IWTU facility, and
HIP treatment/processing of all calcine within a modified
IWTU facility.
DOE has consulted with the State of Idaho on the decisions
described herein. The State of Idaho concurs with DOE's selection of
HIP technology to treat calcine (and concurs that it provides the
technological capability to further treat the SBW steam-reformed
carbonate waste form, should such treatment be necessary) to produce a
glass ceramic and volume reduced monolithic waste form. This treatment
appears comparable to single-phase borosilicate glass resulting from
vitrification which was Idaho's previous preferred alternative. Idaho
prefers the HIP technology with the addition of treatment additives
because it is the most likely form to meet current regulatory
requirements allowing for disposal outside the State of Idaho. Idaho
does not object to the HIP technology without the addition of treatment
additives provided the final waste form is eligible for transport
outside the State of Idaho for storage or disposition. DOE will
continue to consult with the State on the decisions yet to be made
concerning the addition of treatment additives for the HIP treatment of
the calcine waste.
No environmental impacts resulting from operations under this
decision would require specific mitigation measures. DOE will, however,
use all practicable means to avoid or minimize environmental harm when
implementing the actions described in this amended ROD. Those measures
include employing engineering design features to ensure that calcine
waste processing via HIP is conducted safely and in accordance with all
applicable regulatory requirements. Other measures include maintaining
a rigorous health and safety program to protect workers from
radiological and chemical contaminants, monitoring worker and
environmental risk, and continuing efforts to reduce generation of
wastes. DOE will implement the comprehensive list of standards and
requirements to protect workers, the public, and the environment
specified in Chapter 6 of the Final EIS, as appropriate.
VI. Basis for Decision
DOE is selecting the HIP technology to treat calcine HLW for a
number of reasons. The HIP technology is anticipated to cost-
effectively treat the calcine waste, reduce the volume of the waste,
and place the waste in a form ready to be moved out of the State of
Idaho, consistent with the dates in the Settlement Agreement.
Issued in Washington, DC, on December 23, 2009.
In[eacute]s R. Triay,
Assistant Secretary for Environmental Management.
[FR Doc. E9-31151 Filed 12-31-09; 8:45 am]
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