Waste Confidence Decision Update, 59551-59570 [E8-23381]
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Regulatory Analysis
A draft regulatory analysis has not
been prepared for this proposed
regulation because this regulation does
not establish any requirements that
would place a burden on licensees.
Regulatory Flexibility Certification
Under the Regulatory Flexibility Act
of 1980, 5 U.S.C. 605(b), the
Commission certifies that this rule, if
adopted, would not have a significant
economic impact on a substantial
number of small entities. The proposed
rule would describe a revised basis for
continuing in effect the current
provisions of 10 CFR 51.23(b) which
provides that no discussion of any
environmental impact of spent fuel
storage in reactor facility storage pools
or ISFSIs for the period following the
term of the reactor operating license or
amendment or initial ISFSI license or
amendment for which application is
made is required in any environmental
report, environmental impact statement,
environmental assessment, or other
analysis prepared in connection with
certain actions. This rule affects only
the licensing and operation of nuclear
power plants or ISFSIs. Entities seeking
or holding Commission licenses for
these facilities do not fall within the
scope of the definition of ‘‘small
entities’’ set forth in the Regulatory
Flexibility Act or the size standards
established by the NRC at 10 CFR 2.810.
Backfit Analysis
The NRC has determined that the
backfit rule (§§ 50.109, 70.76, 72.62, or
76.76) does not apply to this proposed
rule because this amendment would not
involve any provisions that would
impose backfits as defined in the backfit
rule. Therefore, a backfit analysis is not
required.
List of Subjects in 10 CFR Part 51
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Administrative practice and
procedure, Environmental impact
statement, Nuclear materials, Nuclear
power plants and reactors, Reporting
and recordkeeping requirements.
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1. The authority citation for Part 51
continues to read as follows:
Authority: Sec. 161, 68 Stat. 948, as
amended, sec. 1701, 106 Stat. 2951, 2952,
2953, (42 U.S.C. 2201, 2297(f)); secs. 201, as
amended, 202, 88 Stat. 1242, as amended,
1244 (42 U.S.C. 5841, 5842); sec. 1704, 112
Stat. 2750 (44 U.S.C. 3504 note). Subpart A
also issued under National Environmental
Policy Act of 1969, secs. 102, 104, 105, 83
Stat. 853–854, as amended (42 U.S.C. 4332,
4334, 4335), and Public Law 95–604, Title II,
92 Stat. 3033–3041; and sec. 193, Public Law
101–575, 104 Stat. 2835 (42 U.S.C. 2243).
Sections 51.20, 51.30, 51.60, 41.80, and 51.97
also issued under secs. 135, 141, Public Law
97–425, 96 Stat. 2232, 2241, and sec. 148,
Public Law 100–203, 101 Stat. 1330–223 (42
U.S.C. 10155, 10161, 10168). Section 51.22
also issued under sec. 274, 73 Stat. 688, as
amended by 92 Stat. 3036–3038 (42 U.S.C.
2021) and under Nuclear Waste Policy Act of
1982, sec. 121, 96 Stat. 2228 (42 U.S.C.
10141). Sections 51.43, 51.67, and 51.109
also under Nuclear Waste Policy Act of 1982,
sec 114(f), 96 Stat 2216, as amended (42
U.S.C. 10134 (f)).
2. In § 51.23, paragraph (a) is revised
to read as follows:
§ 51.23 Temporary storage of spent fuel
after cessation of reactor operation—
generic determination of no significant
environmental impact.
(a) The Commission has made a
generic determination that, if necessary,
spent fuel generated in any reactor can
be stored safely and without significant
environmental impacts beyond the
licensed life for operation (which may
include the term of a revised or renewed
license) of that reactor at its spent fuel
storage basin or at either onsite or offsite
independent spent fuel storage
installations until a disposal facility can
reasonably be expected to be available.
*
*
*
*
*
Dated at Rockville, Maryland, this 29th day
of September 2008.
For the Nuclear Regulatory Commission.
Annette L. Vietti-Cook,
Secretary of the Commission.
[FR Doc. E8–23384 Filed 10–8–08; 8:45 am]
BILLING CODE 7590–01–P
NUCLEAR REGULATORY
COMMISSION
For the reasons set out in the
preamble and under the authority of the
Atomic Energy Act of 1954, as amended;
the Energy Reorganization Act of 1974,
as amended; and 5 U.S.C. 553, the NRC
is proposing to adopt the following
amendment to 10 CFR Part 51.
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PART 51—ENVIRONMENTAL
PROTECTION REGULATIONS FOR
DOMESTIC LICENSING AND RELATED
REGULATORY FUNCTIONS
10 CFR Part 51
[Docket ID–2008–0482]
Waste Confidence Decision Update
Nuclear Regulatory
Commission.
AGENCY:
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59551
Update and proposed revision
of Waste Confidence Decision.
ACTION:
SUMMARY: On September 18, 1990, the
Nuclear Regulatory Commission (NRC
or Commission) issued a decision
reaffirming and revising, in part, the five
Waste Confidence findings reached in
its 1984 Waste Confidence Decision.
The 1984 decision and the 1990 review
were products of rulemaking
proceedings designed to assess the
degree of assurance that radioactive
wastes generated by nuclear power
plants can be safely disposed of, to
determine when such disposal or offsite
storage would be available, and to
determine whether radioactive wastes
can be safely stored onsite past the
expiration of existing facility licenses
until offsite disposal or storage is
available. The Commission has decided
to again undertake a review of its Waste
Confidence findings as part of an effort
to enhance the efficiency of combined
operating license proceedings for
applications for nuclear power plants
anticipated in the near future. To assure
that its Waste Confidence findings are
up-to-date, the Commission has
prepared an update of the findings and
proposes to revise two of the findings.
The purpose of this notice is to seek
public comment on the update and the
proposed revisions.
The Commission proposes that the
second and fourth findings in the Waste
Confidence Decision be revised as
follows:
Finding 2: The Commission finds
reasonable assurance that sufficient
mined geologic repository capacity can
reasonably be expected to be available
within 50–60 years beyond the licensed
life for operation (which may include
the term of a revised or renewed license)
of any reactor to dispose of the
commercial high-level radioactive waste
and spent fuel originating in such
reactor and generated up to that time.
Finding 4: The Commission finds
reasonable assurance that, if necessary,
spent fuel generated in any reactor can
be stored safely without significant
environmental impacts for at least 60
years beyond the licensed life for
operation (which may include the term
of a revised or renewed license) of that
reactor in a combination of storage in its
spent fuel storage basin and either
onsite or offsite independent spent fuel
storage installations.
The Commission proposes to reaffirm
the remaining findings. Each finding,
any proposed revisions, and the reasons
for revising or reaffirming them are
discussed below. In keeping with the
proposed revised Findings 2 and 4, the
Commission is publishing concurrently
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in this issue of the Federal Register
proposed conforming amendments to its
10 CFR part 51 rule providing its
generic determination on the
environmental impacts of storage of
spent fuel at, or away from, reactor sites
after the expiration of reactor operating
licenses.
DATES: Submit comments by December
8, 2008. Comments received after this
date will be considered if it is practical
to do so, but NRC is able to assure
consideration only for comments
received on or before this date.
ADDRESSES: You may submit comments
by any one of the following methods.
Comments submitted in writing or in
electronic form will be made available
for public inspection. Because your
comments will not be edited to remove
any identifying or contact information,
the NRC cautions you against including
any information in your submission that
you do not want to be publicly
disclosed.
Federal e-Rulemaking Portal: Go to
https://www.regulations.gov and search
for documents filed under Docket ID
[NRC–2008–0482]. Address questions
about NRC dockets to Carol Gallagher
301–415–5905; e-mail
Carol.Gallagher@nrc.gov.
Mail comments to: Secretary, U.S.
Nuclear Regulatory Commission,
Washington, DC 20555–0001, ATTN:
Rulemakings and Adjudications Staff.
E-mail comments to:
Rulemaking.Comments@nrc.gov. If you
do not receive a reply e-mail confirming
that we have received your comments,
contact us directly at 301–415–1677.
Hand deliver comments to: 11555
Rockville Pike, Rockville, Maryland
20852, between 7:30 am and 4:15 pm
Federal workdays. (Telephone 301–415–
1677).
Fax comments to: Secretary, U.S.
Nuclear Regulatory Commission at 301–
415–1101.
You can access publicly available
documents related to this document
using the following methods:
NRC’s Public Document Room (PDR):
The public may examine and have
copied for a fee publicly available
documents at the NRC’s PDR, Public
File Area O1 F21, One White Flint
North, 11555 Rockville Pike, Rockville,
Maryland.
NRC’s Agencywide Documents
Access and Management System
(ADAMS): Publicly available documents
created or received at the NRC are
available electronically at the NRC’s
Electronic Reading Room at https://
www.nrc.gov/reading-rm/adams.html.
From this page, the public can gain
entry into ADAMS, which provides text
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and image files of NRC’s public
documents. If you do not have access to
ADAMS or if there are problems in
accessing the documents located in
ADAMS, contact the NRC’s PDR
reference staff at 1–800–397–4209, 301–
415–4737, or by e-mail to
pdr.resource@nrc.gov.
Neil
Jensen, Office of the General Counsel,
U.S. Nuclear Regulatory Commission,
Washington, DC 20555–0001, telephone
301–415–8480, e-mail,
neil.jensen@nrnc.gov.
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
Background
In October 1979, the NRC initiated a
rulemaking proceeding, known as the
Waste Confidence proceeding, to assess
its degree of assurance that radioactive
wastes produced by nuclear power
plants can be safely disposed of, to
determine when such disposal or offsite
storage will be available, and to
determine whether radioactive wastes
can be safely stored onsite past the
expiration of existing facility licenses
until offsite disposal or storage is
available (44 FR 1372; October 25,
1979). The Commission’s action
responded to a remand from the U.S.
Court of Appeals for the District of
Columbia Circuit in State of Minnesota
v. NRC, 602 F.2d 412 (1979). That case
raised the question whether an offsite
storage or disposal solution would be
available for the spent nuclear fuel
(SNF) produced at the Vermont Yankee
and Prairie Island reactors at the
expiration of the licenses for those
facilities in the 2007–2009 period or, if
not, whether the SNF could be stored at
those reactor sites until an offsite
solution was available. The Waste
Confidence proceeding also stemmed
from the Commission’s statement, in its
denial of a petition for rulemaking filed
by the Natural Resources Defense
Council (NRDC), that it intended to
reassess periodically its finding of
reasonable assurance that methods of
safe permanent disposal of high-level
radioactive waste (HLW) would be
available when they were needed.
Further, the Commission stated that, as
a matter of policy, it ‘‘would not
continue to license reactors if it did not
have reasonable confidence that the
wastes can and will in due course be
disposed of safely.’’ (42 FR 34391,
34393; July 5, 1977, pet. for rev.
dismissed sub nom. NRDC v. NRC, 582
F.2d 166 (2d Cir. 1978)).1
1 The NRDC petition asserted that the Atomic
Energy Act of 1954, as amended (AEA), required
NRC to make a finding, before issuing an operating
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The Waste Confidence proceeding
resulted in five Waste Confidence
findings which the Commission issued
August 31, 1984; 49 FR 34658:
(1) The Commission finds reasonable
assurance that safe disposal of HLW and
SNF in a mined geologic repository is
technically feasible;
(2) The Commission finds reasonable
assurance that one or more mined
geologic repositories for commercial
HLW and SNF will be available by the
years 2007–2009, and that sufficient
repository capacity will be available
within 30 years beyond the expiration of
any reactor operating license to dispose
of existing commercial HLW and SNF
originating in such reactor and
generated up to that time;
(3) The Commission finds reasonable
assurance that HLW and SNF will be
managed in a safe manner until
sufficient repository capacity is
available to assure the safe disposal of
all HLW and SNF;
(4) The Commission finds reasonable
assurance that, if necessary, spent fuel
generated in any reactor can be stored
safely and without significant
environmental impacts for at least 30
years beyond the expiration of that
reactor’s operating license at that
reactor’s spent fuel storage basin, or at
either onsite or offsite independent
spent fuel storage installations (ISFSIs);
(5) The Commission finds reasonable
assurance that safe independent onsite
or offsite spent fuel storage will be made
available if such storage capacity is
needed.
Based on these findings, the
Commission amended 10 CFR part 51 of
its regulations to provide a generic
determination, codified in 10 CFR
51.23(a), that for at least 30 years
beyond the expiration of reactor
operating licenses, no significant
environmental impacts will result from
the storage of spent fuel in reactor
facility storage pools or ISFSIs located at
reactor or away-from-reactor sites.
The Commission conducted a review
of its findings in 1989–1990 which
resulted in the revision of the second
and fourth findings to reflect revised
expectations for the date of availability
of the first repository, and to clarify that
the expiration of a reactor’s operating
license referred to the full 40 year initial
license for operation, as well as any
additional term of a revised or renewed
license. These findings are:
license for a reactor, that permanent disposal of
HLW generated by that reactor can be accomplished
safely. The Commission found that the AEA did not
require this safety finding to be made in the context
of reactor licensing, but rather in the context of the
licensing of a geologic disposal facility.
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(2) The Commission finds reasonable
assurance that at least one mined
geologic repository will be available
within the first quarter of the twentyfirst century, and sufficient repository
capacity will be available within 30
years beyond the licensed life for
operation (which may include the term
of a revised or renewed license) of any
reactor to dispose of the commercial
HLW and SNF originating in such
reactor and generated up to that time;
(4) The Commission finds reasonable
assurance that, if necessary, spent fuel
generated in any reactor can be stored
safely and without significant
environmental impacts for at least 30
years beyond the licensed life for
operation (which may include the term
of a revised or renewed license) of that
reactor at its spent fuel storage basin, or
at either onsite or offsite ISFSIs.
The Commission amended the generic
determination made in 10 CFR 51.23(a)
consistent with these revised findings
(55 FR 38472; September 18, 1990):
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The Commission has made a generic
determination that, if necessary, spent fuel
generated in any reactor can be stored safely
and without significant environmental
impacts for at least 30 years beyond the
licensed life for operation (which may
include the term of a revised or renewed
license) of that reactor at its spent fuel
storage basin or at either onsite or offsite
[ISFSIs]. Further, the Commission believes
there is reasonable assurance that at least one
mined geologic repository will be available
within the first quarter of the twenty-first
century, and sufficient repository capacity
will be available within 30 years beyond the
licensed life for operation of any reactor to
dispose of the commercial [HLW and SNF]
originating in such reactor and generated up
to that time.
This generic determination is applied in
licensing proceedings conducted under
10 CFR Parts 50, 52, 54 and 72. See 10
CFR 51.23 (2008).
In 1999, the Commission reviewed its
Waste Confidence findings and
concluded that experience and
developments since 1990 had confirmed
the findings and made a comprehensive
reevaluation of the findings
unnecessary. It also stated that it would
consider undertaking such a
reevaluation when the impending
repository development and regulatory
activities run their course or if
significant and pertinent unexpected
events occur, raising substantial doubt
about the continuing validity of the
Waste Confidence findings (64 FR
68005; December 6, 1999).
The Commission does not believe that
the criteria set in 1999 for reopening the
Waste Confidence findings have been
met. However, the Commission is now
preparing to conduct a significant
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number of proceedings on combined
construction permit and operating
license (COL) applications for new
reactors. The Commission anticipates
that the issue of waste confidence may
be raised in those proceedings and
desires to take a fresh look at its Waste
Confidence findings to take into account
developments since 1990. For this
purpose, the Commission has prepared
this update of the Waste Confidence
findings and now proposes the
following revisions of Findings 2 and 4:
(2) The Commission finds reasonable
assurance that sufficient mined geologic
repository capacity can reasonably be
expected to be available within 50–60
years beyond the licensed life for
operation (which may include the term
of a revised or renewed license) of any
reactor to dispose of the commercial
HLW and SNF originating in such
reactor and generated up to that time.
(4) The Commission finds reasonable
assurance that, if necessary, spent fuel
generated in any reactor can be stored
safely and without significant
environmental impacts for at least 60
years beyond the licensed life for
operation (which may include the term
of a revised or renewed license) of that
reactor in a combination of storage in its
spent fuel storage basin and either
onsite or offsite ISFSIs.
The update restates and supplements
the bases for the earlier findings. The
Commission seeks public comment on
the update and on its proposed
revisions of Findings 2 and 4.
The Commission is also publishing
concurrently in this issue of the Federal
Register a proposed rule revising 10
CFR 51.23(a) to conform with the
proposed revisions of Findings 2 and 4.
I. Finding 1: The Commission Finds
Reasonable Assurance That Safe
Disposal of High-Level Radioactive
Waste and Spent Fuel in a Mined
Geologic Repository Is Technically
Feasible
A. Bases for Finding 1
The Commission reached this finding
in 1984 and reaffirmed it in 1990. The
focus of this finding is on whether safe
disposal of HLW and SNF is technically
possible using existing technology and
without a need for any fundamental
breakthroughs in science and
technology. To reach this finding, the
Commission considered the basic
features of a repository designed for a
multi-barrier system for waste isolation
and examined the problems the
Department of Energy (DOE) would
need to resolve in developing a final
design for such a repository. The
Commission identified three major
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technical problems: (1) The selection of
a suitable geologic setting as host for a
technically acceptable repository site;
(2) the development of waste packages
that will contain the waste until the
fission products are greatly reduced;
and (3) the development of engineered
barriers, such as backfilling and sealing
of the drifts and shafts of the repository,
that can effectively retard migration of
radionuclides out of the repository (49
FR 34667; August 31, 1984).
DOE’s selection of a suitable geologic
setting has been governed by Congress’
passage of the Nuclear Waste Policy Act
of 1982, Public Law 97–425, 42 U.S.C.
10101 et seq. (NWPA) and by the 1987
amendments to NWPA in the Nuclear
Waste Policy Amendments Act, Pub. L.
100–202 (NWPAA). DOE had begun to
explore potential repository sites before
the NWPA, but that Act set in place a
formal process and schedule for the
development of two geologic
repositories. The following brief
summary of key provisions of these Acts
may assist readers in understanding the
process followed by DOE in locating a
suitable geologic setting.
As initially enacted, NWPA directed
DOE to issue guidelines for the
recommendation of sites and then to
nominate at least 5 sites as being
suitable for site characterization for
selection as the first repository site and,
not later than January 1, 1985, to
recommend 3 of those sites to the
President for characterization as
candidate sites. Section 112 of NWPA,
42 U.S.C. 10132. Not later than July 1,
1989, DOE was to again nominate 5 sites
and recommend 3 of them to the
President for characterization for
selection of the second repository. Id.
DOE was then to carry out site
characterization activities for approved
sites. Section 113 of NWPA, 42 U.S.C.
10133. Following site characterization,
DOE was then to recommend sites to the
President as suitable for development as
repositories and the President was to
recommend one site to the Congress by
March 31, 1987, and another site by
March 31, 1989, for development as the
first two repositories. Section 114 of
NWPA, 42 U.S.C. 10134. States and
affected Indian tribes were given the
opportunity to object, but if the
recommendations were approved by
Congress, DOE was then to submit
applications for a construction
authorization to NRC. Id. NRC was
given until January 1, 1989, to reach a
decision on the first application and
until January 1, 1992, on the second.
The Commission was directed to
prohibit the emplacement in the first
repository of more than 70,000 metric
tons of heavy metal (MTHM) until a
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second repository was in operation. Id.
The 1987 NWPAA, inter alia, restricted
site characterization solely to a site at
Yucca Mountain, NV (YM) and
terminated the program for a second
repository. The NWPAA provided that if
DOE at any time determines YM to be
unsuitable for development as a
repository, DOE must report to Congress
its recommendations for further action
to assure the safe, permanent disposal of
SNF and HLW, including the need for
new legislation. Section 113 of NWPA,
as amended, 42 U.S.C. 10133.
In 1984, the Commission reviewed
DOE’s site exploration program and
concluded that it was providing
information on site characteristics at a
sufficiently large number and variety of
sites and geologic media to support the
expectation that one or more technically
acceptable sites would be identified (49
FR 34668; August 31, 1984). In 1990, the
Commission noted that the 1987
amendment of NWPA that focused
solely on the YM site carried the
potential for considerable delay in
opening a repository if that site were
found to be unlicenseable. However, the
possibility of that delay did not
undermine the Commission’s
confidence that a technically acceptable
site would be located, either at YM or
elsewhere. The Commission observed
that the NRC staff had provided
extensive comments on DOE’s draft
environmental assessments of the 9 sites
it had identified as being potentially
acceptable and on the final
environmental assessments for the 5
sites nominated.2 NRC had not
identified any fundamental technical
flaw or disqualifying factor which
would render any of the sites unsuitable
for characterization or potentially
unlicenseable, although NRC noted that
many issues would need to be resolved
during site characterization for YM or
any other site (55 FR 38486; September
18, 1990).
With respect to the development of
effective waste packages, the
Commission, in 1984, reviewed DOE’s
scientific and engineering program on
this subject. The Commission also
considered whether the possibility of
renewed reprocessing of SNF might
alter the technical feasibility of
achieving a suitable waste package
because of the need to accommodate a
waste form other than spent fuel. The
Commission concluded that the studies
of DOE and others demonstrated that
2 Under the program established by the initial
NWPA, DOE had nominated sites at Hanford WA,
Yucca Mountain NV, Deaf Smith County TX, Davis
Canyon UT, and Richton Dome MS, and had
recommended the first 3 sites for site
characterization.
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the chemical and physical properties of
SNF and HLW can be sufficiently
understood to permit the design of a
suitable waste package and that the
possibility of commercial reprocessing
would not substantially affect this
conclusion (49 FR 34671; August 31,
1984). In 1990, the Commission
reviewed continued research and
experimentation on waste packages that
were undertaken by DOE in other
countries, particularly Sweden and
Canada. NRC noted that DOE had
narrowed the range of waste package
designs to a design tailored for
unsaturated tuff at the YM site due to
the 1987 redirection of the HLW
program. NRC also noted that some
reprocessing wastes from the defense
program and the West Valley
Demonstration Project were now
anticipated to be disposed in the
repository. However, NRC remained
confident that, given a range of waste
forms and conservative test conditions,
the technology is available to design
acceptable waste packages (55 FR
38489; September 18, 1990).
With respect to the development of
effective engineered barriers, the
Commission’s confidence in 1984 rested
upon its consideration of DOE’s ongoing
research and development activities
regarding backfill materials and
borehole and shaft sealants which led it
to the conclusion that these activities
provided a basis for reasonable
assurance that engineered barriers can
be developed to isolate or retard
radioactive material released by the
waste package (49 FR 34671; August 31,
1984). In 1990, although DOE’s research
had narrowed to focus on YM, the
Commission continued to have
confidence that backfill or packing
materials can be developed as needed
for the underground facility and waste
package, and that an acceptable seal can
be developed for candidate sites in
different geologic media (55 FR 38489–
38490; September 18, 1990).
B. Evaluation of Finding 1
There remains high confidence among
the scientific and technical community
engaged in waste management that safe
geologic disposal is achievable with
currently available technology. See, e.g.,
National Research Council, ‘‘Technical
Bases for Yucca Mountain Standards,’’
1995. No insurmountable technical or
scientific problem has emerged to
disturb this confidence that safe
disposal of SNF and HLW can be
achieved in a mined geologic repository.
To the contrary, there has been
significant progress in the enhancement
of scientific understanding and
technological development needed for
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geologic disposal over the past 18 years.
There is now a much deeper
understanding of processes that affect
the ability of repositories to isolate
waste over long periods. Id. at 71–72;
International Atomic Energy Agency
(IAEA), ‘‘Scientific and Technical Basis
for the Geologic Disposal of Radioactive
Wastes, Technical Reports Series No.
413,’’ 2003. The ability to characterize
and quantitatively assess the
capabilities of geologic and engineered
barriers has been repeatedly
demonstrated. NRC, ‘‘Disposal of HighLevel Radioactive Wastes in a Proposed
Geologic Repository at Yucca Mountain,
Nevada; Proposed Rule,’’ (64 FR 8640,
8649; February 22, 1999); Organization
for Economic Cooperation and
Development, Nuclear Energy Agency,
‘‘Lessons Learned from Ten
Performance Assessment Studies,’’
1997. Specific sites have been
investigated and extensive experience
has been gained in underground
engineering. IAEA, ‘‘Radioactive Waste
Management Studies and Trends, IAEA/
WMDB/ST/4,’’ 2005; IAEA, ‘‘The Use of
Scientific and Technical Results from
Underground Research Laboratory
Investigations for the Geologic Disposal
of Radioactive Waste, IAEA–TECDOC–
1243,’’ 2001. These advances and others
throughout the world, in underground
research laboratories, continue to
confirm the soundness of the basic
concept of deep geologic disposal.
IAEA, ‘‘Joint Convention on Safety of
Spent Fuel Management and on Safety
of Radioactive Waste Management,
INFCIRC/546,’’ 1997.
In the United States, the technical
approach for safe HLW disposal has
remained unchanged for several
decades: Use a deep geologic repository
containing natural barriers to hold
canisters of HLW with additional
engineered barriers to further retard
radionuclide release. Although some
specifics in this technical approach
have changed in response to new
knowledge (e.g., engineered backfill was
removed as a design concept for YM in
the late 1990s in response to enhanced
understandings of heat and water
transfer processes in the near-field drift
environment), safe disposal continues to
appear to be a feasible goal with current
technology. Assessments for long-term
performance of a potential repository at
YM were conducted by DOE in 1998
(DOE/RW–0508, Viability Assessment)
and 2002 (DOE/RW–0539, Site
Recommendation). These assessments
used existing technology and available
scientific information, and did not
identify areas where fundamental
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breakthroughs in science or technology
were needed to support the assessments.
With respect to the issue of
identifying a suitable geologic setting as
host for a technically acceptable site,
DOE made its suitability determination
for the YM site in 2002. On June 3,
2008, DOE submitted the application to
NRC and on September 08, 2008, NRC
Staff notified DOE that it found the
application acceptable for docketing (73
FR 53284; September 15, 2008).
Whether this particular site will be
found to be technically acceptable must
await the outcome of an NRC licensing
proceeding. The 1987 amendments to
NWPA barred DOE from continuing site
investigations elsewhere within the U.S.
However, Congress’ decision to focus
solely on YM was not based on any
finding that information DOE had
obtained on other sites ruled them out
for technical reasons; rather, the
decision was aimed at controlling the
costs of the HLW program (55 FR 38486;
September 18, 1990). Repository
programs in other countries are actively
considering crystalline rock, clay
formations, and salt formations as
repository host media. IAEA,
‘‘Radioactive Waste Management Status
and Trends, IAEA/WMDB/ST/4,’’ 2005;
IAEA, ‘‘The Use of Scientific and
Technical Results from Underground
Research Laboratory Investigations for
the Geologic Disposal of Radioactive
Waste, IAEA–TECDOC–1243,’’ 2001.
Many of these programs have been
conducting research on these geologic
media for several decades. Although
there are relative strengths to the
capabilities of each of these potential
host media, no geologic media
previously identified as a candidate host
has been ruled out based on technical or
scientific information. Salt formations
currently are being considered as hosts
only for reprocessed nuclear materials
because heat-generating waste, like
spent nuclear fuel, exacerbates a process
by which salt can rapidly deform. This
process could potentially cause
problems for keeping drifts stable and
open during the operating period of a
repository.
In 2001, NRC amended its regulations
to include a new 10 CFR Part 63,
‘‘Disposal of High-Level Radioactive
Wastes in a Geologic Repository at
Yucca Mountain, Nevada,’’ (66 FR
55732; November 2, 2001), which
requires use of both natural and
engineered barriers to meet overall total
system performance objectives without
pre-determined subsystem performance
requirements, such as substantially
complete containment for a waste
package, as is required in 10 CFR Part
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60.3 Accordingly, U.S. research and
development activities have focused on
understanding the long-term capability
of natural and engineered barriers
which can prevent or substantially
reduce the release rate of radionuclides
from a potential repository system.
Although the performance of individual
barriers may change through time, the
overall performance of the total system
is required to be acceptable throughout
the performance period for the
repository. In this context of total
system performance, research and
development has supported the view
that it appears technically possible to
design and construct a waste package
and an engineered barrier system that,
in conjunction with natural barriers,
could prevent or substantially reduce
the release rate of radionuclides from a
potential repository system during the
performance period. NRC, ‘‘Disposal of
High-Level Radioactive Wastes in a
Proposed Geologic Repository at Yucca
Mountain, Nevada; Proposed Rule,’’ (64
FR 8649; February 22, 1999); IAEA,
‘‘Joint Convention on Safety of Spent
Fuel Management and on Safety of
Radioactive Waste Management,
INFCIRC/546,’’ 1997.
Since the Commission last considered
Waste Confidence issues, NRC has
issued design certifications under its
regulations at 10 CFR Part 52, ‘‘Early
Site Permits; Standard Design
Certifications; and Combined Licenses
for Nuclear Power Plants,’’ and is
currently reviewing several plant
designs in response to applications for
design certifications and for COL
applications that reference designs
under review or designs previously
certified. These facilities would use the
same or similar fuel assembly designs as
the nuclear power plants currently
operating in the United States. A need
for possible design changes for
repository disposal may be affected by
the extent of a licensee’s reliance on
cladding or fuel type as a barrier to
waste isolation. If limited reliance is
placed on the barrier capabilities of
cladding or fuel type in a demonstration
of compliance with repository safety
requirements, then minimal design
changes may be needed to accommodate
new types of SNF or cladding. As such,
the new reactor designs and specific
3 NRC’s regulations at 10 CFR Part 63 apply only
to the proposed repository at YM. NRC’s regulations
at 10 CFR Part 60, ‘‘Disposal of High-Level
Radioactive Wastes in Geologic Repositories,’’
govern the licensing of any repository other than
one located at YM. However, at the time Part 63 was
proposed, the Commission indicated it would
consider revising Part 60 if it seemed likely to be
used in the future. 64 FR 8640, 8643; February 22,
1999.
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license applications currently under
review would not raise issues as to the
technical feasibility of repository
disposal.
NRC is also engaged in preliminary
interactions with DOE and possible
reactor vendors proposing advanced
reactor designs that are different from
the currently operating light-water
reactors. Some of these advanced
reactors use gas-cooled or liquid metal
cooled technologies and have fuel and
reactor components that might require
different transportation and storage
containers. Geometric, thermal, and
criticality constraints could conceivably
require a design modification to
disposal containers from that currently
proposed for YM. Nevertheless, the
technical requirements for disposal of
advanced reactor components appear
similar to the requirements for disposal
of components for current light water
reactors. For example, DOE currently
plans to dispose of spent fuel at YM
from both gas-cooled (Peach Bottom 1)
and liquid-metal cooled (Fermi 1)
reactors, using the same basic
technological approach as for other
SNF. Although radionuclide inventory,
fuel matrix, and cladding characteristics
for advanced fuels might be distinct
from current light-water reactors, the
safe disposal of advanced fuel appears
to involve the same scientific and
engineering knowledge as used for fuel
from current light-water reactors.
There is currently a high uncertainty
regarding the growth of advanced
reactors in the U.S. The licensing
strategy developed by NRC and DOE for
the next generation nuclear plant
(NGNP) program found that an
aggressive licensing approach may lead
to operation of a prototype facility in
2021. Based on comparison with current
disposal strategies for fuel from existing
gas cooled or liquid-metal cooled
reactors, NRC is confident that current
technology appears to be adequate to
support the safe disposal of spent fuel
from a potential prototype facility. In
addition to the NGNP activities related
to the prototype reactor, various
activities, such as DOE’s Advanced Fuel
Cycle Initiative, are underway to
evaluate fuel cycle alternatives that
could affect the volume and form of
waste from the prototype reactor or
other advanced nuclear reactor designs.
The need to consider waste disposal as
part of the overall research and
development activities for advanced
reactors is recognized and included in
the activities of designers, DOE and
NRC. See, e.g., DOE Nuclear Energy
Research Advisory Committee and the
Generation IV International Forum, ‘‘A
Technology Roadmap for Generation IV
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Nuclear Energy Systems,’’ December
2002.
Based on the information described
previously, the Commission proposes to
reaffirm Finding 1.
II. Finding 2 (1990): The Commission
Finds Reasonable Assurance That at
Least One Mined Geologic Repository
Will Be Available Within the First
Quarter of the Twenty-First Century,
and That Sufficient Repository
Capacity Will Be Available Within 30
Years Beyond the Licensed Life for
Operation (Which May Include the
Term of a Revised or Renewed License)
of Any Reactor To Dispose of the
Commercial High-Level Radioactive
Waste and Spent Fuel Originating in
Such Reactor and Generated Up to That
Time
jlentini on PROD1PC65 with PROPOSALS
A. Bases for Finding 2
The dual objectives of this finding are
to predict when a repository will be
available for use and to predict how
long spent fuel may need to be stored
at a reactor site until repository space is
available for the spent fuel generated at
that reactor. With respect to the first
prediction, the Commission’s focus in
1984 was on the years 2007–2009, the
years during which the operating
licenses for the Vermont Yankee and
Prairie Island nuclear power plants
would expire.4 In 1984, DOE anticipated
that the first repository would begin
operation in 1998 and the second in
2004. However, NRC concluded that
technical and institutional uncertainties
made it preferable to focus on the 2007–
2009 time period. The technical
uncertainties involved the questions of
how long it would take DOE to locate
a suitable geologic setting for a
potentially technically acceptable
repository and how long it would take
to develop an appropriate waste package
and engineered barriers. The
Commission expressed the view that
despite early delays DOE’s program was
on track and, under the impetus given
by the recently-enacted NWPA, would
timely resolve the technical problems
(49 FR 34674–34675; August 31, 1984).
The Commission also identified
institutional uncertainties that needed
to be resolved: (1) Measures for dealing
with Federal-state disputes; (2) An
assured funding mechanism that would
be sufficient over time to cover the
4 Under the court remand which precipitated the
initial waste confidence review, NRC was required
to consider whether there was reasonable assurance
that an offsite storage solution would be available
by the years 2007–2009 and, if not, whether there
was reasonable assurance that the spent fuel could
be stored safely at those sites beyond those dates.
See State of Minnesota v. NRC, 602 F.2d 412, 418
(DCDC Cir. 1979).
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period for developing a repository; (3)
An organizational capability for
managing the HLW program; and (4) A
firm schedule and establishment of
responsibilities. The Commission
expressed its confidence in the ability of
the provisions of the then recentlypassed NWPA to timely resolve these
uncertainties (49 FR 34675–34679;
August 31, 1984).
With respect to the second prediction,
NRC reviewed DOE’s estimates of the
amount of installed generating capacity
of commercial nuclear power plants in
the year 2000 and concluded that the
total amount of spent fuel that would be
produced during the operating lifetimes
of these reactors would likely be about
160,000 MTHM. To accommodate this
amount, NRC assumed that two
repositories would be needed. NRC
calculated that if the first repository
began to receive SNF in 2005, and the
second in 2008, then all the SNF would
be emplaced by about 2026. This would
mean that sufficient repository capacity
would be available within 30 years
beyond the expiration of any reactor
license for disposal of its SNF (49 FR
34679; August 31, 1984).
In reviewing these predictions in
1990, the Commission faced a
considerably changed landscape. First,
DOE’s schedule for the availability of a
repository had slipped several times so
that its then-current projection was
2010. Second, Congress’ 1987
amendment of NWPA had confined site
characterization to the YM site, meaning
that there were no ‘‘back-up’’ sites being
characterized in case the YM site should
be found unsuitable or unlicenseable.
Finally, site characterization activities at
YM had not proceeded without
problems, notably in DOE’s schedule for
sub-surface exploration and in
development of its quality assurance
program. Given these considerations,
the Commission found it would not be
prudent to reaffirm its confidence in the
availability of a repository in the 2007–
2009 period (55 FR 38495; September
18, 1990).
Instead, the Commission found that it
would be reasonable to assume that
DOE could make its finding whether
YM was suitable for development of a
repository by the year 2000. The
Commission was unwilling to assume
that DOE would make a finding of
suitability (which would be necessary
for a repository to be available by 2010).
To establish a new time-frame for
repository availability, the Commission
made the assumption that DOE would
find the YM site unsuitable by the year
2000 and that (as DOE had estimated) it
would take 25 years for a repository to
become available at a different site.
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The Commission then considered
whether it had sufficient bases for
confidence that a repository would be
available by 2025 using the same
technical and institutional criteria it had
used in 1984. The Commission found no
reason to believe that another
potentially technically acceptable site
could not be located if the YM site were
found unsuitable. The development of a
waste package and engineered barriers
was tied up with the question of the
suitability of the YM site but NRC found
no reason to believe that a waste
package and engineered barriers could
not be developed for a different site by
2025, if necessary (55 FR 38495;
September 18, 1990). The institutional
uncertainties were perhaps more
difficult to calculate. The Commission
acknowledged that DOE’s efforts to
address the concerns of States, local
governments and Indian tribes had met
with mixed results. Nevertheless, the
Commission retained its confidence that
NWPA, as amended, had achieved the
proper balance between providing for
participation by affected parties and
providing for the exercise of
Congressional authority to carry out the
national program for waste disposal (55
FR 38497; September 18, 1990).
Similarly, the Commission believed that
management and funding issues had
been adequately resolved by NWPA, as
amended, and would not call into
question the availability of a repository
by 2025 (55 FR 38497–38498;
September 18, 1990). Thus, except for
the schedule, the Commission was
confident that the HLW program set
forth in the amended NWPA would
ultimately be successful.
The Commission also considered
whether the termination of activities for
a second repository, combined with the
70,000 MTHM limit for the first
repository, together with its new
projection of 2025 as the time for the
availability for a repository, undermined
its prediction that sufficient repository
capacity would be available within 30
years beyond expiration of any reactor
operating license to dispose of the SNF
originating in such reactor and
generated up to that time (55 FR 38501–
38504; September 18, 1990). The
Commission noted that almost all
reactor licenses would not expire until
some time in the first three decades of
the twenty-first century and license
renewal was expected to extend the
terms of some of these licenses. Thus, a
repository was not needed by 2007–
2009 to provide disposal capacity
within 30 years beyond expiration of
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most operating licenses.5 The
Commission acknowledged, however,
that it appeared likely that two
repositories would be needed to dispose
of all the SNF and HLW from the
current generation of reactors unless
Congress provided statutory relief from
the 70,000 MTHM limit for the first
repository and unless the first repository
had adequate capacity to hold all the
SNF and HLW generated. This was
because DOE’s spent fuel projections, in
1990, called for 87,000 MTHM to have
been generated by the year 2036. In
addition, DOE’s projections were based
on the assumption of no new reactor
orders. The Commission believed that
that assumption probably
underestimated the total spent fuel
discharges to be expected due to the
likelihood of reactor license renewals.
The Commission expressed the belief
that if the need for a second repository
was established, Congress would
provide the needed institutional support
and funding, as it had for the first
repository.6 The Commission reasoned
that if work began on the second
repository program in 2010, that
repository could be available by 2035.
Two repositories available in
approximately 2025 and 2035, each
with acceptance rates of 3400 MTHM/
year within several years after
commencement of operations, would
provide assurance that sufficient
repository capacity will be available
within 30 years of operating license
expiration for reactors to dispose of the
spent fuel generated at their sites up to
that time. The Commission concluded
that a second repository, or additional
capacity at the first repository, would be
needed only to accommodate the
additional quantity of spent fuel
generated during the later years of
reactors operating under a renewed
license. The Commission stated that the
availability of a second repository
would permit spent fuel to be shipped
offsite well within 30 years after
expiration of these reactors’ operating
licenses and that the same would be
true of the spent fuel discharged from
any new generation of reactor designs
(55 FR 38503–38504; September 18,
1990).
5 NRC identified Dresden 1, licensed in 1959, as
the earliest licensed power reactor and noted that
30 years beyond its licensed life for operation
would be 2029 and that it was possible, if a
repository were to become available by 2025, for all
the Dresden 1 SNF to be removed from that facility
by 2029 (55 FR 38502; September 18, 1991).
6 DOE is statutorily required to report to the
President and to Congress on the need for a second
repository between January 1, 2007 and January 1,
2010. Section 161 of NWPA, as amended, 42 U.S.C.
10172a. DOE intends to submit the report in 2008.
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The Commission acknowledged that
there were several licenses that had
been prematurely terminated where it
was possible that SNF would be stored
more than 30 years beyond the effective
expiration of the license and that there
could be more of these premature
terminations. However, the Commission
remained confident that in these cases,
the overall safety and environmental
impacts of extended spent fuel storage
would be insignificant. The Commission
had found that spent fuel could be
safely stored for at least 100 years
(Finding 4), 7 and that spent fuel in atreactor storage would be safely
maintained until disposal capacity at a
repository was available (Finding 3).
The Commission emphasized that it had
not identified a date by which a
repository must be available for health
and safety reasons. The Commission
found that in effect, under the second
part of Finding 2, safe management and
safe storage would not need to continue
for more than 30 years beyond
expiration of any reactor’s operating
license because sufficient repository
capacity was expected to become
available within those 30 years (55 FR
38504; September 18, 1990).
B. Evaluation of Finding 2
As explained previously, the
Commission based its estimate in 1990
on the premise that at least one geologic
repository would be available within the
first quarter of the twenty-first century
on an assumption that DOE would make
its suitability determination under
section 114 of NWPA around the year
2000. To avoid being put in the position
of assuming the suitability of the YM
site, the Commission then assumed that
DOE would find that site unsuitable
and, as DOE had estimated, that it
would take 25 years before a repository
could become available at an alternate
site.
DOE made its suitability
determination in early 2002 and found
the YM site suitable for development as
a repository.8 Although DOE’s
7 The Commission conservatively assumed that
licenses would be renewed for 30 year terms (55 FR
38503; September 18, 1990). Thus, the initial 40
year term of the operating license, plus 30 years for
the renewed operating license term and 30 years
beyond the expiration of the renewed license
amounts to storage for at least 100 years.
8 On February 14, 2002, the Secretary of Energy
recommended the YM site for the development of
a repository to the President thereby setting in
motion the approval process set forth in sections
114 and 115 of the NWPA. See 42 U.S.C.
10134(a)(1); 10134(a)(2); 10135(b), 10136(b)(2). On
February 15, 2002, the President recommended the
site to Congress. On April 8, 2002, the State of
Nevada submitted a notice of disapproval of the site
recommendation to which Congress responded, on
July 9, 2002, by passing a joint resolution approving
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59557
application for a construction
authorization for a repository was
considerably delayed from the schedule
set out in NWPA, 9 on June 3, 2008, DOE
submitted the application to NRC and
on September 08, 2008, NRC Staff
notified DOE that it found the
application acceptable for docketing (73
FR 53284; September 15, 2008). DOE’s
current estimate of the best achievable
date for opening of the YM repository,
assuming it is licensed, is 2020. At the
hearing before the Subcommittee on
Energy and Air Quality of the House
Committee on Energy and Commerce
held on July 15, 2008, Edward F. Sproat
III, Director of DOE’s Office of Civilian
Radioactive Waste Management
(OCRWM), informed the Congress that
DOE could be ready to begin accepting
SNF by 2020, but only if adequate
funding is provided.
The NWPA process thus remains on
track for making available a geologic
repository for the disposal of SNF and
HLW. DOE’s projection of a date for
repository availability has moved from
2010 in 1990 to 2020 today and could
slip further. Even with some slippage in
DOE’s schedule, it remains possible that
a repository will be available by 2025.
Of course, now the only repository that
could become available by 2025 is the
proposed repository at YM and it will
only become available if the
Commission issues a construction
authorization and a subsequent
authorization to receive and possess
HLW. In 2005, the State of Nevada filed
a petition for rulemaking with NRC
(PRM–51–8) which raised the question
whether continued use of the 2025 date,
in effect, indicated prejudgment of the
outcome of any licensing proceeding
that might be held. The Commission
rejected this notion in its denial of the
petition:
Even if DOE’s estimate as to when it will
tender a license application should slip
further, the 2025 date would still allow for
unforeseen delays in characterization and
licensing. It also must be recognized that the
Commission remains committed to a fair and
comprehensive adjudication and, as a result,
there is the potential for the Commission to
deny a license for the Yucca Mountain site
based on the record established in the
adjudicatory proceeding. That commitment is
not jeopardized by the 2025 date for
repository availability. The Commission did
not see any threat to its ability to be an
the development of a repository at YM which the
President signed on July 23, 2002. See Pub. L. No.
107–200, 116 Stat. 735 (2002) (codified at 42 U.S.C.
10135 note (Supp. IV 2004)).
9 Section 114(b) of NWPA directs the Secretary of
Energy to submit a construction authorization
application to NRC within 90 days of the date the
site designation becomes effective. 42 U.S.C.
10134(b).
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impartial adjudicator in 1990 when it
selected the 2025 date even though then, as
now, a repository could only become
available if the Commission’s decision is
favorable. Should the Commission’s decision
be unfavorable and should DOE abandon the
site, the Commission would need to
reevaluate the 2025 availability date, as well
as other findings made in 1990. State of
Nevada; Denial of a Petition for Rulemaking
(70 FR 48329, 48333; August 17, 2005).
jlentini on PROD1PC65 with PROPOSALS
In the absence of an unfavorable NRC
decision and DOE’s abandonment of the
site, the Commission found no reason to
reopen its Waste Confidence findings.
However, the Commission has now
considered the recommendations of the
Combined License Review Task Force
Report and, in its June 22, 2007, Staff
Requirements Memorandum (SRM) on
that report, has approved rulemaking to
resolve generic issues associated with
combined license applications. SRM—
COMDEK–07–0001/COMJSM–07–
0001—Report of the Combined License
Review Task Force (ML071760109). In a
subsequent SRM of September 7, 2007,
the Commission expressed the view that
a near-term update to the Waste
Confidence findings was appropriate.
SRM—Periodic Briefing on New Reactor
Issues (ML072530192). The staff, in its
response to these SRMs, recognized that
there would likely be long-term
inefficiencies in combined license
application proceedings, due to the
need to respond to potential questions
and petitions directed to the existing
Waste Confidence Decision, and
committed to evaluate possible updates
to the decision.10 See memorandum
from Luis A. Reyes to the
Commissioners, ‘‘Rulemakings that Will
Provide the Greatest Efficiencies to
Complete the Combined License
Application Reviews in a Timely
Manner,’’ December 17, 2007, at 3
(ML073390094). Undertaking a public
rulemaking proceeding now to consider
revisions to the Waste Confidence
findings and rule—rather than waiting
until some point closer to the 2025
date—will allow sufficient time to
10 Challenges to 10 CFR 51.23 in individual COL
proceedings would likely be addressed through
application of 10 CFR 2.335, ‘‘Consideration of
Commission rules and regulations in adjudicatory
proceedings.’’ This rule generally prohibits attacks
on NRC rules during adjudicatory proceedings but
does allow a party to an adjudicatory proceeding to
petition that application of a specified rule be
waived or an exception made for the particular
proceeding. 10 CFR 2.335(b). The sole ground for
such a waiver or exception is that ‘‘special
circumstances with respect to the subject matter of
the particular proceeding are such that the
application of the rule or regulation * * * would
not serve the purposes for which the rule or
regulation was adopted.’’ Id. Thus, a review of the
Waste Confidence findings and rule now might be
expected to obviate such challenges in individual
COL proceedings.
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conduct a studied and orderly
reassessment and, as appropriate, to
revise and update the findings and rule.
In particular, it will allow the
Commission to consider alternative
time-frames which would provide
reasonable assurance for the availability
of a repository.
One possibility might be to make an
assumption that the Commission would
ultimately find the YM site
unacceptable by a certain date and then
set the expected availability of a
different repository at a time around 25
years later in accordance with DOE’s
1990 estimate of the time it would take
to make a repository available at a
different site. However, the Commission
rejected this route in the denial of the
Nevada petition:
[T]he use of a Commission acceptability
finding as the basis for repository availability
is impossible to implement because it would
require the Commission to prejudge the
acceptability of any alternative to Yucca
Mountain in order to establish a reasonably
supported outer date for the Waste
Confidence finding. That is, if the
Commission were to assume that a license for
the Yucca Mountain site might be denied in
2015 and establish a date 25 years hence for
the ‘availability’ of an alternative repository
(i.e., 2040), it would still need to presume the
‘acceptability’ of the alternate site to meet
that date (70 FR 48333; August 17, 2005).
Another approach would be to revise
the finding to include a target date or
timeframe for which it now seems
reasonable to assume that a repository
would be available. A target date for
when a disposal facility can reasonably
be expected to be available would result
from an examination of the technical
and institutional issues that would need
to be resolved before a repository could
be available. The target date approach
would be consistent with the HLW
disposal programs in other countries, as
explained further in this document. The
target date could be placed in the
finding itself, or described in the
explanation for the finding. A target
date is admittedly not very different
from ‘‘the first quarter of the twenty-first
century’’ as stated in the current
finding, but this approach would make
it more clear that specification of a
particular time for when a repository
could be built does not imply that
radioactive waste would pose unsafe
conditions if a repository were not
available at that time. The capability to
safely store radioactive waste over long
periods is a viable interim alternative
not dependent on any one specific year
for availability of a repository. The
Commission has adopted this approach
in updating its finding.
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Most countries possessing HLW and
SNF eventually plan to confine these
wastes using deep geologic disposal.
Currently, there are 24 other countries
that consider disposal of spent or
reprocessed nuclear fuel in deep
geologic repositories. From the vantage
point of near-term safety, there has been
little urgency in these countries for
implementing disposal facilities because
of the perceived high degree of safety
provided by interim storage, either at
reactors or at independent storage
facilities. Of these 24 countries,10 have
established target dates for the
availability of a repository. Most of the
14 countries which have not established
target dates rely on centralized interim
storage, which may include a protracted
period of onsite storage before shipment
to a centralized facility.11
The ‘‘target date’’ approach would
need to assume a beginning date for a
new repository program. NRC believes
that it is reasonable to select 2025 as the
starting point, the current outer date of
the Commission’s prediction of
repository availability. It is reasonable
to assume that it will be known by 2025
whether a repository is available at the
YM site. If it is not available, it seems
reasonable to assume that a new
repository program would get underway
around that time. The need for a new
repository program would not
necessarily be the result of an NRC
denial of the license application; it
could result from a change in national
policy for HLW disposal, a court
reversal of a Commission licensing
action, or other factors. The assumption
of a need for a new repository program
would be based on an assumption that
the proposed YM repository does not
become available, and not on an
assumption that NRC determines that
facility to be technically unacceptable.
In sum, the Commission would be
saying that it will remove its
expectation that a repository will be
available by 2025 but, even in the event
that the YM repository does not become
available, it retains confidence that
spent fuel can be safely stored with no
significant environmental impact until a
repository can reasonably be expected to
be available and that the Commission
has a target date for the availability of
the repository in that circumstance.
If it is assumed that a new repository
program begins around the year 2025,
then setting a target date for the
11 The three countries with target dates that plan
direct disposal of SNF are: Czech Republic (2050),
Finland (2020), and Sweden (2020). The seven
countries with target dates that plan disposal of
reprocessed SNF/HLW are: Belgium (2035), China
(2050), France (2025), Germany (2025), Japan
(2030s), Netherlands (2013), Switzerland (2042).
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availability of a repository becomes a
matter of examining the technical and
institutional problems DOE would need
to resolve to achieve the target date. The
technical problems should be the same
as the ones NRC examined in the earlier
Waste Confidence reviews, namely, how
long it would take DOE to locate a
suitable site and how long it would take
to develop a waste package and
engineered barriers for that site. For the
reasons explained in our evaluation of
Finding 1, the Commission continues to
have reasonable assurance that disposal
in a geologic repository is technically
feasible. That is the approach being
taken in all the countries identified
previously which have set target dates
for the availability of a repository. It is
also the approach of 14 other countries
which have HLW disposal programs,
but which have not set target dates.12 In
addition when Congress amended
NWPA in 1987 to focus exclusively on
the YM site, it did so for budgetary
reasons and not because the sites DOE
was considering at the time were
discovered to be technically
unacceptable. The research being done
nationally and internationally strongly
suggests that potentially acceptable sites
exist and can be identified.
The amount of time DOE might need
to develop an alternative repository site
would depend upon the context of any
enabling legislation, budgetary
constraints, and the degree of similarity
between a candidate site and other wellcharacterized sites with similar HLW
disposal concepts. DOE began
characterization of the YM site in 1982,
made its suitability determination in
2002, and submitted a license
application in 2008. However, the
history of potential repository
development at YM may be a poor
indicator of the amount of time needed
to develop a new repository. Many
problems extraneous to site
characterization activities adversely
impacted DOE’s repository program,
such as changes in enabling legislation,
public confidence issues, funding in
Congressional appropriations, and
significant delay in issuing
environmental standards. In terms of the
technical work alone, a lot would
depend on whether Congress
established a program involving
characterization of many sites
preliminary to the recommendation of a
single site (similar to the 1982 NWPA)
or a program focused on a single site
(similar to the amended NWPA). The
former would likely take longer but
might have a better chance of success if
problems developed with the single site.
Much would also depend on whether
the site(s) chosen for characterization is
similar to sites in this or other countries
for which much information is available
or whether the site(s) would present
novel challenges for which much
fundamental knowledge would have to
be developed. An alternative site with a
disposal approach that is similar to that
used in other international repository
programs could make use of the
extensive knowledge from those
international programs to gain
efficiencies in the alternative repository
development program.
In addition, there should be a certain
amount of ‘‘lessons learned’’ from the
YM repository program that could help
to shorten the length of a new program.
For example, performance assessment
techniques have improved significantly
over the past 20 years (e.g., the Goldsim
software package of DOE’s Total System
Performance Assessment was not
available 20 years ago and represents a
significant improvement over the
FORTRAN language of years past) such
that performance assessment models are
easier to develop and more reliable from
what was available 20 years ago.
Similarly, operational and
manufacturing aspects developed
during the YM program (e.g.,
manufacturing of waste packages,
excavation of drifts, waste handling),
would be applicable to another program.
Also, regulatory issues considered
during the YM program (e.g., burn-up
credit for nuclear fuel and seismic
performance analysis) should provide
information useful for setting new
standards or revising current
standards.13
Whether waste package and
engineered barrier information
developed during the YM repository
program would be transferable to a new
program depends heavily on the degree
of similarity between an alternative site
and YM. The fundamental physical
characteristics of the potential YM
repository are significantly different
from other potential repository sites that
were considered in the U.S. repository
program before 1987. If YM does not
become available, DOE could select an
alternative candidate site that was
similar to YM in important physical
characteristics (such as oxidizing
conditions, drifts above the water table
12 These countries are: Brazil, Canada, Hungary,
Lithuania, Romania, South Korea, Slovak Republic,
Spain (direct disposal of SNF); Bulgaria, India,
Italy, Russia, United Kingdom, Ukraine (disposal of
reprocessed SNF/HLW).
13 Both NRC’s Part 63 and EPA’s Part 197 are
applicable only for a repository at YM. NRC and
EPA have in place standards for a repository at a
different site, but these standards would likely be
revised in a new repository program.
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with low amounts of water infiltration,
water chemistry buffered by volcanic
tuff rocks). In this instance, much of the
existing knowledge for engineered
barrier performance at YM might be
transferable to a different site.
Nevertheless, much of DOE’s current
research on engineered barriers for YM
could be inapplicable if an alternative
site had significantly different
characteristics than the YM site, such as
an emplacement horizon in reducing
conditions below the water table. In this
instance, research from additional
programs by DOE, industry, and other
countries might provide important
information on engineered barriers,
provided DOE’s alternative was
analogous to sites and engineered
barriers being considered elsewhere.
It is important to note, however, that
broader institutional issues have
emerged since 1990 that bear on the
time it takes to implement geologic
disposal. International developments
have made clear that technical
experience and confidence in geologic
disposal, on their own, have not
sufficed to bring about the broader
societal and political acceptance needed
to realize the authorization of a single
national repository.
In the United Kingdom (UK), in 1997,
an application for the construction of a
rock characterization facility at
Sellafield was rejected, leaving the
country without a path forward for longterm management or disposal of HLW or
SNF. In 1998, an inquiry by the UK
House of Lords subsequently endorsed
geologic disposal, but specified that
public acceptance was required. As a
result, the UK Government embraced a
repository plan based on the principles
of voluntarism and partnership between
communities and implementers. This
led to the initiation of a national public
consultation, and major structural
reorganization within the UK program.
In 2007, the Scottish Government
officially rejected any further
consultation with the UK Government
on deep geologic disposal of HLW and
SNF. Discussions may continue on
issues of interim storage only. This
action by the Scottish Government
effectively ends more than 7 years of
consultations with stakeholders from
communities near Scottish nuclear
installations and represents another
major setback for the UK program.
In Germany, a large salt dome at
Gorleben has been under study since
1977 as a potential repository for SNF.
After decades of intense discussions and
protests, an agreement was reached in
2000 between the utilities and the
government to suspend exploration of
Gorleben for at least three, and at most,
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ten years. In 2003, the Federal Ministry
for the Environment set up an
interdisciplinary expert group to
identify, with public participation,
criteria for selecting new candidate
sites.
After detailed site investigations in
several locations in Switzerland, in
1993, the Swiss national cooperative for
radioactive waste disposal proposed a
deep geologic repository for low- and
intermediate-level waste at Wellenberg.
Despite a finding by Swiss authorities,
in 1998, that technical feasibility of the
disposal concept was successfully
demonstrated, a public cantonal
referendum rejected the proposed
repository in 2002. Even after more than
25 years of high quality field and
laboratory research, Swiss authorities do
not expect a deep geologic repository
will be available in their country before
2040.
In 1998, an independent panel
reported to the Governments of Canada
and Ontario on its review of Atomic
Energy of Canada Ltd.’s concept of
geologic disposal. Canadian Nuclear
Fuel Waste Disposal Concept
Environmental Assessment Panel,
Report of the Nuclear Fuel Waste
Management and Disposal Concept
Environmental Assessment Panel,
February 1998. The panel found that
from a technical perspective, safety of
the concept had been adequately
demonstrated, but from a social
perspective, it had not. The panel
concluded that broad public support is
necessary in Canada to ensure the
acceptability of a concept for managing
nuclear fuel wastes. The panel also
found that technical safety is a key part,
but only one part of acceptability. To be
considered acceptable in Canada, the
panel found that a concept for managing
nuclear fuel wastes must: (1) Have broad
public support; (2) be safe from both a
technical and social perspective; (3)
have been developed within a sound
ethical and social assessment
framework; (4) have the support of
Aboriginal people; (5) be selected after
comparison with the risks, costs and
benefits of other options; and (6) be
advanced by a stable and trustworthy
proponent and overseen by a
trustworthy regulator. Resulting
legislation mandated a nationwide
consultation process and widespread
organizational reform. Eight years later,
in 2005, a newly-created Nuclear Waste
Management Organization (NWMO),
recommended an Adaptive Phased
Management approach for long-term
care of Canada’s SNF, based on the
outcomes of the public consultation.
This approach includes both a technical
method and a new management system.
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According to NWMO, it ‘‘* * *
provides for centralized containment
and isolation of used nuclear fuel deep
underground in suitable rock
formations, with continuous monitoring
and opportunity for retrievability; and it
allows sequential and collaborative
decision-making, providing the
flexibility to adapt to experience and
societal and technological change.’’
NWMO, Choosing a Way Forward: The
Future Management of Canada’s Used
Nuclear Fuel, Final Study Report,
November 2005.
In 2007, the Government of Canada
announced its selection of the Adaptive
Phased Management approach, and
directed NWMO to take at least two
years to develop a ‘‘collaborative
community-driven site-selection
process.’’ NWMO must then use this
process to open consultations with
citizens, communities, Aboriginals, and
other interested parties to find a suitable
site in a willing host community. The
Canadian Government explicitly
acknowledges that this approach will
‘‘take time to develop a process that is
open, transparent, inclusive, and that is
built on a solid foundation of trust,
integrity and respect for Canadians and
the environment.’’ The Honorable Gary
Lunn, P.C., M.P., Minister of Natural
Resources, Canada, to President of
NWMO, July 12, 2007. For financial
planning and cost estimation purposes
only, NWMO assumes the availability of
a deep geological repository in 2035, 27
years after initiating development of
new site selection criteria, 30 years after
embarking on a national public
consultation, and 37 years after rejection
of the original geologic disposal
concept. NWMO, Annual Report 2007:
Moving Forward Together, March 2008.
Repository development programs in
Finland and Sweden are much further
advanced, but have nonetheless taken
the time to build support from potential
host communities. Preliminary site
investigations in Finland began in 1986,
and detailed characterizations of four
locations were performed between 1993
and 2000. In 2001, the Finnish
Parliament ratified the Government’s
decision to proceed with a repository
project at a chosen site only after the
municipal council of the host
community had approved the siting of
the disposal facility in 1999. Finland
expects this facility to begin receipt of
SNF for disposal in 2020, 34 years after
the start of preliminary site
investigations.
Between 1993 and 2000, Sweden
conducted feasibility studies in eight
municipalities. Based on technical
considerations, one site was found
unsuitable for further study, and two,
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based on municipal referenda, decided
against allowing further investigations.
Three of the remaining five sites were
selected for detailed site investigations.
Municipalities adjacent to two of these
sites agreed to be potential hosts and
one refused. One of the two volunteer
sites will be selected for development as
a repository and an application to the
Swedish safety authorities is expected
in 2009. If construction is authorized,
Sweden expects the repository to be
available for disposal in 2018, 25 years
after starting feasibility studies in 1993.
If YM is not licensed, Congress will
need to provide direction to DOE for
development of a new site or,
potentially, a new management concept,
for the long-term management and
disposal of SNF and HLW. Whatever
approach Congress mandates,
international experience since 1990
would appear to suggest that greater
attention may need to be paid to
developing societal and political
acceptance in concert with essential
technical, safety and security
assurances. While there is no technical
basis for making precise estimates of the
minimum time needed to accomplish
these objectives, examination of the
international examples cited previously
would support a range of between 25
and 35 years.
Another important institutional issue
is whether funding for a new repository
program is likely to be available. The
provisions of NWPA for funding the
repository have proved to be adequate
for assuring the timely development of
a repository in the sense that there have
always been more than sufficient funds
available for meeting the level of
funding Congress appropriates for the
repository program. Section 302(e)(2) of
NWPA provides that the Secretary of
Energy may make expenditures from the
Nuclear Waste Fund (NWF), subject to
appropriations by the Congress. At the
FY 2009 Appropriations Hearing (April
10, 2008), Edward F. Sproat III, Director
of OCRWM, DOE, stated that the NWF
has a balance of approximately $21.0
billion. Thus, the NWF has the capacity
to ensure timely development of a
repository consistent with
Congressional funding constraints.
Moreover, DOE is in the process of
preparing contracts to be signed by
utilities planning to build new reactors.
Therefore, there will be a source of
funding for disposal of the fuel to be
generated by these reactors.
Arriving at a target date involves
balancing the technical and institutional
factors discussed previously. It appears
that the technical work needed to make
a repository available could probably be
done in less time than it took DOE to
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jlentini on PROD1PC65 with PROPOSALS
submit a license application for the YM
site (26 years measured from the
beginning of site characterization).
However, as discussed previously, the
time needed to develop societal and
political acceptance of a repository
might range between 25 and 35 years.
Therefore, if the starting point for a new
program were 2025, a reasonable target
date would be 2050–2060 for the
availability of a repository.
Finding 2 also includes the prediction
that sufficient repository capacity will
be available within 30 years beyond the
licensed life for operation (which may
include the term of a revised or renewed
license) of any reactor to dispose of
HLW and SNF originating in such
reactor and generated up to that time.
As explained previously, in 1990 DOE
projected that 87,000 MTHM would be
generated by the year 2036. Given the
statutory limit of 70,000 MTHM for the
first repository, either statutory relief
from that limit or a second repository
would be needed. The Commission’s
continued assurance that sufficient
repository capacity would be available
within 30 years of license expiration of
all reactors rested on an assumption that
two repositories would be available in
approximately 2025 and 2035, each
with acceptance rates of 3400 MTHM/
year within several years after
commencement of operations. See 55 FR
38502; September 18, 1990.
If an assumption is made, for
purposes of establishing a target date,
that a repository will not become
available until approximately 2050–
2060, it appears that a finding that
sufficient repository space will be
available within 30 years beyond the
licensed life for operation (which may
include the term of a revised or renewed
license) is not supportable.14 According
to the 2007–2008 USNRC Information
Digest, NUREG–1350, Vol. 19, Table 11,
p.48 (Information Digest), there are 18
reactor operating licenses that will
expire between 2009 and 2020. There
are an additional 44 licenses that will
expire between 2021 and 2030. Many of
these licenses may be renewed which
would extend their operating lifetimes,
but this cannot be assumed.15 For
14 Based on the inventory of SNF in nuclear
power plant pools and interim storage facilities, the
amount of spent fuel is anticipated to exceed the
70,000 MTHM disposal limit in the NWPA by 2010.
See Institute of Nuclear Material Management
Seminar XXV, January 16, 2008, paper by Bob
Quinn of Energy Solutions, Industry Perspective on
the GNEP—Yucca Mountain Relationship.
Therefore, a new repository program would need to
remove this limit or provide for more than one
repository.
15 Six of these reactor operating licenses have
already been renewed (Dresden 2, Ginna, Nine Mile
Point 1, Robinson 2, Point Beach 1, and
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licenses that are not renewed, some
spent fuel will need to be stored for
more than 30 years beyond the
expiration of the license if a repository
is not available until 2050–2060.
According to the Information Digest,
Appendix B, there are 22 reactors which
were formerly licensed to operate, but
which have been permanently shut
down. Thirty years beyond their
licensed life of operation will come as
early as 2029 for Dresden 1 and as late
as 2056 for Millstone 1, but for most of
these plants, 30 years beyond the
licensed life for operation will fall in the
2030s and 2040s. Thus, for virtually all
of these plants, spent fuel will have to
be stored beyond 30 years from the
expiration of the license if a repository
is not available until 2050–2060.
In 1990, the Commission emphasized
that this 30 year period was not a safety
finding. It was only an estimate of how
long it was likely that SNF would need
to be stored, given its confidence that
repository disposal would be available
by 2025. In fact, the Commission said it
was not concerned about the fact that it
was already clear in 1990 that a few
reactors would need to store spent fuel
on-site beyond 30 years after the
effective expiration date of their licenses
(i.e., the date the license prematurely
terminated) due to its confidence in the
safety of spent fuel storage (55 FR
38503; September 18, 1990). For the
reasons presented in the evaluation of
Finding 4, the Commission is now able
to say that there is no public health and
safety or environmental concern if its
target date of 2050–2060 for the
availability of a disposal facility results
in the need to store fuel at some reactors
for a 50–60 year period after expiration
of the license or even longer.
Based on the information described
previously, the Commission is
proposing to revise Finding 2 to
eliminate a specific date for the
availability of a repository and to state
that a repository may reasonably be
expected to be available within 50–60
years beyond the licensed life for
operation of any reactor.
C. Proposed Finding 2
The Commission finds reasonable
assurance that sufficient mined geologic
repository capacity can reasonably be
expected to be available within 50–60
years beyond the licensed life for
operation (which may include the term
of a revised or renewed license) of any
reactor to dispose of the commercial
Monticello). Forty-two other reactor operating
licenses have been renewed and the renewed
licenses will expire after 2030.
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59561
HLW and spent fuel originating in such
reactor and generated up to that time.
D. Specific Question for Public
Comment
An alternative approach would be for
the Commission to revise Finding 2
without reference to a timeframe for the
availability of a repository. (The
proposed revision to simplify 10 CFR
§ 51.23(a) removes the reference to a
repository date although it is based on
an expectation of repository availability
by 2050–2060 as set forth in the
proposed revision to Finding 2). In
2005, in response to PRM–51–8, the
Commission had declined to consider
such an approach to define
‘‘availability’’ based on a presumption
that some acceptable disposal site
would become available at some
undefined time in the future. The
Commission concluded then that such
an approach would be a departure from
the framework it had established in its
original 1984 decision to use a specific
timeframe as a basis for assessing the
degree of assurance that radioactive
waste can be disposed of safely and for
determining when such disposal will be
available (70 FR. 48333; August 17,
2005).
The Commission’s proposed revision
of Finding 2 is based on its assessment
not only of our understanding of the
technical issues involved, but also
predictions of the time needed to bring
about the necessary societal and
political acceptance for a repository site.
Recognizing the inherent difficulties in
making such predictions, the
Commission seeks specific comment on
whether it should revise its approach to
Finding 2 and adopt a more general
finding of reasonable assurance that
SNF generated in any reactor can be
stored safely and without significant
environmental impacts until a disposal
facility can reasonably be expected to be
available. In other words, in response to
the court’s concerns that precipitated
the original Waste Confidence
proceeding, the Commission could now
say that there is no need to be
concerned about the possibility that
spent fuel may need to be stored at
onsite or offsite storage facilities at the
expiration of the license (including a
renewed license) until such time as a
repository is available because we have
reasonable assurance that spent fuel can
be so stored for long periods of time,
safely and without significant
environmental impact. Such a finding
would be made on the basis of the
Commission’s accumulated experience
of the safety of long-term spent fuel
storage with no significant
environmental impact (see Finding 4)
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and its accumulated experience of the
safe management of spent fuel storage
during and after the expiration of the
reactor operating license (see Finding 3).
The Commission seeks comment on
this alternative revision of Finding 2
and whether additional information is
needed for or accompanying changes
should be made to its other Findings on
the long term storage of spent fuel if
such a revision of Finding 2 were to be
adopted.
jlentini on PROD1PC65 with PROPOSALS
III. Finding 3: The Commission Finds
Reasonable Assurance That HLW and
Spent Fuel Will Be Managed in a Safe
Manner Until Sufficient Repository
Capacity Is Available To Assure the
Safe Disposal of All HLW and Spent
Fuel
A. Bases for Finding 3
The Commission reached this finding
in 1984, and reaffirmed it in 1990. The
focus of this finding is on whether
reactor licensees can be expected to
safely store their spent fuel in the period
between the cessation of reactor
operations and the availability of
repository capacity for their fuel. The
Commission placed its main reliance
that the spent fuel would be managed
safely on the fact that, under either a
possession-only Part 50 license or a Part
72 license, the utility would remain
under NRC’s regulatory control and
inspections and oversight of storage
facilities would continue (49 FR 34679–
34680; August 31, 1984; 55 FR 38508;
September 18, 1990). In 1990, when
extended storage at the reactor site
seemed more probable, the Commission
pointed out that NRC’s regulations
provided for license renewals of Part 72
licenses and that NRC was considering
issuance of a general Part 72 license
under which spent fuel could be stored
in NRC-certified casks,16 (55 FR 38508;
September 18, 1990). The Commission
reasoned that these regulations would
provide further mechanisms for NRC
supervision of spent fuel management
by licensees. The Commission was not
concerned about then-looming
contractual disputes between DOE and
the utilities regarding DOE’s obligation
to begin removing spent fuel from
reactor sites in 1998 because NRC
licensees cannot abandon spent fuel in
their possession and would remain
responsible for it (55 FR 38508;
September 18, 1990).
The Commission also considered the
unusual case where a utility was unable
to manage its spent fuel. The NWPA had
16 Part 72 was, in fact, amended to provide for
storage of spent fuel in NRC-certified casks
pursuant to a general license (55 FR 29191; July 18,
1990).
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provided an Interim Storage Program
(Subtitle B) which enabled a utility to
enter into a contract with DOE for
temporary storage of its fuel but, by
1990 (the expiration of the program), no
utility had sought to take advantage of
it (55 FR 38508; September 18, 1990). In
a case where a utility became insolvent,
NRC believed that the cognizant state
public utility commission would be
likely to require an orderly transfer to
another entity which could be
accomplished if the new entity met
NRC’s regulations (49 FR 34680; August
31, 1984). Further, the Commission
expressed the view that, while the
possibility of a need for Federal action
to take over stored spent fuel from a
defunct utility or from a utility that
lacked technical competence to assure
safe storage was remote, the authority
for this type of action exists in sections
186c and 188 of the Atomic Energy Act.
Id.
B. Evaluation of Finding 3
As explained previously, the focus of
Finding 3 is on whether reactor
licensees can be expected to safely store
their spent fuel in the period between
the cessation of reactor operations and
the availability of repository capacity for
their fuel. In this regard, the NRC is
successfully regulating four
decommissioned reactor sites that
continue to hold Part 50 licenses and
consist only of an ISFSI under the Part
72 general license provisions.17 In
addition, the NRC staff has discussed
plans to build and operate ISFSIs under
the Part 72 general license provisions
with the licensees at the La Crosse and
Zion plants, which are currently
undergoing decommissioning. The NRC
is also successfully regulating ISFSIs at
two fully decommissioned reactor sites
(Trojan and Ft. St. Vrain) under specific
Part 72 licenses.18
The NRC monitors the performance of
ISFSIs at decommissioned reactor sites
by conducting periodic inspections that
are the same as the inspections
performed for ISFSIs at operating
reactor sites. When conducting
inspections at these ISFSIs, NRC
inspectors follow the guidance in NRC
Inspection Manual Chapter 2690,
‘‘Inspection Program for Dry Storage of
Spent Reactor Fuel at Independent
Spent Fuel Storage Installations and for
Part 71 Transportation Packages.’’ At all
six decommissioned reactor sites
mentioned previously, all spent fuel on
17 These reactor sites include Maine Yankee,
Yankee Rowe, Connecticut Yankee (also known as
Haddam Neck), and Big Rock Point.
18 There are several additional sites with specific
Part 72 ISFSI licenses that are in the process of
decommissioning (e.g., Humbolt Bay, Rancho Seco).
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site has been successfully loaded into
the ISFSI, so only those inspection
procedures applicable to the existing
storage configurations are conducted.
Also, any generally licensed ISFSI
where decommissioning and final
survey activities related to reactor
operations have been completed is
treated as an ‘‘away from reactor’’ (AFR)
ISFSI for inspection purposes.
Therefore, those programs relied upon
under the 10 CFR Part 50 license for
operation of the generally licensed ISFSI
are also subject to inspection.
The NRC has not encountered any
management problems associated with
the ISFSIs at these six decommissioned
reactor sites. Further, NRC’s inspection
findings do not indicate unique
management problems at any currently
operating ISFSI. Generally, the types of
issues identified through NRC
inspections of ISFSIs are similar to
issues identified for Part 50 licensees.
Most issues are identified early in the
operational phase of the dry cask storage
process, during loading preparations
and actual spent fuel loading activities.
Once a loaded storage cask is placed on
the storage pad, relatively few
inspection issues are identified due to
the passive nature of these facilities.
Further, NRC’s regulations require
that every nuclear power reactor
operating license issued under 10 CFR
part 50, and every COL issued under 10
CFR part 52 must contain a condition
requiring licensees to submit written
notification to the Commission of the
licensees’ plan for managing irradiated
fuel between cessation of reactor
operation and the time the DOE takes
title to and possession of the irradiated
fuel for ultimate disposal in a
repository. The submittal, required by
10 CFR 50.54(bb), must include
information on how the licensee intends
to provide funding for the management
of its irradiated fuel. Specifically, 10
CFR 50.54(bb) requires the licensee to:
[W]ithin 2 years following permanent
cessation of operation of the reactor or 5
years before expiration of the reactor
operating license, whichever occurs first,
submit written notification to the
Commission for its review and preliminary
approval of the program by which the
licensee intends to manage and provide
funding for the management of all irradiated
fuel at the reactor following permanent
cessation of operation of the reactor until title
to the irradiated fuel and possession of the
fuel is transferred to the Secretary of Energy
for its ultimate disposal * * * Final
Commission review will be undertaken as
part of any proceeding for continued
licensing under part 50 or 72 of this chapter.
The licensee must demonstrate to NRC that
the elected actions will be consistent with
NRC requirements for licensed possession of
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irradiated nuclear fuel and that the actions
will be implemented on a timely basis.
Where implementation of such actions
requires NRC authorizations, the licensee
shall verify in the notification that submittals
for such actions have been or will be made
to NRC and shall identify them. A copy of
the notification shall be retained by the
licensee as a record until expiration of the
reactor operating license. The licensee shall
notify the NRC of any significant changes in
the proposed waste management program as
described in the initial notification.
While the interim storage program
under Subtitle B of the NWPA expired
in 1990, in the past arrangements have
been made with DOE to take possession
of spent fuel in urgent or unusual
circumstances, as was done for the
Three Mile Island Unit 2 fuel debris. 10
CFR 50.54(bb) (2008).
To date, the NRC has also renewed
three specific Part 72 ISFSI licenses.
These renewals include the Part 72
specific licenses for the General Electric
Morris Operation (the only wet, or pooltype ISFSI), as well as the Surry and
H.B. Robinson ISFSIs. The NRC staff is
also currently reviewing an application
for renewal of the specific ISFSI license
for the Oconee plant (ML081280084)
and anticipates a renewal application
for the Fort St. Vrain ISFSI sometime in
2009. Specific licenses for six additional
ISFSIs will expire between 2012 and
2020. It is expected that license renewal
will be requested by these licensees,
unless a permanent repository or some
other interim storage option is made
available. Although the NRC staff’s
experience with renewal of ISFSI
licenses is limited to these three cases,
it is noteworthy that both the Surry and
H.B. Robinson ISFSI licenses were
renewed for a period of 40-years,
instead of the 20-year renewal period
currently provided for under Part 72.
The Commission authorized the staff to
grant exemptions to allow the 40-year
renewal period after the staff reviewed
the applicants’ evaluations of aging
effects on the structures, systems, and
components important to safety. The
Commission determined that the
evaluations, supplemented by the
licensees’ aging management programs,
provided reasonable assurance of
continued safe storage of spent fuel in
these ISFSIs. See SECY–04–0175,
‘‘Options for Addressing the Surry
Independent Spent Fuel Storage
Installation License-Renewal Period
Exemption Request,’’ September 28,
2004 (ML041830697).
With regard to generally licensed
ISFSIs, the NRC staff is currently
working on a proposed rulemaking to
clarify the processes for the renewal of
ISFSIs operated under the general
license provisions of 10 CFR part 72,
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and for renewal of the Certificates of
Compliance for dry cask storage
systems. See License and Certificate of
Compliance Terms (73 FR 45173;
August 4, 2008). There are currently
nine sites operating generally licensed
ISFSIs that will reach the prescribed 20
year limit on storage between 2013 and
2020.
The Commission concludes that the
events that have occurred since the last
formal review of the Waste Confidence
Decision in 1990 provide support for a
continued finding of reasonable
assurance that HLW and spent fuel will
be managed in a safe manner until
sufficient repository capacity is
available. Specifically, the NRC has
continued its regulatory control and
oversight of spent fuel storage at both
operating and decommissioned reactor
sites, through both specific and general
Part 72 licenses. With regard to general
Part 72 licenses, the NRC has
successfully implemented a general
licensing and cask-certification
program, as envisioned by the
Commission in 1990. There are
currently 15 certified spent fuel storage
cask designs. 10 CFR 72.214 (2008). In
addition, the Commission’s reliance on
the license renewal process in its 1990
review has proven well placed, with
two specific Part 72 ISFSI licenses
having been successfully renewed for an
extended 40-year renewal period, and a
third having been renewed for a period
of 20 years. Further, while DOE did not
meet its contractual obligation to begin
removing spent fuel from reactor sites in
1998, NRC licensees have continued to
meet their obligation to safely store
spent fuel in accordance with the
requirements of 10 CFR Parts 50 and
72.19
19 Section 302 of NWPA authorizes the Secretary
of Energy to enter into contracts with utilities
generating HLW and SNF under which the utilities
are to pay statutorily imposed fees into the NWF in
return for which the Secretary, ‘‘beginning not later
than January 31, 1998, will dispose of the [HLW]
or [SNF] involved * * *’’ 42 U.S.C. 10222(a)(5)(B).
The NWPA also prohibits NRC from issuing or
renewing a reactor operating license unless the
prospective licensee has entered into a contract
with DOE or is engaged in good-faith negotiations
for such a contract. 42 U.S.C. 10222(b)(1). When it
became evident that a repository would not be
available in 1998, DOE took the position that it did
not have an unconditional obligation to accept the
HLW or SNF in the absence of a repository. See
Final Interpretation of Nuclear Waste Acceptance
Issues, (60 FR 21793; April 28, 1995). The U.S.
Court of Appeals for the District of Columbia
Circuit, however, held that DOE’s statutory and
contractual obligation to accept the waste no later
than January 31, 1998 was unconditional. Indiana
Michigan Power Co. v. DOE, 88 F.3d 1272 (DCDC
Cir. 1996). Subsequently, the utilities have
continued to safely manage the storage of SNF in
reactor storage pools and in ISFSIs and have
received damage awards as determined in lawsuits
brought before the U.S. Federal Claims Court, See,
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On the basis of the information
described previously, the Commission
proposes to reaffirm Finding 3.
IV. Finding 4 (1990): The Commission
Finds Reasonable Assurance That, if
Necessary, Spent Fuel Generated in
Any Reactor Can Be Stored Safely and
Without Significant Environmental
Impacts for at Least 30 Years Beyond
the Licensed Life for Operation (Which
May Include The Term of a Revised or
Renewed License) of That Reactor at Its
Spent Fuel Storage Basin, or at Either
Onsite or Offsite Independent Spent
Fuel Storage Installations
A. Bases for Finding 4
The focus of this finding is on the
safety and environmental effects of longterm storage of spent fuel. In 1984, the
Commission found that spent fuel can
be stored safely and without significant
environmental impacts for at least 30
years beyond the expiration of reactor
operating licenses (49 FR 34660; August
31, 1984). In 1990, the Commission
determined that if the reactor operating
license were renewed for 30 years,20
storage would be safe and without
environmental significance for at least
30 years beyond the term of licensed
operation for a total of at least 100 years
(55 FR 38513; September 18, 1990). The
Commission looked at four broad issues
in making this finding: (1) The longterm integrity of spent fuel under water
pool storage conditions; (2) the structure
and component safety for extended
facility operation for storage of spent
fuel in water pools; (3) the safety of dry
storage; and (d) the potential risks of
accidents and acts of sabotage at spent
fuel storage facilities (49 FR 34681;
August 31, 1984; 55 FR 38509;
September 18, 1990).
With respect to the safety of water
pool storage, the Commission found in
1984 that research and experience in the
United States and Canada and other
countries confirmed that long-term
storage could be safely undertaken,
e.g., that the cladding which encases
spent fuel is highly resistant to failure
(49 FR 34681–34682; August 31, 1984).
In 1990, the Commission determined
that experience with water storage of
e.g., System Fuels Inc. v. U.S., 78 Fed. Cl. 769
(October 11, 2007).
NRC has recently become aware that DOE is in
the process of developing an amendment to the
standard spent fuel contract for new nuclear power
plants. This amendment would include a revised
commitment for removal of spent fuel from new
reactor sites by DOE. See discussion of Finding 5,
infra.
20 Subsequently, the Commission limited the
renewal period for power reactor licenses to 20
years beyond expiration of the operating license or
combined license. 10 CFR 54.31 (56 FR 64943,
64964; December, 13, 1991).
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spent fuel continued to confirm that
pool storage is a benign environment for
spent fuel that does not lead to
significant degradation of spent fuel
integrity and that the water pools in
which the assemblies are stored will
remain safe for extended periods.
Further, degradation mechanisms are
well understood and allow time for
appropriate remedial action, (55 FR
38510, 38511; September 18, 1990). In
sum, wet storage was affirmed as a fullydeveloped technology with no
associated major technical problems,
based on both experience and scientific
studies.
In 1984, the Commission based its
confidence in the safety of dry storage
on an understanding of the material
degradation processes, derived largely
from technical studies, together with the
recognition that dry storage systems are
simpler and more readily maintained,
(49 FR 34683–34684; August 31, 1984).
By 1990, NRC and ISFSI operators had
gained considerable experience with dry
storage. NRC staff safety reviews of
topical reports on storage system
designs, the licensing and inspection of
dry storage at two reactor sites under
Part 72, and NRC’s promulgation of an
amendment to Part 72, incorporating a
monitored retrievable storage
installation (MRS) (a dry storage facility)
into the regulations had confirmed the
1984 conclusions on the safety of dry
storage. In fact, under the environmental
assessment for the amendment
(NUREG–1092), the Commission found
confidence in the safety and
environmental insignificance of dry
storage at an MRS for 70 years following
a period of 70 years of storage in spent
fuel storage pools (55 FR 38509–38513;
September 18, 1990).
The Commission also found that the
risks of major accidents at spent fuel
storage pools resulting in offsite
consequences were remote because of
the secure and stable character of the
spent fuel in the storage pool
environment, and the absence of
reactive phenomena—‘‘driving
forces’’—which might result in dispersal
of radioactive material. The Commission
noted that storage pools and ISFSIs are
designed to safely withstand accidents
caused either by natural or man-made
phenomena and that human error does
not have the capability to create a major
radiological hazard to the public due to
the absence of high temperature and
pressure conditions (49 FR 34684–
34685; August 31, 1984). By 1990, the
NRC staff had spent several years
studying in detail catastrophic loss of
reactor spent fuel pool water, possibly
resulting in a fuel fire in a dry pool, but
concluded that because of the large
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inherent safety margins in the design
and construction of a spent fuel pool no
action was justified to further reduce the
risk (55 FR 38511; September 18, 1990).
In 1984, the Commission recognized
that the intentional sabotage of a storage
pool was theoretically possible but
found that the consequences would be
limited by the realities that, except for
some gaseous fission products, the
radioactive content of spent fuel is in
the form of solid ceramic material
encapsulated in high-integrity metal
cladding and stored underwater in a
reinforced concrete structure (49 FR
34685; August 31, 1984). Under these
conditions, the Commission noted that
the radioactive content of spent fuel is
relatively resistant to dispersal to the
environment. Similarly, because of the
weight and size of the sealed protective
enclosures, dry storage of spent fuel in
dry wells, vaults, silos and metal casks
is also relatively resistant to sabotage
and natural disruptive forces. Id.
Although the 1990 decision examined
several studies of accident risk, no
considerations had arisen to affect the
Commission’s confidence that the
possibility of a major accident or
sabotage with offsite radiological
impacts at a spent fuel storage facility is
extremely remote (55 FR 38512;
September 18, 1990).
Finally, the Commission noted that
the generation and onsite storage of a
greater amount of spent fuel as a result
of reactor license renewals would not
affect the Commission’s findings on
environmental impact. Finding 4 is not
based on a determination of a specific
number of reactors and amount of spent
fuel generated. Finding 4 evaluates the
safety of spent fuel storage and lack of
environmental impacts overall, noting
that individual license renewal actions
would be subject to safety and
environmental reviews (55 FR 38512;
September 18, 1990).
B. Evaluation of Finding 4
As explained previously, the focus of
Finding 4 is on the safety and
environmental significance of long-term
storage of spent fuel. Specifically, the
Commission examined four broad issues
in making this finding: (1) The longterm integrity of spent fuel under water
pool storage conditions; (2) the structure
and component safety for extended
facility operation for storage of spent
fuel in water pools; (3) the safety of dry
storage; and (4) the potential risks of
accidents and acts of sabotage at spent
fuel storage facilities.
1. Storage in Spent Fuel Pools
Since 1990, the NRC has continued its
periodic examination of spent fuel pool
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storage to assure adequate safety is
maintained and that there are no
adverse environmental effects of storage
of spent fuel in pools. The Office of
Nuclear Reactor Regulation (NRR) and
the former Office for Analysis and
Evaluation of Operational Data (AEOD)
independently evaluated the safety of
spent fuel pool storage, and the results
of these evaluations were documented
in a memo to the Commission dated July
26, 1996, entitled ‘‘Resolution of Spent
Fuel Storage Pool Action Plan Issues,’’
(ML003706364) and a separate memo to
the Commission dated October 3, 1996),
entitled, ‘‘Assessment of Spent Fuel
Pool Cooling,’’ (ML003706381) (later
published as NUREG–1275, Vol. 12,
‘‘Operating Experience Feedback
Report: Assessment of Spent Fuel
Cooling,’’ February 1997), respectively.
As a result of these studies, potential
follow-up activities were identified. The
NRR staff described NRC follow-up
activities and associated industry
actions in a memo to the Commission
dated September 30, 1997, entitled
‘‘Followup Activities on the Spent Fuel
Pool Action Plan,’’ (ML003706412).
These evaluations became part of the
investigation of Generic Safety Issue
173, ‘‘Spent Fuel Pool Storage Safety,’’
which found that the relative risk posed
by loss of spent fuel cooling is low
when compared with the risk of events
not involving the SFP.
The safety and environmental effects
of spent fuel pool storage were also
addressed in conjunction with
regulatory assessments on permanently
shutdown nuclear plants and
decommissioning nuclear power plants.
NUREG/CR–6451, ‘‘A Safety and
Regulatory Assessment of Generic BWR
and PWR Permanently Shutdown
Nuclear Power Plants,’’ (August 1997)
addressed the appropriateness of
regulations (e.g., requirements for
emergency planning and insurance)
associated with spent fuel pool storage.
The study identified a number of
regulations that were pertinent only to
an operating reactor and not to spent
fuel storage. Those regulations were not
needed to ensure the safe maintenance
of a permanently shutdown plant. This
study also provided what are now
known to be conservative bounding
estimates of fuel coolability, and
provided a number of conservative
bounding estimates of offsite
consequences for the most severe
accidents that involve draining of the
spent fuel pool.
More recently, the NRC issued
NUREG–1738, ‘‘Technical Study of
Spent Fuel Pool Accident Risk at
Decommissioning Nuclear Power
Plants,’’ (February 2001). This study
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provided the results of the NRC staff’s
latest evaluation of the potential
accident risk in a spent fuel pool at
decommissioning plants. The report
contained a discussion of fuel
coolability for various types of accidents
and included potential offsite
consequences based on assumed
radiation releases. The study
demonstrated that using conservative
and bounding assumptions regarding
the postulated accidents, the predicted
risk estimates were below that
associated with reactor accidents and
well below the Commission’s safety
goal. There was even some concern
within the NRC that the level of
conservatism in the analysis
accompanying NUREG–1738 overstated
the likelihood and severity of the more
extreme spent fuel pool accidents.
These concerns have proven valid, as
subsequent studies (described in the
following paragraph) have conclusively
and consistently shown that the safety
margins are much larger than indicated
by previous studies, such as NUREG–
1738. See The Attorney General of
Commonwealth of Massachusetts, The
Attorney General of California; Denial of
Petitions for Rulemaking (73 FR 46204;
August 8, 2008).
Following the terrorist attacks of
September 11, 2001, the NRC undertook
a complete reexamination of spent fuel
pool safety and security issues. This
reexamination included a significantly
improved methodology, based on
detailed state-of-the-art analytical
modeling, for assessing the response of
spent fuel assemblies during security
events including those which might
result in draining of the spent fuel pool.
This more detailed and realistic
analytical modeling was also supported
by extensive testing of zirconium
oxidation kinetics in an air environment
and full scale coolability and ‘‘zirc fire’’
testing of spent fuel assemblies. This
extensive effort resulted in both the
confirmation of the conservatism of past
analyses and improved, more realistic
analyses of fuel coolability and potential
responses during accident or security
event conditions. Importantly, the new
more detailed and realistic modeling led
to the development of improvements in
spent fuel safety, which were required
to be implemented at spent fuel pools
by the Commission for all operating
reactor sites. See id.
In 2003, the U.S. Congress asked the
National Academies to provide
independent scientific and technical
advice on the safety and security of
commercial SNF storage including the
potential safety and security risks of
SNF presently stored in cooling pools
and dry casks at commercial nuclear
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reactor sites. A classified report was
issued by the National Academy of
Sciences (NAS) in July 2004, and an
unclassified summary for public
distribution was issued in 2005. As part
of the information gathering for the
study, the NRC and Sandia National
Laboratories briefed the NAS authoring
committee on the ongoing work to
reassess spent fuel pool safety and
security issues. The NAS report
contains findings and recommendations
for reducing the risk of events involving
spent fuel pools as well as dry casks.
The NRC provided its response to the
NAS in a letter to Senator Pete V.
Domenici from NRC Chairman Nils J.
Diaz, dated March 14, 2005
(ML050280428). In essence, the NRC
concluded, as a result of its own study
and subsequent regulatory actions, that
it had adopted the important
recommendations of the NAS report
relevant to spent fuel pools. As a result
of the improvements to spent fuel pool
safety and security, together with the
inherent safety and robustness of spent
fuel pool designs, the NRC concluded
that the risk associated with security
events at spent fuel pools is acceptably
low. Because those safety improvements
to spent fuel pool storage are applicable
to non-security events (randomly
initiated accidents), accident risk will
also have been further reduced.
While the Commission continues to
have reasonable assurance that storage
in spent fuel pools provides adequate
protection of public health and safety
and the common defense and security,
and will not result in significant
impacts on the environment, NRC
acknowledges several incidents of
groundwater contamination originating
from leakage in reactor spent fuel pools
and associated structures. In 1990, the
Commission specifically acknowledged
two incidents where radioactive water
leaked from spent fuel pools, one case
resulting in contamination outside of
the owner controlled area. (See 55 FR.
38511; September 18, 1990). The
Commission addressed these events
stating, ‘‘[t]he occurrence of operational
events like these have been addressed
by NRC staff at the plants listed. The
staff has taken inspection and
enforcement actions to reduce the
potential for such operational
occurrences in the future.’’ Id.
On March 10, 2006, the Liquid
Radioactive Release Lessons Learned
Task Force was established by the NRC
Executive Director for Operations in
response to incidents at several plants
involving unplanned, unmonitored
releases of radioactive liquids into the
environment. Liquid Radioactive
Release Lessons Learned Task Force
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59565
Final Report, September 1, 2006 (Task
Force Report) (ML062650312). One of
the incidents that prompted formation
of the Task Force involved leakage from
the Unit 1 and 2 spent fuel pools at
Indian Point.21 Task Force Report, at 1,
5–6, 11. The Task Force reviewed
historical data on inadvertent releases of
radioactive liquids, including four
additional incidents involving leakage
from spent fuel pools (Seabrook, Salem,
Watts Bar, and Palo Verde). As a result
of its review, the Task Force concluded
that ‘‘[b]ased on bounding dose
calculations and/or actual
measurements, the near-term public
health impacts have been negligible for
the events at NRC-licensed operating
power facilities discussed in this
report.’’ Task Force Report, at 15. While
concluding that near-term public health
impacts were negligible, the Task Force
made 26 specific recommendations for
improvements to NRC’s regulatory
programs with regard to unplanned or
unmonitored releases of radioactive
liquids from nuclear power reactors.
The NRC staff has addressed, or is in
the process of addressing, the Task
Force recommendations. See ‘‘Liquid
Release Task Force Recommendations
Implementation Status as of February
26, 2008’’ (ML073230982)
(Implementation Status). Actions taken
in response to Task Force
recommendations have included
revisions to several guidance
documents, development of draft
regulatory guidance on implementation
of the requirements of 10 CFR 20.1406
(i.e. DG–4012),22 revisions to Inspection
Procedure 71122.01, and an evaluation
of whether further action was required
to enhance the performance of SFP telltale drains.23 For example, Regulatory
21 The NRC staff recently completed an inspection
at Indian Point Units 1 and 2. NRC Inspection
Report Nos. 05000003/2007010 and 05000247/
2007010, May 13, 2008 (ML0813404250). The
purpose of the inspection was to assess Entergy’s
site groundwater characterization conclusions and
the radiological significance of Entergy’s discovery
of a spent fuel pool leakage at Units 1 and 2. The
NRC staff concluded that Entergy’s response to the
spent fuel pool leakage was reasonable and
technically sound. The NRC staff stated that ‘‘[t]he
existence of on-site groundwater contamination, as
well as the circumstances surrounding the causes
of leakage and previous opportunities for
identification and intervention, have been reviewed
in detail. Our inspection determined that public
health and safety has not been, nor is likely to be,
adversely affected, and the dose consequence to the
public that can be attributed to current on-site
conditions associated with groundwater
contamination is negligible.’’ Id.
22 DG–4012 was formally issued as Regulatory
Guide 4.21, ‘‘Minimization of Contamination and
Radioactive Waste Generation: Life-Cycle Planning’’
in June 2008.
23 In addition to the NRC’s efforts, the nuclear
industry collectively responded to these incidents
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Guide 4.1 is being revised to provide
guidance to industry for detecting,
evaluating, and monitoring releases
from operating facilities via
unmonitored pathways; to ensure
consistency with current industry
standards and commercially available
radiation detection methodology; to
clarify when a licensee’s radiological
effluent and environmental monitoring
programs should be expanded based on
data or environmental conditions; and
to ensure that leaks and spills will be
detected before radionuclides migrate
offsite via an unmonitored pathway.
Also, Regulatory Guide 1.21 is being
revised to provide a definition of
‘‘significant contamination’’ that should
be documented in a licensee’s
decommissioning records under to 10
CFR 50.75(g); to clarify how to report
summaries of spills and leaks in a
licensee’s Annual Radioactive Effluent
Release Report; to provide guidance on
remediation of onsite contamination;
and to upgrade the capability and scope
of the in-plant radiation monitoring
system to include additional monitoring
locations and the capability to detect
lower risk radionuclides. Further,
Inspection Procedure 71122.01 has been
revised to provide for review of onsite
contamination events, including events
involving groundwater; evaluation of
effluent pathways so that new pathways
are identified and placed in the
licensee’s Offsite Dose Calculation
Manual, as applicable; and inclusion of
limited, defined documentation of
significant radioactive releases to the
environment in inspection reports for
those cases where such events would
not normally be documented under
current inspection guidance. See
Implementation Status (ML073230982).
In addition, on January 22, 2008; 73
FR 3812, the NRC published a proposed
rule that would, in part, amend 10 CFR
part 20 to clarify existing requirements
by explicitly requiring licensees to
conduct their operations to minimize
the introduction of residual
radioactivity into the site, including
subsurface soil and groundwater. This
proposed rule also would include a
requirement that licensees perform
surveys to evaluate the concentrations
and quantities of residual radioactivity
of unplanned, unmonitored releases of radioactive
liquids through the Industry Initiative on
Groundwater Protection (Industry Initiative). The
Industry Initiative has resulted in publication of
voluntary industry guidance on the implementation
of groundwater protection programs at nuclear
power plants. See ‘‘Industry Ground Water
Protection Initiative-Final Guidance Document,’’
NEI–07–07, August 2007 (ML072610036);
‘‘Groundwater Protection Guidelines for Nuclear
Power Plants: Public Edition, EPRI, Palo Alto, CA:
EPRI Doc. No. 1016099, 2008.
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and the potential radiological hazards of
residual radioactivity detected. Id.
While unmonitored, unplanned releases
continue to require the NRC’s and
licensees’ attention, the NRC staff is
confident that this issue will be
adequately addressed through
continued regulatory oversight of
operating and new nuclear reactors and
enhanced through the NRC’s continued
implementation of the Task Force
recommendations. Therefore, the NRC
staff continues to have assurance that no
significant environmental impacts or
safety concerns will result from
extended storage in spent fuel pools.
2. Storage in Dry Casks
With regard to dry cask storage,
studies of the accident risk of dry
storage since 1990 have focused on
specific dry cask storage systems located
at either a generic Pressurized Water
Reactor (PWR) site or a specific Boiling
Water Reactor (BWR) site. In 2004, the
Electric Power Research Institute (EPRI)
performed a Probabilistic Risk
Assessment (PRA) of a bolted dry spent
fuel storage cask at a generic PWR site.
K. Canavan, ‘‘Probabilistic Risk
Assessment (PRA) of Bolted Storage
Casks Updated Quantification and
Analysis Report,’’ Electric Power
Research Institute, Palo Alto, California;
EPRI Doc. No. 1009691, December 2004.
In 2007, the NRC published a pilot PRA
methodology that assessed the risk to
the public and identified the dominant
contributors to risk associated with a
welded canister dry spent fuel storage
system at a specific BWR site. NUREG–
1864, ‘‘A Pilot Probabilistic Risk
Assessment of a Dry Cask Storage
System at a Nuclear Power Plant,’’
March 2007. Both studies calculated the
annual individual radiological risk and
consequences associated with a single
cask lifecycle where the lifecycle is
divided into three phases: loading,
onsite transfer, and onsite storage. The
results of the EPRI study showed that
risk is extremely low with no calculated
early fatalities, a first year risk of latent
cancer fatality of 5.6E–13 per cask, and
subsequent year cancer risk of 1.7E–13
per cask. The NRC study also showed
that risk is extremely low with no
prompt fatalities expected, a first year
risk of latent cancer fatality of 1.8E–12
per cask and subsequent year cancer
risk of 3.2E–14 per cask. The major
contributors to the low risk associated
with dry cask storage are that they are
passive systems, relying on natural air
circulation for cooling, and are
inherently robust massive structures
that are highly damage resistant.
NRC and licensee experience to date
with ISFSIs and with certification of
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casks has indicated that interim storage
of spent fuel at reactor sites can be
safely and effectively conducted using
passive dry storage technology. There
have not been any safety problems
during dry storage. The problems that
have been encountered primarily occur
during cask preparation activities, after
initial loading of spent fuel, but before
placement on the storage pad. One issue
involved the unanticipated collection
and ignition of combustible gas during
cask welding activities. The NRC issued
generic communications in 1996
addressing the problem and providing
direction for preventing its recurrence.
NRC Bulletin 96–04, ‘‘Chemical,
Galvanic, or Other Reactions in Spent
Fuel Storage and Transportation Casks,’’
and NRC Information Notice 96–34:
‘‘Hydrogen Gas Ignition During Closure
Welding of a VSC–24 Multi-Assembly
Sealed Basket.’’ NRC inspection and
review guidance was also revised to
ensure that appropriate measures are in
place to preclude these events. See NRC
Inspection Manual, Inspection
Procedure 60854 Item 60854–02 and
02.03.a.6 and SFPO Interim Staff
Guidance No. 15, dated January 10,
2001.
In addition, issuance of Materials
License No. SNM–2513 for the Private
Fuel Storage, LLC (PFS) facility has
confirmed the feasibility of licensing an
AFR ISFSI under 10 CFR Part 72. While
there are several issues that would have
to be resolved before the PFS AFR ISFSI
could be built and operated,24 the
extensive review of safety and
environmental issues associated with
licensing the PFS facility provides
additional confidence that spent fuel
may be safely stored at an AFR ISFSI for
long periods, after storage at a reactor
site. The PFS facility was licensed for a
24 For example, on September 7, 2006, two
separate Interior Department agencies refused PFS
a lease to use tribal lands to store spent fuel and
refused to grant a right-of-way to access the land.
On July 17, 2007, PFS filed a complaint against the
Interior Department challenging its decisions. The
case has not yet been resolved. Another issue is
associated with the February 2006 (NAS) Report on
the transport of SNF in the United States, which
concluded that while safe transport is technically
viable, ‘‘the societal risks and related institutional
challenges may impinge on the successful
implementation of large-quantity shipping
programs.’’ National Research Council 2006, ‘‘Going
the Distance? The Safe Transport of Spent Nuclear
Fuel and High-Level Radioactive Waste in the
United States,’’ Washington, DC: National Academy
Press, TIC: 217588, at pp. 214. The NAS committee
found that ‘‘malevolent acts against spent fuel and
high-level waste shipment are a major technical and
societal concern,’’ and recommended that ‘‘an
independent examination of security of spent fuel
and high-level waste transportation be carried out
prior to the commencement of large-quantity
shipments to a federal repository or to interim
storage.’’ Id.
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period of 20 years with the potential for
license renewal.
In addition, as noted in its 1990 Waste
Confidence Decision, the Commission
has confidence in the safety and
environmental insignificance of dry
storage at an MRS for 70 years following
a period of 70 years of storage in spent
fuel storage pools (55 FR 38509–38513;
September 18, 1990). Specifically, the
Commission stated:
Under the environmental assessment for
the MRS rule [NUREG–1092], the
Commission has found confidence in the
safety and environmental insignificance of
dry storage of spent fuel for 70 years
following a period of 70 years of storage in
spent fuel storage pools. Thus, this
environmental assessment supports the
proposition that spent fuel may be stored
safely and without significant environmental
impact for a period of up to 140 years if
storage in spent fuel pools occurs first and
the period of dry storage does not exceed 70
years.
Further, a commenter on the 1990
Waste Confidence Decision asserted that
there was reasonable assurance that
spent fuel could be stored safely and
without significant environmental risk
in dry casks at reactor sites for up to 100
years. The Commission responded (55
FR 38482; September 18, 1990):
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The Commission does not dispute a
conclusion that dry spent fuel storage is safe
and environmentally acceptable for a period
of 100 years. Evidence supports safe storage
for this period. A European study published
in 1988 states, ‘‘in conclusion, present-day
technology allows wet or dry storage over
very long periods, and up to 100 years
without undue danger to workers and
population (See Fettel, W., Kaspar, G., and
Guntehr, H., ‘‘Long-Term Storage of Spent
Fuel from Light-Water Reactors’’ (EUR 11866
EN), Executive Summary, p.v., 1988).
Although spent fuel can probably be safely
stored without significant environmental
impact for longer periods, the Commission
does not find it necessary to make a specific
conclusion regarding dry cask storage in this
proceeding, as suggested by the commenter,
in part because the Commission’s Proposed
Fourth Finding states that the period of safe
storage is ‘‘at least’’ 30 years after expiration
of a reactor’s operating license. The
Commission supports timely disposal of
spent fuel and high-level waste in a geologic
repository, and by this decision does not
intend to support storage of spent fuel for an
indefinitely long period.
The Commission also explained the
nature of its finding that spent fuel
could be stored safely and without
significant environmental impacts for at
least 30 years beyond the licensed life
for operation, stating (55 FR 38509;
September 18, 1990):
[I]n using the words ‘‘at least’’ in its
revised Finding Four, the Commission is not
suggesting 30 years beyond the licensed life
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for operation * * * represents any technical
limitation for safe and environmentally
benign storage. Degradation rates of spent
fuel in storage, for example, are slow enough
that it is hard to distinguish by degradation
alone between spent fuel in storage for less
than a decade and spent fuel stored for
several decades.
As explained previously in this
document under the discussion of
Finding 3, the NRC has renewed two
specific ISFSI licenses for an extended
40-year period under exemptions
granted from 10 CFR part 72, which
provides for 20-year renewals. In
addition, NRC is considering a
rulemaking which would provide a 40year license term for an ISFSI with the
possibility of renewal. See License and
Certificate of Compliance Terms, 73 FR
45173; August 4, 2008. Continued
suitability of materials is a prime
consideration for ISFSI license
renewals. As discussed under Finding 3
in this document, the applicants’
evaluation of aging effects on the
structures, systems and components
important to safety, supplemented by
the licensees’ aging management
programs, provided reasonable
assurance of continued safe storage of
spent fuel in these ISFSIs. Thus, these
cases reaffirm the Commission’s
confidence in the safety of interim dry
storage for an extended period. While
these license renewal cases only address
storage for a period of up to 60 years
(20-year initial license, plus 40-year
renewal), studies performed to date
indicate no major issues with dry
storage for up to 100 years. See, e.g.,
NUREG/CR–6831, ‘‘Examination of
Spent PWR Fuel rods after 15 Years in
Dry Storage,’’ (September 2003); J.
Kessler, ‘‘Technical Bases for Extended
Dry Storage of Spent Nuclear Fuel,’’
Electric Power Research Institute, Palo
Alto, California; EPRI Doc. No. 1003416,
December 2002. (55 FR 38509;
September 18, 1990).
3. Terrorism and Spent Fuel
Management
The NRC has, since the 1970s,
regarded spent fuel in storage as a
potential terrorist target and provided
for appropriate security measures.
Before the tragic events of September
11, 2001, spent fuel was well protected
by physical barriers, armed guards,
intrusion detection systems, area
surveillance systems, access controls,
and access authorization requirements
for persons working inside nuclear
power plants and spent fuel storage
facilities. Since September 11, 2001, the
NRC has significantly modified its
requirements, and licensees have
significantly increased their resources to
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59567
further enhance and improve security at
spent fuel storage facilities and nuclear
power plants. See Letter to Senator Pete
V. Domenici from NRC Chairman Nils J.
Diaz, dated March 14, 2005
(ML050280428) (Diaz Letter), at 20.
Consistent with the approach taken at
other categories of nuclear facilities, the
NRC responded to the terrorist attacks of
September 11, 2001 by promptly
developing and requiring security
enhancements for spent fuel storage
both in spent fuel pools and dry casks.
In February 2002, the NRC required
power reactor licensees to enhance
security and improve their capabilities
to respond to terrorist attack. The NRC’s
orders included requirements for spent
fuel pool cooling to deal with the
consequences of potential terrorist
attacks. These enhancements to security
included increased security patrols,
augmented security forces, additional
security posts, increased vehicle
standoff distances, and improved
coordination with law enforcement and
intelligence communities, as well as
strengthened safety-related mitigation
procedures and strategies. The February
2002 orders required licensees to
develop specific guidance and strategies
to maintain or restore spent fuel pool
cooling capabilities using existing or
readily available resources (equipment
and personnel) that can be effectively
implemented under the circumstances
associated with the loss of large areas of
the plant due to large fires and
explosions. The NRC issued additional
orders on security, including security
for spent fuel storage in January and
April of 2003. The NRC subsequently
inspected each facility to verify the
licensee’s implementation, evaluated
inspection findings and, as necessary,
required actions to address any noted
deficiencies. The NRC’s inspection
activities in this area are ongoing. In
2004, the NRC reviewed and approved
revised security plans submitted by
licensees to reflect the implementation
of new security requirements. The
enhanced security at licensee facilities
is routinely inspected using a revised
baseline inspection program, and power
reactor licensees’ capabilities (including
spent fuel pools) are tested in periodic
(every 3 years) force-on-force exercises.
Diaz Letter, at iii, 7, 9.
In 2002, the NRC required power
reactors in decommissioning, wet ISFSIs
and dry storage ISFSIs to enhance
security and improve their capabilities
to respond to, and mitigate the
consequences of, a terrorist attack. In
the same year, the NRC required
licensees transporting more than a
specified amount of spent fuel to
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enhance security during transport. Diaz
Letter, at 7, 8.
In 2002, the NRC also initiated a
classified program on the capability of
nuclear facilities to withstand a terrorist
attack. The early focus of the program
was on power reactors, including spent
fuel pools, and on dry cask storage and
transportation. As the results of that
classified program became available,
NRC provided licensees additional
guidance on the Commission’s
expectations regarding the
implementation of the orders on the
spent fuel mitigation measures. Diaz
Letter, at iv.
More recently, on October 26, 2006;
71 FR 62664, the NRC issued a proposed
rule to improve security measures at
nuclear power reactors. The
Commission is currently considering a
draft final rule. In addition, in 2007 the
NRC issued a final rule revising the
Design Basis Threat, which also
increased the security requirements for
power reactors and their spent fuel
pools (72 FR 12705; March 19, 2007).
i. Spent Fuel Pools
SFPs are extremely robust structures
that are designed to safely contain spent
fuel under a variety of normal, offnormal, and hypothetical accident
conditions (e.g., loss of electrical power,
floods, earthquakes, tornadoes). SFPs
are massive structures made of
reinforced concrete with walls typically
over six feet thick, lined with welded
stainless steel plates to form a generally
leak-tight barrier, fitted with racks to
store the fuel assemblies in a controlled
configuration and provided with
redundant monitoring, cooling and
make-up water systems. Spent fuel
stored in SFPs is typically covered by
about 25 feet of water that serves as both
shielding and an effective protective
cover against impacts directly on the
stored fuel. Diaz Letter, at 2; The
Attorney General of Commonwealth of
Massachusetts, The Attorney General of
California; Denial of Petitions for
Rulemaking, 73 FR 46206; August 8,
2008 (Denial of PRMs).
The post September 11, 2001 studies
noted previously confirm the
effectiveness of additional mitigation
strategies to maintain spent fuel cooling
in the event the pool is drained and its
initial water inventory is reduced or lost
entirely. Based on this recent
information and the implementation of
additional strategies following
September 11, 2001, the probability,
and, accordingly, the risk of an SFP
zirconium fire initiation will be less
than reported in NUREG–1738 and
previous studies. Given the physical
robustness of SFPs, the physical
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security measures, and the SFP
mitigation measures, and based upon
NRC site evaluations of every SFP in the
United States, the NRC has determined
that the risk of an SFP zirconium fire,
whether caused by an accident or a
terrorist attack, is very low. In addition,
the NRC has approved license
amendments and issued safety
evaluations to incorporate mitigation
measures into the plant licensing bases
of all operating nuclear power plants in
the United States. (See Denial of PRMs,
73 FR 46207–08; August 8, 2008).
ii. Dry Storage Casks
Dry storage casks are massive
canisters, either all metal or a
combination of concrete and metal, and
are inherently robust (e.g., some casks
weigh over 100 tons). Storage casks
contain spent fuel in a sealed and
chemically-inert environment. Diaz
Letter, at 3.
The NRC has evaluated the results of
security assessments involving large
commercial aircraft attacks, which were
performed on four prototypical spent
fuel cask designs, and concluded that
the likelihood is very low that a
radioactive release from a spent fuel
storage cask would be significant
enough to cause adverse health
consequences to nearby members of the
public. While differences exist with
storage cask designs, the results of the
security assessments indicate that any
potential radioactive releases were
consistently very low.
The NRC also evaluated the results of
security assessments involving vehicle
bomb and ground assault attacks against
these same four cask designs. The NRC
concluded that while a potential
radiological release was possible, the
size and nature of the release did not
require the Commission to immediately
implement additional security
compensatory measures. Accordingly,
the NRC staff has recommended, and
the Commission has approved,
development of risk-informed,
performance-based security
requirements and associated guidance
applicable to all ISFSI licensees (general
and specific), which would enhance
existing security requirements. This
proposed ISFSI security rulemaking
would apply to all existing and future
licensees. See SECY–07–0148,
‘‘Independent Spent Fuel Storage
Installation Security Requirements for
Radiological Sabotage,’’ (August 28,
2007) (ML080250294); Staff
Requirements—SECY–07–0148–
Independent Spent Fuel Storage
Installation Security Requirements for
Radiological Sabotage, (December 18,
2007) (ML073530119). In addition, the
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NRC has noted that distributing spent
fuel over many discrete storage casks
(e.g., in an ISFSI) limits the total
quantity of spent fuel that could
potentially be attacked at any one time,
due to limits on the number of
adversaries and the amount of
equipment they can reasonably bring
with them. Diaz Letter, at 17, 18, 22.
iii. Conclusion-Security
Today, spent fuel is better protected
than ever. The results of security
assessments, existing security
regulations, and the additional
protective and mitigative measures
imposed since September 11, 2001,
provide high assurance that the spent
fuel in both spent fuel pools and in dry
storage casks will be adequately
protected. The ongoing efforts to update
the ISFSI security requirements to
address the current threat environment
will integrate the additional protective
measures imposed since September 11,
2001, into a formalized regulatory
framework in a transparent manner that
balances public participation against
protection of exploitable information.
4. Conclusion
The Commission concludes that the
events that have occurred since the last
formal review of its Waste Confidence
Decision in 1990 provide support for a
continued finding of reasonable
assurance that, if necessary, spent fuel
generated in any reactor can be stored
safely and without significant
environmental impacts for at least 30
years beyond the licensed life for
operation of that reactor at its spent fuel
storage basin. Specifically, NRC finds
continued support for this finding in the
extensive study of spent fuel pool
storage that has occurred since 1990,
and the continued regulatory oversight
of operating plants, which has been
enhanced by the recommendations of
the Liquid Release Task Force.
Further, the Commission is proposing
to revise Finding 2 to reflect its
expectation that repository capacity will
be available within 50–60 years of the
licensed life for operation of any reactor.
Consistent with this, the Commission is
proposing to revise Finding 4 to reflect
that spent fuel can be safely stored in
dry casks for a period of at least 60 years
without significant environmental
impacts. Specifically, the inherent
robustness and passive nature of dry
cask storage—coupled with the
operating experience and research
accumulated to date, the 70 year finding
in the Environmental Assessment for
the MRS rule, and the renewal of two
specific Part 72 licenses for an extended
40 year period (for a total ISFSI
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operating life of at least 60 years)—
support this finding. Further, this
finding is consistent with the
Commission’s statements in 1990 that it
did not dispute that dry spent fuel
storage is safe and environmentally
acceptable for a period of 100 years (55
FR 38482; September 18, 1990); that
spent fuel could probably be safely
stored without significant
environmental impact for periods longer
than 30 years (55 FR 38482; September
18, 1990); and that the 30 year finding
did not represent a technical limitation
for safe and environmentally benign
storage (55 FR 38509; September 18,
1990).
C. Finding 4
The Commission finds reasonable
assurance that, if necessary, spent fuel
generated in any reactor can be stored
safely and without significant
environmental impacts for at least 60
years beyond the licensed life for
operation (which may include the term
of a revised or renewed license) of that
reactor in a combination of storage in its
spent fuel storage basin and either
onsite or offsite independent spent fuel
storage installations.
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V. Finding 5: The Commission Finds
Reasonable Assurance That Safe
Independent Onsite Spent Fuel Storage
or Offsite Spent Fuel Storage Will Be
Made Available if Such Storage
Capacity Is Needed
A. Bases for Finding 5
The focus of this finding is on the
timeliness of the availability of facilities
for storage of spent fuel when the fuel
can no longer be stored in the reactor’s
spent fuel storage pool. At the outset of
the Waste Confidence proceeding there
was uncertainty as to who had the
responsibility for providing this storage,
with the expectation that the Federal
government would provide away-fromreactor facilities for this purpose.
However, in 1981 DOE announced its
decision to discontinue the AFR
program. The Commission found that
the industry’s response to this change
was a general commitment to do
whatever was necessary to avoid
shutting down reactors. The NWPA
provided Federal policy on this issue by
defining public and private
responsibilities for spent fuel storage
and by providing for an MRS program,
an interim storage program at a Federal
facility for utilities for whom there was
no other solution, and a research,
development, and demonstration
program for dry storage designed to
assist utilities in using dry storage
methods. These NWPA provisions,
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together with the availability of ISFSI
technology and the fact that the Part 72
regulations and licensing procedures
were in place gave the Commission
assurance that safe independent onsite
or offsite spent fuel storage would be
available when needed (49 FR 34686–
34687; August 31, 1984).
In 1990, the Commission saw no need
to revise this finding. It recognized that
the NWPAA had undermined the ability
of an MRS to provide for timely storage
by linking the MRS to the siting and
schedule for a repository (e.g., DOE was
not permitted to select an MRS site until
it had recommended a site for
development as a repository). However,
it found that whatever the uncertainty
introduced by these NWPAA
provisions, it was more than
compensated for by operational and
planned spent fuel pool expansions and
dry storage investments by the utilities
themselves. The Commission also
considered the fact that it seemed
probable that DOE would not meet the
1998 deadline for beginning to remove
spent fuel from the utilities. This did
not undermine the Commission’s
confidence that storage capacity would
be made available as needed because
NRC licensees cannot abrogate their
safety responsibilities and would
remain responsible for the stored fuel
despite any possible contractual
disputes with DOE. The Commission
noted that DOE’s research program had
successfully demonstrated the viability
of dry storage technology and that the
utilities had continued to add dry
storage capacity at their sites. Further,
the Commission believed that there
would be sufficient time for
construction and licensing of any
additional storage capacity that might be
needed due to operating license
renewals (55 FR 38513–38514;
September 18, 1990).
B. Evaluation of Finding 5
In 1990 the Commission reaffirmed
Finding 5 despite significant
uncertainties regarding DOE’s MRS and
repository programs, and the potential
for the renewal of reactor operating
licenses. Specifically, in reaffirming
Finding 5 the Commission stated:
In summary, the Commission finds no
basis to change the Fifth Finding in its Waste
Confidence Decision. Changes by the
NWPAA, which may lessen the likelihood of
an MRS facility, and the potential for some
slippage in repository availability to the first
quarter of the twenty-first century * * * are
more than offset by the continued success of
utilities in providing safe at-reactor-site
storage capacity in reactor pools and their
progress in providing independent onsite
storage. Therefore, the Commission continues
to find ‘‘* * * reasonable assurance that safe
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59569
independent onsite spent fuel storage or
offsite spent fuel storage will be made
available if such storage is needed.’’ (55 FR
38514; September 18, 1990).
In reaching this conclusion, the
Commission stressed that—regardless of
the outcome of possible contractual
disputes between DOE and utilities—the
utilities possessing spent fuel could not
abrogate their safety responsibilities. In
addition, the Commission cited to three
situations where dry storage had been
licensed at specific reactor sites (Surry,
H.B. Robinson, and Oconee), and to
several additional applications for
licenses permitting dry cask storage at
reactor sites. Id.
1. Operating and Decommissioned
Reactors
As in 1990, the NRC staff is not aware
of any current operating reactor that has
an insurmountable problem with safe
storage of SNF. The options successfully
being used to increase onsite storage
capacity are spent fuel pool re-racking
and fuel-pin consolidation, as well as
onsite dry cask storage. While there are
cases where a licensee’s ability to use an
onsite dry cask storage option may be
limited by State or Public Utility
Commission authorities, the NRC is
successfully regulating six fully
decommissioned reactor sites that
contain ISFSIs licensed under either the
general or specific license provisions of
Part 72. The NRC has not encountered
any management problems associated
with the ISFSIs at these six
decommissioned reactor sites and has
discussed plans to build generally
licensed ISFSI’s with two additional
licensees that are in the process of
decommissioning.
In addition, since 1990, the NRC has
renewed the specific Part 72 ISFSI
licenses for both the Surry and H.B.
Robinson plants for an extended 40-year
period, instead of the 20-year renewal
period currently provided for under Part
72. As discussed previously under
Finding 3, the Commission authorized
the staff to grant exemptions to allow
the 40-year renewal period after the staff
reviewed the applicants’ evaluations of
aging effects on the structures, systems,
and components important to safety,
and determined that the evaluations,
supplemented by the licensees’ aging
management programs, provided
reasonable assurance of continued safe
storage of spent fuel in these ISFSIs. See
SECY–04–0175, ‘‘Options for
Addressing the Surry Independent
Spent Fuel Storage Installation LicenseRenewal Period Exemption Request,’’
September 28, 2004 (ML041830697).
With regard to the uncertainty
surrounding the contractual disputes
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between DOE and the utilities
referenced by the Commission in 1990,
the U.S. Court of Appeals for the District
of Columbia Circuit has since held that
DOE’s statutory and contractual
obligation to accept the waste no later
than January 31, 1998, was
unconditional. Indiana Michigan Power
Co. v. DOE, 88 F.3d 1272 (DC Cir. 1996).
Subsequently, the utilities have
continued to manage spent fuel safely in
spent fuel pools and ISFSIs and have
received damage awards as determined
in lawsuits brought before the U.S.
Federal Claims Court, see, e.g., System
Fuels Inc. v. U.S., 78 Fed. Cl. 769
(October 11, 2007).
In total, there are currently 51
licensed ISFSIs being managed at 47
sites across the country, under either
specific or general Part 72 NRC licenses.
As explained in the discussion of
Finding 3, NRC’s inspection findings do
not indicate unique management
problems at any currently operating
ISFSI regulated by the NRC. Generally,
the types of issues identified through
NRC inspections of ISFSIs are similar to
issues identified for Part 50 licensees.
Most issues are identified early in the
operational phase of the dry cask storage
process, during loading preparations
and actual spent fuel loading activities.
Once an ISFSI is fully loaded with spent
fuel, relatively few inspection issues are
identified due to the passive nature of
these facilities.
Finally, on June 3, 2008, the DOE
submitted its license application for the
proposed Yucca Mountain HLW
repository, and on September 8, 2008,
NRC Staff notified DOE that it found the
application acceptable for docketing (73
FR 53284; September 15, 2008). While
the Commission can express no view on
the quality or acceptability of the
application in this evaluation of waste
confidence, its submittal is evidence of
a continued Federal commitment to
providing for ultimate disposal of spent
fuel.
2. New Reactors
With regard to the status of contracts
requiring DOE to take title to and
possession of the irradiated fuel
generated by utilities, the NRC staff
understands that DOE has drafted
language for a new amendment to the
standard DOE-utility contracts.
According to reports in the trade press,
the revised contract will require DOE to
accept spent fuel from any new nuclear
power plants ten years after expiration
of the operating license or any extension
of the operating license. The utilities
have not publicly expressed an opinion
on the revised contracts to date. See
Energy Daily, ED Vol. 36 No. 107,
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Thursday, June 5, 2008. In addition,
before licensing a new reactor the NRC
must find that the applicant has entered
into a contract with DOE for removal of
spent fuel from the reactor site, or
receive written affirmation from DOE
that the applicant is actively and in
good faith negotiating with the DOE for
such a contract. NWPA, Sec.302(b). This
finding will be documented in the
Safety Evaluation Report produced by
the NRC staff in response to specific
license applications for new reactors.
The near-term design certifications
and existing or planned combined
license applications do not undermine
the Commission’s confidence that spent
fuel storage will become available when
such storage is needed. These facilities
will use the same or similar fuel
assembly designs as the nuclear power
plants currently operating in the United
States and the spent fuel will be
accommodated using existing or similar
transportation and storage containers.
As discussed under Finding 1, the NRC
is also engaged in preliminary
interactions with DOE on ‘‘advanced
reactors’’ (e.g., gas-cooled or liquidmetal cooled technologies). The fuel and
reactor components associated with
some of these advanced reactor designs
would likely require different storage,
transportation and disposal packages
than those currently used for spent fuel
from light-water reactors. The possible
need for further assessment of
performance and storage capability for
new and different fuels would depend
on the number and types of reactors
actually licensed and operated. There is
currently a high uncertainty regarding
the growth of advanced reactors in the
U.S. In addition, the need to consider
waste disposal as part of the overall
research and development activities for
advanced reactors is recognized and
included in the activities of DOE,
designers, and the NRC (see, for
example, ‘‘A Technology Roadmap for
Generation IV Nuclear Energy Systems,’’
issued by the U.S. DOE Nuclear Energy
Research Advisory Committee and the
Generation IV International Forum,
December 2002).
Nonetheless, the addition of new
plants will undoubtedly add to the
amount of spent fuel requiring disposal.
This fact does not affect the
Commission’s confidence that safe
storage options will be available when
needed because, as the Commission
stated in 1990—utilities have sought to
meet storage capacity needs at their
respective reactor sites (55 FR 38514;
September 18, 1990). Specifically, as
discussed under Finding 3, NRC
licensees have successfully and safely
used onsite storage capacity in spent
PO 00000
Frm 00031
Fmt 4702
Sfmt 4702
fuel pools and, more recently, in onsite
ISFSIs licensed under 10 CFR part 72.
In addition, while construction and
operation of an MRS facility by DOE is
uncertain, the NRC has promulgated
regulations that provide a framework for
licensing such a facility. See 10 CFR
part 72 (53 FR 31651; August 19, 1988).
Further, while there are unresolved
issues that prevent construction and
operation of the PFS facility, the
extensive safety and environmental
reviews that supported issuance of an
NRC license for PFS provide added
confidence that licensing of a private
AFR facility is technically feasible.
The Commission concludes that the
events that have occurred since the last
formal review of the Waste Confidence
Decision in 1990, provide support for a
continued finding of reasonable
assurance that safe independent onsite
spent fuel storage or offsite spent fuel
storage will be made available if such
storage capacity is needed. Specifically,
since 1990, NRC licensees have
continued to develop and successfully
use onsite storage capacity in the form
of pool and dry cask storage in a safe
and environmentally sound fashion.
With regard to offsite storage, the
Commission licensed the PFS facility
after an extensive safety and
environmental review process, and a
protracted adjudicatory hearing that
resulted in over 70 ASLB and
Commission decisions. The Commission
also has a regulatory framework in place
for licensing an MRS facility, should the
need arise. In addition, based on
discussions with the DOE and recent
reports in the trade press, the NRC
understands that a new standard
contract providing for disposal of spent
fuel by DOE is currently being prepared.
This, coupled with the recent
submission of a license application for
the proposed Yucca Mountain
repository, provides the NRC with
continued confidence in the Federal
commitment to providing for the
ultimate disposal of spent fuel.
For all the above reasons, the Commission
proposes to reaffirm Finding 5.
Dated at Rockville, Maryland, this 29th day
of September 2008.
For the Nuclear Regulatory Commission.
Annette Vietti-Cook,
Secretary of the Commission.
[FR Doc. E8–23381 Filed 10–8–08; 8:45 am]
BILLING CODE 7590–01–P
E:\FR\FM\09OCP1.SGM
09OCP1
Agencies
[Federal Register Volume 73, Number 197 (Thursday, October 9, 2008)]
[Proposed Rules]
[Pages 59551-59570]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-23381]
-----------------------------------------------------------------------
NUCLEAR REGULATORY COMMISSION
10 CFR Part 51
[Docket ID-2008-0482]
Waste Confidence Decision Update
AGENCY: Nuclear Regulatory Commission.
ACTION: Update and proposed revision of Waste Confidence Decision.
-----------------------------------------------------------------------
SUMMARY: On September 18, 1990, the Nuclear Regulatory Commission (NRC
or Commission) issued a decision reaffirming and revising, in part, the
five Waste Confidence findings reached in its 1984 Waste Confidence
Decision. The 1984 decision and the 1990 review were products of
rulemaking proceedings designed to assess the degree of assurance that
radioactive wastes generated by nuclear power plants can be safely
disposed of, to determine when such disposal or offsite storage would
be available, and to determine whether radioactive wastes can be safely
stored onsite past the expiration of existing facility licenses until
offsite disposal or storage is available. The Commission has decided to
again undertake a review of its Waste Confidence findings as part of an
effort to enhance the efficiency of combined operating license
proceedings for applications for nuclear power plants anticipated in
the near future. To assure that its Waste Confidence findings are up-
to-date, the Commission has prepared an update of the findings and
proposes to revise two of the findings. The purpose of this notice is
to seek public comment on the update and the proposed revisions.
The Commission proposes that the second and fourth findings in the
Waste Confidence Decision be revised as follows:
Finding 2: The Commission finds reasonable assurance that
sufficient mined geologic repository capacity can reasonably be
expected to be available within 50-60 years beyond the licensed life
for operation (which may include the term of a revised or renewed
license) of any reactor to dispose of the commercial high-level
radioactive waste and spent fuel originating in such reactor and
generated up to that time.
Finding 4: The Commission finds reasonable assurance that, if
necessary, spent fuel generated in any reactor can be stored safely
without significant environmental impacts for at least 60 years beyond
the licensed life for operation (which may include the term of a
revised or renewed license) of that reactor in a combination of storage
in its spent fuel storage basin and either onsite or offsite
independent spent fuel storage installations.
The Commission proposes to reaffirm the remaining findings. Each
finding, any proposed revisions, and the reasons for revising or
reaffirming them are discussed below. In keeping with the proposed
revised Findings 2 and 4, the Commission is publishing concurrently
[[Page 59552]]
in this issue of the Federal Register proposed conforming amendments to
its 10 CFR part 51 rule providing its generic determination on the
environmental impacts of storage of spent fuel at, or away from,
reactor sites after the expiration of reactor operating licenses.
DATES: Submit comments by December 8, 2008. Comments received after
this date will be considered if it is practical to do so, but NRC is
able to assure consideration only for comments received on or before
this date.
ADDRESSES: You may submit comments by any one of the following methods.
Comments submitted in writing or in electronic form will be made
available for public inspection. Because your comments will not be
edited to remove any identifying or contact information, the NRC
cautions you against including any information in your submission that
you do not want to be publicly disclosed.
Federal e-Rulemaking Portal: Go to https://www.regulations.gov and
search for documents filed under Docket ID [NRC-2008-0482]. Address
questions about NRC dockets to Carol Gallagher 301-415-5905; e-mail
Carol.Gallagher@nrc.gov.
Mail comments to: Secretary, U.S. Nuclear Regulatory Commission,
Washington, DC 20555-0001, ATTN: Rulemakings and Adjudications Staff.
E-mail comments to: Rulemaking.Comments@nrc.gov. If you do not
receive a reply e-mail confirming that we have received your comments,
contact us directly at 301-415-1677.
Hand deliver comments to: 11555 Rockville Pike, Rockville, Maryland
20852, between 7:30 am and 4:15 pm Federal workdays. (Telephone 301-
415-1677).
Fax comments to: Secretary, U.S. Nuclear Regulatory Commission at
301-415-1101.
You can access publicly available documents related to this
document using the following methods:
NRC's Public Document Room (PDR): The public may examine and have
copied for a fee publicly available documents at the NRC's PDR, Public
File Area O1 F21, One White Flint North, 11555 Rockville Pike,
Rockville, Maryland.
NRC's Agencywide Documents Access and Management System (ADAMS):
Publicly available documents created or received at the NRC are
available electronically at the NRC's Electronic Reading Room at http:/
/www.nrc.gov/reading-rm/adams.html. From this page, the public can gain
entry into ADAMS, which provides text and image files of NRC's public
documents. If you do not have access to ADAMS or if there are problems
in accessing the documents located in ADAMS, contact the NRC's PDR
reference staff at 1-800-397-4209, 301-415-4737, or by e-mail to
pdr.resource@nrc.gov.
FOR FURTHER INFORMATION CONTACT: Neil Jensen, Office of the General
Counsel, U.S. Nuclear Regulatory Commission, Washington, DC 20555-0001,
telephone 301-415-8480, e-mail, neil.jensen@nrnc.gov.
SUPPLEMENTARY INFORMATION:
Background
In October 1979, the NRC initiated a rulemaking proceeding, known
as the Waste Confidence proceeding, to assess its degree of assurance
that radioactive wastes produced by nuclear power plants can be safely
disposed of, to determine when such disposal or offsite storage will be
available, and to determine whether radioactive wastes can be safely
stored onsite past the expiration of existing facility licenses until
offsite disposal or storage is available (44 FR 1372; October 25,
1979). The Commission's action responded to a remand from the U.S.
Court of Appeals for the District of Columbia Circuit in State of
Minnesota v. NRC, 602 F.2d 412 (1979). That case raised the question
whether an offsite storage or disposal solution would be available for
the spent nuclear fuel (SNF) produced at the Vermont Yankee and Prairie
Island reactors at the expiration of the licenses for those facilities
in the 2007-2009 period or, if not, whether the SNF could be stored at
those reactor sites until an offsite solution was available. The Waste
Confidence proceeding also stemmed from the Commission's statement, in
its denial of a petition for rulemaking filed by the Natural Resources
Defense Council (NRDC), that it intended to reassess periodically its
finding of reasonable assurance that methods of safe permanent disposal
of high-level radioactive waste (HLW) would be available when they were
needed. Further, the Commission stated that, as a matter of policy, it
``would not continue to license reactors if it did not have reasonable
confidence that the wastes can and will in due course be disposed of
safely.'' (42 FR 34391, 34393; July 5, 1977, pet. for rev. dismissed
sub nom. NRDC v. NRC, 582 F.2d 166 (2d Cir. 1978)).\1\
---------------------------------------------------------------------------
\1\ The NRDC petition asserted that the Atomic Energy Act of
1954, as amended (AEA), required NRC to make a finding, before
issuing an operating license for a reactor, that permanent disposal
of HLW generated by that reactor can be accomplished safely. The
Commission found that the AEA did not require this safety finding to
be made in the context of reactor licensing, but rather in the
context of the licensing of a geologic disposal facility.
---------------------------------------------------------------------------
The Waste Confidence proceeding resulted in five Waste Confidence
findings which the Commission issued August 31, 1984; 49 FR 34658:
(1) The Commission finds reasonable assurance that safe disposal of
HLW and SNF in a mined geologic repository is technically feasible;
(2) The Commission finds reasonable assurance that one or more
mined geologic repositories for commercial HLW and SNF will be
available by the years 2007-2009, and that sufficient repository
capacity will be available within 30 years beyond the expiration of any
reactor operating license to dispose of existing commercial HLW and SNF
originating in such reactor and generated up to that time;
(3) The Commission finds reasonable assurance that HLW and SNF will
be managed in a safe manner until sufficient repository capacity is
available to assure the safe disposal of all HLW and SNF;
(4) The Commission finds reasonable assurance that, if necessary,
spent fuel generated in any reactor can be stored safely and without
significant environmental impacts for at least 30 years beyond the
expiration of that reactor's operating license at that reactor's spent
fuel storage basin, or at either onsite or offsite independent spent
fuel storage installations (ISFSIs);
(5) The Commission finds reasonable assurance that safe independent
onsite or offsite spent fuel storage will be made available if such
storage capacity is needed.
Based on these findings, the Commission amended 10 CFR part 51 of
its regulations to provide a generic determination, codified in 10 CFR
51.23(a), that for at least 30 years beyond the expiration of reactor
operating licenses, no significant environmental impacts will result
from the storage of spent fuel in reactor facility storage pools or
ISFSIs located at reactor or away-from-reactor sites.
The Commission conducted a review of its findings in 1989-1990
which resulted in the revision of the second and fourth findings to
reflect revised expectations for the date of availability of the first
repository, and to clarify that the expiration of a reactor's operating
license referred to the full 40 year initial license for operation, as
well as any additional term of a revised or renewed license. These
findings are:
[[Page 59553]]
(2) The Commission finds reasonable assurance that at least one
mined geologic repository will be available within the first quarter of
the twenty-first century, and sufficient repository capacity will be
available within 30 years beyond the licensed life for operation (which
may include the term of a revised or renewed license) of any reactor to
dispose of the commercial HLW and SNF originating in such reactor and
generated up to that time;
(4) The Commission finds reasonable assurance that, if necessary,
spent fuel generated in any reactor can be stored safely and without
significant environmental impacts for at least 30 years beyond the
licensed life for operation (which may include the term of a revised or
renewed license) of that reactor at its spent fuel storage basin, or at
either onsite or offsite ISFSIs.
The Commission amended the generic determination made in 10 CFR
51.23(a) consistent with these revised findings (55 FR 38472; September
18, 1990):
The Commission has made a generic determination that, if
necessary, spent fuel generated in any reactor can be stored safely
and without significant environmental impacts for at least 30 years
beyond the licensed life for operation (which may include the term
of a revised or renewed license) of that reactor at its spent fuel
storage basin or at either onsite or offsite [ISFSIs]. Further, the
Commission believes there is reasonable assurance that at least one
mined geologic repository will be available within the first quarter
of the twenty-first century, and sufficient repository capacity will
be available within 30 years beyond the licensed life for operation
of any reactor to dispose of the commercial [HLW and SNF]
originating in such reactor and generated up to that time.
This generic determination is applied in licensing proceedings
conducted under 10 CFR Parts 50, 52, 54 and 72. See 10 CFR 51.23
(2008).
In 1999, the Commission reviewed its Waste Confidence findings and
concluded that experience and developments since 1990 had confirmed the
findings and made a comprehensive reevaluation of the findings
unnecessary. It also stated that it would consider undertaking such a
reevaluation when the impending repository development and regulatory
activities run their course or if significant and pertinent unexpected
events occur, raising substantial doubt about the continuing validity
of the Waste Confidence findings (64 FR 68005; December 6, 1999).
The Commission does not believe that the criteria set in 1999 for
reopening the Waste Confidence findings have been met. However, the
Commission is now preparing to conduct a significant number of
proceedings on combined construction permit and operating license (COL)
applications for new reactors. The Commission anticipates that the
issue of waste confidence may be raised in those proceedings and
desires to take a fresh look at its Waste Confidence findings to take
into account developments since 1990. For this purpose, the Commission
has prepared this update of the Waste Confidence findings and now
proposes the following revisions of Findings 2 and 4:
(2) The Commission finds reasonable assurance that sufficient mined
geologic repository capacity can reasonably be expected to be available
within 50-60 years beyond the licensed life for operation (which may
include the term of a revised or renewed license) of any reactor to
dispose of the commercial HLW and SNF originating in such reactor and
generated up to that time.
(4) The Commission finds reasonable assurance that, if necessary,
spent fuel generated in any reactor can be stored safely and without
significant environmental impacts for at least 60 years beyond the
licensed life for operation (which may include the term of a revised or
renewed license) of that reactor in a combination of storage in its
spent fuel storage basin and either onsite or offsite ISFSIs.
The update restates and supplements the bases for the earlier
findings. The Commission seeks public comment on the update and on its
proposed revisions of Findings 2 and 4.
The Commission is also publishing concurrently in this issue of the
Federal Register a proposed rule revising 10 CFR 51.23(a) to conform
with the proposed revisions of Findings 2 and 4.
I. Finding 1: The Commission Finds Reasonable Assurance That Safe
Disposal of High-Level Radioactive Waste and Spent Fuel in a Mined
Geologic Repository Is Technically Feasible
A. Bases for Finding 1
The Commission reached this finding in 1984 and reaffirmed it in
1990. The focus of this finding is on whether safe disposal of HLW and
SNF is technically possible using existing technology and without a
need for any fundamental breakthroughs in science and technology. To
reach this finding, the Commission considered the basic features of a
repository designed for a multi-barrier system for waste isolation and
examined the problems the Department of Energy (DOE) would need to
resolve in developing a final design for such a repository. The
Commission identified three major technical problems: (1) The selection
of a suitable geologic setting as host for a technically acceptable
repository site; (2) the development of waste packages that will
contain the waste until the fission products are greatly reduced; and
(3) the development of engineered barriers, such as backfilling and
sealing of the drifts and shafts of the repository, that can
effectively retard migration of radionuclides out of the repository (49
FR 34667; August 31, 1984).
DOE's selection of a suitable geologic setting has been governed by
Congress' passage of the Nuclear Waste Policy Act of 1982, Public Law
97-425, 42 U.S.C. 10101 et seq. (NWPA) and by the 1987 amendments to
NWPA in the Nuclear Waste Policy Amendments Act, Pub. L. 100-202
(NWPAA). DOE had begun to explore potential repository sites before the
NWPA, but that Act set in place a formal process and schedule for the
development of two geologic repositories. The following brief summary
of key provisions of these Acts may assist readers in understanding the
process followed by DOE in locating a suitable geologic setting.
As initially enacted, NWPA directed DOE to issue guidelines for the
recommendation of sites and then to nominate at least 5 sites as being
suitable for site characterization for selection as the first
repository site and, not later than January 1, 1985, to recommend 3 of
those sites to the President for characterization as candidate sites.
Section 112 of NWPA, 42 U.S.C. 10132. Not later than July 1, 1989, DOE
was to again nominate 5 sites and recommend 3 of them to the President
for characterization for selection of the second repository. Id. DOE
was then to carry out site characterization activities for approved
sites. Section 113 of NWPA, 42 U.S.C. 10133. Following site
characterization, DOE was then to recommend sites to the President as
suitable for development as repositories and the President was to
recommend one site to the Congress by March 31, 1987, and another site
by March 31, 1989, for development as the first two repositories.
Section 114 of NWPA, 42 U.S.C. 10134. States and affected Indian tribes
were given the opportunity to object, but if the recommendations were
approved by Congress, DOE was then to submit applications for a
construction authorization to NRC. Id. NRC was given until January 1,
1989, to reach a decision on the first application and until January 1,
1992, on the second. The Commission was directed to prohibit the
emplacement in the first repository of more than 70,000 metric tons of
heavy metal (MTHM) until a
[[Page 59554]]
second repository was in operation. Id. The 1987 NWPAA, inter alia,
restricted site characterization solely to a site at Yucca Mountain, NV
(YM) and terminated the program for a second repository. The NWPAA
provided that if DOE at any time determines YM to be unsuitable for
development as a repository, DOE must report to Congress its
recommendations for further action to assure the safe, permanent
disposal of SNF and HLW, including the need for new legislation.
Section 113 of NWPA, as amended, 42 U.S.C. 10133.
In 1984, the Commission reviewed DOE's site exploration program and
concluded that it was providing information on site characteristics at
a sufficiently large number and variety of sites and geologic media to
support the expectation that one or more technically acceptable sites
would be identified (49 FR 34668; August 31, 1984). In 1990, the
Commission noted that the 1987 amendment of NWPA that focused solely on
the YM site carried the potential for considerable delay in opening a
repository if that site were found to be unlicenseable. However, the
possibility of that delay did not undermine the Commission's confidence
that a technically acceptable site would be located, either at YM or
elsewhere. The Commission observed that the NRC staff had provided
extensive comments on DOE's draft environmental assessments of the 9
sites it had identified as being potentially acceptable and on the
final environmental assessments for the 5 sites nominated.\2\ NRC had
not identified any fundamental technical flaw or disqualifying factor
which would render any of the sites unsuitable for characterization or
potentially unlicenseable, although NRC noted that many issues would
need to be resolved during site characterization for YM or any other
site (55 FR 38486; September 18, 1990).
---------------------------------------------------------------------------
\2\ Under the program established by the initial NWPA, DOE had
nominated sites at Hanford WA, Yucca Mountain NV, Deaf Smith County
TX, Davis Canyon UT, and Richton Dome MS, and had recommended the
first 3 sites for site characterization.
---------------------------------------------------------------------------
With respect to the development of effective waste packages, the
Commission, in 1984, reviewed DOE's scientific and engineering program
on this subject. The Commission also considered whether the possibility
of renewed reprocessing of SNF might alter the technical feasibility of
achieving a suitable waste package because of the need to accommodate a
waste form other than spent fuel. The Commission concluded that the
studies of DOE and others demonstrated that the chemical and physical
properties of SNF and HLW can be sufficiently understood to permit the
design of a suitable waste package and that the possibility of
commercial reprocessing would not substantially affect this conclusion
(49 FR 34671; August 31, 1984). In 1990, the Commission reviewed
continued research and experimentation on waste packages that were
undertaken by DOE in other countries, particularly Sweden and Canada.
NRC noted that DOE had narrowed the range of waste package designs to a
design tailored for unsaturated tuff at the YM site due to the 1987
redirection of the HLW program. NRC also noted that some reprocessing
wastes from the defense program and the West Valley Demonstration
Project were now anticipated to be disposed in the repository. However,
NRC remained confident that, given a range of waste forms and
conservative test conditions, the technology is available to design
acceptable waste packages (55 FR 38489; September 18, 1990).
With respect to the development of effective engineered barriers,
the Commission's confidence in 1984 rested upon its consideration of
DOE's ongoing research and development activities regarding backfill
materials and borehole and shaft sealants which led it to the
conclusion that these activities provided a basis for reasonable
assurance that engineered barriers can be developed to isolate or
retard radioactive material released by the waste package (49 FR 34671;
August 31, 1984). In 1990, although DOE's research had narrowed to
focus on YM, the Commission continued to have confidence that backfill
or packing materials can be developed as needed for the underground
facility and waste package, and that an acceptable seal can be
developed for candidate sites in different geologic media (55 FR 38489-
38490; September 18, 1990).
B. Evaluation of Finding 1
There remains high confidence among the scientific and technical
community engaged in waste management that safe geologic disposal is
achievable with currently available technology. See, e.g., National
Research Council, ``Technical Bases for Yucca Mountain Standards,''
1995. No insurmountable technical or scientific problem has emerged to
disturb this confidence that safe disposal of SNF and HLW can be
achieved in a mined geologic repository. To the contrary, there has
been significant progress in the enhancement of scientific
understanding and technological development needed for geologic
disposal over the past 18 years. There is now a much deeper
understanding of processes that affect the ability of repositories to
isolate waste over long periods. Id. at 71-72; International Atomic
Energy Agency (IAEA), ``Scientific and Technical Basis for the Geologic
Disposal of Radioactive Wastes, Technical Reports Series No. 413,''
2003. The ability to characterize and quantitatively assess the
capabilities of geologic and engineered barriers has been repeatedly
demonstrated. NRC, ``Disposal of High-Level Radioactive Wastes in a
Proposed Geologic Repository at Yucca Mountain, Nevada; Proposed
Rule,'' (64 FR 8640, 8649; February 22, 1999); Organization for
Economic Cooperation and Development, Nuclear Energy Agency, ``Lessons
Learned from Ten Performance Assessment Studies,'' 1997. Specific sites
have been investigated and extensive experience has been gained in
underground engineering. IAEA, ``Radioactive Waste Management Studies
and Trends, IAEA/WMDB/ST/4,'' 2005; IAEA, ``The Use of Scientific and
Technical Results from Underground Research Laboratory Investigations
for the Geologic Disposal of Radioactive Waste, IAEA-TECDOC-1243,''
2001. These advances and others throughout the world, in underground
research laboratories, continue to confirm the soundness of the basic
concept of deep geologic disposal. IAEA, ``Joint Convention on Safety
of Spent Fuel Management and on Safety of Radioactive Waste Management,
INFCIRC/546,'' 1997.
In the United States, the technical approach for safe HLW disposal
has remained unchanged for several decades: Use a deep geologic
repository containing natural barriers to hold canisters of HLW with
additional engineered barriers to further retard radionuclide release.
Although some specifics in this technical approach have changed in
response to new knowledge (e.g., engineered backfill was removed as a
design concept for YM in the late 1990s in response to enhanced
understandings of heat and water transfer processes in the near-field
drift environment), safe disposal continues to appear to be a feasible
goal with current technology. Assessments for long-term performance of
a potential repository at YM were conducted by DOE in 1998 (DOE/RW-
0508, Viability Assessment) and 2002 (DOE/RW-0539, Site
Recommendation). These assessments used existing technology and
available scientific information, and did not identify areas where
fundamental
[[Page 59555]]
breakthroughs in science or technology were needed to support the
assessments.
With respect to the issue of identifying a suitable geologic
setting as host for a technically acceptable site, DOE made its
suitability determination for the YM site in 2002. On June 3, 2008, DOE
submitted the application to NRC and on September 08, 2008, NRC Staff
notified DOE that it found the application acceptable for docketing (73
FR 53284; September 15, 2008). Whether this particular site will be
found to be technically acceptable must await the outcome of an NRC
licensing proceeding. The 1987 amendments to NWPA barred DOE from
continuing site investigations elsewhere within the U.S. However,
Congress' decision to focus solely on YM was not based on any finding
that information DOE had obtained on other sites ruled them out for
technical reasons; rather, the decision was aimed at controlling the
costs of the HLW program (55 FR 38486; September 18, 1990). Repository
programs in other countries are actively considering crystalline rock,
clay formations, and salt formations as repository host media. IAEA,
``Radioactive Waste Management Status and Trends, IAEA/WMDB/ST/4,''
2005; IAEA, ``The Use of Scientific and Technical Results from
Underground Research Laboratory Investigations for the Geologic
Disposal of Radioactive Waste, IAEA-TECDOC-1243,'' 2001. Many of these
programs have been conducting research on these geologic media for
several decades. Although there are relative strengths to the
capabilities of each of these potential host media, no geologic media
previously identified as a candidate host has been ruled out based on
technical or scientific information. Salt formations currently are
being considered as hosts only for reprocessed nuclear materials
because heat-generating waste, like spent nuclear fuel, exacerbates a
process by which salt can rapidly deform. This process could
potentially cause problems for keeping drifts stable and open during
the operating period of a repository.
In 2001, NRC amended its regulations to include a new 10 CFR Part
63, ``Disposal of High-Level Radioactive Wastes in a Geologic
Repository at Yucca Mountain, Nevada,'' (66 FR 55732; November 2,
2001), which requires use of both natural and engineered barriers to
meet overall total system performance objectives without pre-determined
subsystem performance requirements, such as substantially complete
containment for a waste package, as is required in 10 CFR Part 60.\3\
Accordingly, U.S. research and development activities have focused on
understanding the long-term capability of natural and engineered
barriers which can prevent or substantially reduce the release rate of
radionuclides from a potential repository system. Although the
performance of individual barriers may change through time, the overall
performance of the total system is required to be acceptable throughout
the performance period for the repository. In this context of total
system performance, research and development has supported the view
that it appears technically possible to design and construct a waste
package and an engineered barrier system that, in conjunction with
natural barriers, could prevent or substantially reduce the release
rate of radionuclides from a potential repository system during the
performance period. NRC, ``Disposal of High-Level Radioactive Wastes in
a Proposed Geologic Repository at Yucca Mountain, Nevada; Proposed
Rule,'' (64 FR 8649; February 22, 1999); IAEA, ``Joint Convention on
Safety of Spent Fuel Management and on Safety of Radioactive Waste
Management, INFCIRC/546,'' 1997.
---------------------------------------------------------------------------
\3\ NRC's regulations at 10 CFR Part 63 apply only to the
proposed repository at YM. NRC's regulations at 10 CFR Part 60,
``Disposal of High-Level Radioactive Wastes in Geologic
Repositories,'' govern the licensing of any repository other than
one located at YM. However, at the time Part 63 was proposed, the
Commission indicated it would consider revising Part 60 if it seemed
likely to be used in the future. 64 FR 8640, 8643; February 22,
1999.
---------------------------------------------------------------------------
Since the Commission last considered Waste Confidence issues, NRC
has issued design certifications under its regulations at 10 CFR Part
52, ``Early Site Permits; Standard Design Certifications; and Combined
Licenses for Nuclear Power Plants,'' and is currently reviewing several
plant designs in response to applications for design certifications and
for COL applications that reference designs under review or designs
previously certified. These facilities would use the same or similar
fuel assembly designs as the nuclear power plants currently operating
in the United States. A need for possible design changes for repository
disposal may be affected by the extent of a licensee's reliance on
cladding or fuel type as a barrier to waste isolation. If limited
reliance is placed on the barrier capabilities of cladding or fuel type
in a demonstration of compliance with repository safety requirements,
then minimal design changes may be needed to accommodate new types of
SNF or cladding. As such, the new reactor designs and specific license
applications currently under review would not raise issues as to the
technical feasibility of repository disposal.
NRC is also engaged in preliminary interactions with DOE and
possible reactor vendors proposing advanced reactor designs that are
different from the currently operating light-water reactors. Some of
these advanced reactors use gas-cooled or liquid metal cooled
technologies and have fuel and reactor components that might require
different transportation and storage containers. Geometric, thermal,
and criticality constraints could conceivably require a design
modification to disposal containers from that currently proposed for
YM. Nevertheless, the technical requirements for disposal of advanced
reactor components appear similar to the requirements for disposal of
components for current light water reactors. For example, DOE currently
plans to dispose of spent fuel at YM from both gas-cooled (Peach Bottom
1) and liquid-metal cooled (Fermi 1) reactors, using the same basic
technological approach as for other SNF. Although radionuclide
inventory, fuel matrix, and cladding characteristics for advanced fuels
might be distinct from current light-water reactors, the safe disposal
of advanced fuel appears to involve the same scientific and engineering
knowledge as used for fuel from current light-water reactors.
There is currently a high uncertainty regarding the growth of
advanced reactors in the U.S. The licensing strategy developed by NRC
and DOE for the next generation nuclear plant (NGNP) program found that
an aggressive licensing approach may lead to operation of a prototype
facility in 2021. Based on comparison with current disposal strategies
for fuel from existing gas cooled or liquid-metal cooled reactors, NRC
is confident that current technology appears to be adequate to support
the safe disposal of spent fuel from a potential prototype facility. In
addition to the NGNP activities related to the prototype reactor,
various activities, such as DOE's Advanced Fuel Cycle Initiative, are
underway to evaluate fuel cycle alternatives that could affect the
volume and form of waste from the prototype reactor or other advanced
nuclear reactor designs. The need to consider waste disposal as part of
the overall research and development activities for advanced reactors
is recognized and included in the activities of designers, DOE and NRC.
See, e.g., DOE Nuclear Energy Research Advisory Committee and the
Generation IV International Forum, ``A Technology Roadmap for
Generation IV
[[Page 59556]]
Nuclear Energy Systems,'' December 2002.
Based on the information described previously, the Commission
proposes to reaffirm Finding 1.
II. Finding 2 (1990): The Commission Finds Reasonable Assurance That at
Least One Mined Geologic Repository Will Be Available Within the First
Quarter of the Twenty-First Century, and That Sufficient Repository
Capacity Will Be Available Within 30 Years Beyond the Licensed Life for
Operation (Which May Include the Term of a Revised or Renewed License)
of Any Reactor To Dispose of the Commercial High-Level Radioactive
Waste and Spent Fuel Originating in Such Reactor and Generated Up to
That Time
A. Bases for Finding 2
The dual objectives of this finding are to predict when a
repository will be available for use and to predict how long spent fuel
may need to be stored at a reactor site until repository space is
available for the spent fuel generated at that reactor. With respect to
the first prediction, the Commission's focus in 1984 was on the years
2007-2009, the years during which the operating licenses for the
Vermont Yankee and Prairie Island nuclear power plants would expire.\4\
In 1984, DOE anticipated that the first repository would begin
operation in 1998 and the second in 2004. However, NRC concluded that
technical and institutional uncertainties made it preferable to focus
on the 2007-2009 time period. The technical uncertainties involved the
questions of how long it would take DOE to locate a suitable geologic
setting for a potentially technically acceptable repository and how
long it would take to develop an appropriate waste package and
engineered barriers. The Commission expressed the view that despite
early delays DOE's program was on track and, under the impetus given by
the recently-enacted NWPA, would timely resolve the technical problems
(49 FR 34674-34675; August 31, 1984).
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\4\ Under the court remand which precipitated the initial waste
confidence review, NRC was required to consider whether there was
reasonable assurance that an offsite storage solution would be
available by the years 2007-2009 and, if not, whether there was
reasonable assurance that the spent fuel could be stored safely at
those sites beyond those dates. See State of Minnesota v. NRC, 602
F.2d 412, 418 (DCDC Cir. 1979).
---------------------------------------------------------------------------
The Commission also identified institutional uncertainties that
needed to be resolved: (1) Measures for dealing with Federal-state
disputes; (2) An assured funding mechanism that would be sufficient
over time to cover the period for developing a repository; (3) An
organizational capability for managing the HLW program; and (4) A firm
schedule and establishment of responsibilities. The Commission
expressed its confidence in the ability of the provisions of the then
recently-passed NWPA to timely resolve these uncertainties (49 FR
34675-34679; August 31, 1984).
With respect to the second prediction, NRC reviewed DOE's estimates
of the amount of installed generating capacity of commercial nuclear
power plants in the year 2000 and concluded that the total amount of
spent fuel that would be produced during the operating lifetimes of
these reactors would likely be about 160,000 MTHM. To accommodate this
amount, NRC assumed that two repositories would be needed. NRC
calculated that if the first repository began to receive SNF in 2005,
and the second in 2008, then all the SNF would be emplaced by about
2026. This would mean that sufficient repository capacity would be
available within 30 years beyond the expiration of any reactor license
for disposal of its SNF (49 FR 34679; August 31, 1984).
In reviewing these predictions in 1990, the Commission faced a
considerably changed landscape. First, DOE's schedule for the
availability of a repository had slipped several times so that its
then-current projection was 2010. Second, Congress' 1987 amendment of
NWPA had confined site characterization to the YM site, meaning that
there were no ``back-up'' sites being characterized in case the YM site
should be found unsuitable or unlicenseable. Finally, site
characterization activities at YM had not proceeded without problems,
notably in DOE's schedule for sub-surface exploration and in
development of its quality assurance program. Given these
considerations, the Commission found it would not be prudent to
reaffirm its confidence in the availability of a repository in the
2007-2009 period (55 FR 38495; September 18, 1990).
Instead, the Commission found that it would be reasonable to assume
that DOE could make its finding whether YM was suitable for development
of a repository by the year 2000. The Commission was unwilling to
assume that DOE would make a finding of suitability (which would be
necessary for a repository to be available by 2010). To establish a new
time-frame for repository availability, the Commission made the
assumption that DOE would find the YM site unsuitable by the year 2000
and that (as DOE had estimated) it would take 25 years for a repository
to become available at a different site.
The Commission then considered whether it had sufficient bases for
confidence that a repository would be available by 2025 using the same
technical and institutional criteria it had used in 1984. The
Commission found no reason to believe that another potentially
technically acceptable site could not be located if the YM site were
found unsuitable. The development of a waste package and engineered
barriers was tied up with the question of the suitability of the YM
site but NRC found no reason to believe that a waste package and
engineered barriers could not be developed for a different site by
2025, if necessary (55 FR 38495; September 18, 1990). The institutional
uncertainties were perhaps more difficult to calculate. The Commission
acknowledged that DOE's efforts to address the concerns of States,
local governments and Indian tribes had met with mixed results.
Nevertheless, the Commission retained its confidence that NWPA, as
amended, had achieved the proper balance between providing for
participation by affected parties and providing for the exercise of
Congressional authority to carry out the national program for waste
disposal (55 FR 38497; September 18, 1990). Similarly, the Commission
believed that management and funding issues had been adequately
resolved by NWPA, as amended, and would not call into question the
availability of a repository by 2025 (55 FR 38497-38498; September 18,
1990). Thus, except for the schedule, the Commission was confident that
the HLW program set forth in the amended NWPA would ultimately be
successful.
The Commission also considered whether the termination of
activities for a second repository, combined with the 70,000 MTHM limit
for the first repository, together with its new projection of 2025 as
the time for the availability for a repository, undermined its
prediction that sufficient repository capacity would be available
within 30 years beyond expiration of any reactor operating license to
dispose of the SNF originating in such reactor and generated up to that
time (55 FR 38501-38504; September 18, 1990). The Commission noted that
almost all reactor licenses would not expire until some time in the
first three decades of the twenty-first century and license renewal was
expected to extend the terms of some of these licenses. Thus, a
repository was not needed by 2007-2009 to provide disposal capacity
within 30 years beyond expiration of
[[Page 59557]]
most operating licenses.\5\ The Commission acknowledged, however, that
it appeared likely that two repositories would be needed to dispose of
all the SNF and HLW from the current generation of reactors unless
Congress provided statutory relief from the 70,000 MTHM limit for the
first repository and unless the first repository had adequate capacity
to hold all the SNF and HLW generated. This was because DOE's spent
fuel projections, in 1990, called for 87,000 MTHM to have been
generated by the year 2036. In addition, DOE's projections were based
on the assumption of no new reactor orders. The Commission believed
that that assumption probably underestimated the total spent fuel
discharges to be expected due to the likelihood of reactor license
renewals. The Commission expressed the belief that if the need for a
second repository was established, Congress would provide the needed
institutional support and funding, as it had for the first
repository.\6\ The Commission reasoned that if work began on the second
repository program in 2010, that repository could be available by 2035.
Two repositories available in approximately 2025 and 2035, each with
acceptance rates of 3400 MTHM/year within several years after
commencement of operations, would provide assurance that sufficient
repository capacity will be available within 30 years of operating
license expiration for reactors to dispose of the spent fuel generated
at their sites up to that time. The Commission concluded that a second
repository, or additional capacity at the first repository, would be
needed only to accommodate the additional quantity of spent fuel
generated during the later years of reactors operating under a renewed
license. The Commission stated that the availability of a second
repository would permit spent fuel to be shipped offsite well within 30
years after expiration of these reactors' operating licenses and that
the same would be true of the spent fuel discharged from any new
generation of reactor designs (55 FR 38503-38504; September 18, 1990).
---------------------------------------------------------------------------
\5\ NRC identified Dresden 1, licensed in 1959, as the earliest
licensed power reactor and noted that 30 years beyond its licensed
life for operation would be 2029 and that it was possible, if a
repository were to become available by 2025, for all the Dresden 1
SNF to be removed from that facility by 2029 (55 FR 38502; September
18, 1991).
\6\ DOE is statutorily required to report to the President and
to Congress on the need for a second repository between January 1,
2007 and January 1, 2010. Section 161 of NWPA, as amended, 42 U.S.C.
10172a. DOE intends to submit the report in 2008.
---------------------------------------------------------------------------
The Commission acknowledged that there were several licenses that
had been prematurely terminated where it was possible that SNF would be
stored more than 30 years beyond the effective expiration of the
license and that there could be more of these premature terminations.
However, the Commission remained confident that in these cases, the
overall safety and environmental impacts of extended spent fuel storage
would be insignificant. The Commission had found that spent fuel could
be safely stored for at least 100 years (Finding 4), \7\ and that spent
fuel in at-reactor storage would be safely maintained until disposal
capacity at a repository was available (Finding 3). The Commission
emphasized that it had not identified a date by which a repository must
be available for health and safety reasons. The Commission found that
in effect, under the second part of Finding 2, safe management and safe
storage would not need to continue for more than 30 years beyond
expiration of any reactor's operating license because sufficient
repository capacity was expected to become available within those 30
years (55 FR 38504; September 18, 1990).
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\7\ The Commission conservatively assumed that licenses would be
renewed for 30 year terms (55 FR 38503; September 18, 1990). Thus,
the initial 40 year term of the operating license, plus 30 years for
the renewed operating license term and 30 years beyond the
expiration of the renewed license amounts to storage for at least
100 years.
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B. Evaluation of Finding 2
As explained previously, the Commission based its estimate in 1990
on the premise that at least one geologic repository would be available
within the first quarter of the twenty-first century on an assumption
that DOE would make its suitability determination under section 114 of
NWPA around the year 2000. To avoid being put in the position of
assuming the suitability of the YM site, the Commission then assumed
that DOE would find that site unsuitable and, as DOE had estimated,
that it would take 25 years before a repository could become available
at an alternate site.
DOE made its suitability determination in early 2002 and found the
YM site suitable for development as a repository.\8\ Although DOE's
application for a construction authorization for a repository was
considerably delayed from the schedule set out in NWPA, \9\ on June 3,
2008, DOE submitted the application to NRC and on September 08, 2008,
NRC Staff notified DOE that it found the application acceptable for
docketing (73 FR 53284; September 15, 2008). DOE's current estimate of
the best achievable date for opening of the YM repository, assuming it
is licensed, is 2020. At the hearing before the Subcommittee on Energy
and Air Quality of the House Committee on Energy and Commerce held on
July 15, 2008, Edward F. Sproat III, Director of DOE's Office of
Civilian Radioactive Waste Management (OCRWM), informed the Congress
that DOE could be ready to begin accepting SNF by 2020, but only if
adequate funding is provided.
---------------------------------------------------------------------------
\8\ On February 14, 2002, the Secretary of Energy recommended
the YM site for the development of a repository to the President
thereby setting in motion the approval process set forth in sections
114 and 115 of the NWPA. See 42 U.S.C. 10134(a)(1); 10134(a)(2);
10135(b), 10136(b)(2). On February 15, 2002, the President
recommended the site to Congress. On April 8, 2002, the State of
Nevada submitted a notice of disapproval of the site recommendation
to which Congress responded, on July 9, 2002, by passing a joint
resolution approving the development of a repository at YM which the
President signed on July 23, 2002. See Pub. L. No. 107-200, 116
Stat. 735 (2002) (codified at 42 U.S.C. 10135 note (Supp. IV 2004)).
\9\ Section 114(b) of NWPA directs the Secretary of Energy to
submit a construction authorization application to NRC within 90
days of the date the site designation becomes effective. 42 U.S.C.
10134(b).
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The NWPA process thus remains on track for making available a
geologic repository for the disposal of SNF and HLW. DOE's projection
of a date for repository availability has moved from 2010 in 1990 to
2020 today and could slip further. Even with some slippage in DOE's
schedule, it remains possible that a repository will be available by
2025. Of course, now the only repository that could become available by
2025 is the proposed repository at YM and it will only become available
if the Commission issues a construction authorization and a subsequent
authorization to receive and possess HLW. In 2005, the State of Nevada
filed a petition for rulemaking with NRC (PRM-51-8) which raised the
question whether continued use of the 2025 date, in effect, indicated
prejudgment of the outcome of any licensing proceeding that might be
held. The Commission rejected this notion in its denial of the
petition:
Even if DOE's estimate as to when it will tender a license
application should slip further, the 2025 date would still allow for
unforeseen delays in characterization and licensing. It also must be
recognized that the Commission remains committed to a fair and
comprehensive adjudication and, as a result, there is the potential
for the Commission to deny a license for the Yucca Mountain site
based on the record established in the adjudicatory proceeding. That
commitment is not jeopardized by the 2025 date for repository
availability. The Commission did not see any threat to its ability
to be an
[[Page 59558]]
impartial adjudicator in 1990 when it selected the 2025 date even
though then, as now, a repository could only become available if the
Commission's decision is favorable. Should the Commission's decision
be unfavorable and should DOE abandon the site, the Commission would
need to reevaluate the 2025 availability date, as well as other
findings made in 1990. State of Nevada; Denial of a Petition for
Rulemaking (70 FR 48329, 48333; August 17, 2005).
In the absence of an unfavorable NRC decision and DOE's abandonment
of the site, the Commission found no reason to reopen its Waste
Confidence findings.
However, the Commission has now considered the recommendations of
the Combined License Review Task Force Report and, in its June 22,
2007, Staff Requirements Memorandum (SRM) on that report, has approved
rulemaking to resolve generic issues associated with combined license
applications. SRM--COMDEK-07-0001/COMJSM-07-0001--Report of the
Combined License Review Task Force (ML071760109). In a subsequent SRM
of September 7, 2007, the Commission expressed the view that a near-
term update to the Waste Confidence findings was appropriate. SRM--
Periodic Briefing on New Reactor Issues (ML072530192). The staff, in
its response to these SRMs, recognized that there would likely be long-
term inefficiencies in combined license application proceedings, due to
the need to respond to potential questions and petitions directed to
the existing Waste Confidence Decision, and committed to evaluate
possible updates to the decision.\10\ See memorandum from Luis A. Reyes
to the Commissioners, ``Rulemakings that Will Provide the Greatest
Efficiencies to Complete the Combined License Application Reviews in a
Timely Manner,'' December 17, 2007, at 3 (ML073390094). Undertaking a
public rulemaking proceeding now to consider revisions to the Waste
Confidence findings and rule--rather than waiting until some point
closer to the 2025 date--will allow sufficient time to conduct a
studied and orderly reassessment and, as appropriate, to revise and
update the findings and rule. In particular, it will allow the
Commission to consider alternative time-frames which would provide
reasonable assurance for the availability of a repository.
---------------------------------------------------------------------------
\10\ Challenges to 10 CFR 51.23 in individual COL proceedings
would likely be addressed through application of 10 CFR 2.335,
``Consideration of Commission rules and regulations in adjudicatory
proceedings.'' This rule generally prohibits attacks on NRC rules
during adjudicatory proceedings but does allow a party to an
adjudicatory proceeding to petition that application of a specified
rule be waived or an exception made for the particular proceeding.
10 CFR 2.335(b). The sole ground for such a waiver or exception is
that ``special circumstances with respect to the subject matter of
the particular proceeding are such that the application of the rule
or regulation * * * would not serve the purposes for which the rule
or regulation was adopted.'' Id. Thus, a review of the Waste
Confidence findings and rule now might be expected to obviate such
challenges in individual COL proceedings.
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One possibility might be to make an assumption that the Commission
would ultimately find the YM site unacceptable by a certain date and
then set the expected availability of a different repository at a time
around 25 years later in accordance with DOE's 1990 estimate of the
time it would take to make a repository available at a different site.
However, the Commission rejected this route in the denial of the Nevada
petition:
[T]he use of a Commission acceptability finding as the basis for
repository availability is impossible to implement because it would
require the Commission to prejudge the acceptability of any
alternative to Yucca Mountain in order to establish a reasonably
supported outer date for the Waste Confidence finding. That is, if
the Commission were to assume that a license for the Yucca Mountain
site might be denied in 2015 and establish a date 25 years hence for
the `availability' of an alternative repository (i.e., 2040), it
would still need to presume the `acceptability' of the alternate
site to meet that date (70 FR 48333; August 17, 2005).
Another approach would be to revise the finding to include a target
date or timeframe for which it now seems reasonable to assume that a
repository would be available. A target date for when a disposal
facility can reasonably be expected to be available would result from
an examination of the technical and institutional issues that would
need to be resolved before a repository could be available. The target
date approach would be consistent with the HLW disposal programs in
other countries, as explained further in this document. The target date
could be placed in the finding itself, or described in the explanation
for the finding. A target date is admittedly not very different from
``the first quarter of the twenty-first century'' as stated in the
current finding, but this approach would make it more clear that
specification of a particular time for when a repository could be built
does not imply that radioactive waste would pose unsafe conditions if a
repository were not available at that time. The capability to safely
store radioactive waste over long periods is a viable interim
alternative not dependent on any one specific year for availability of
a repository. The Commission has adopted this approach in updating its
finding.
Most countries possessing HLW and SNF eventually plan to confine
these wastes using deep geologic disposal. Currently, there are 24
other countries that consider disposal of spent or reprocessed nuclear
fuel in deep geologic repositories. From the vantage point of near-term
safety, there has been little urgency in these countries for
implementing disposal facilities because of the perceived high degree
of safety provided by interim storage, either at reactors or at
independent storage facilities. Of these 24 countries,10 have
established target dates for the availability of a repository. Most of
the 14 countries which have not established target dates rely on
centralized interim storage, which may include a protracted period of
onsite storage before shipment to a centralized facility.\11\
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\11\ The three countries with target dates that plan direct
disposal of SNF are: Czech Republic (2050), Finland (2020), and
Sweden (2020). The seven countries with target dates that plan
disposal of reprocessed SNF/HLW are: Belgium (2035), China (2050),
France (2025), Germany (2025), Japan (2030s), Netherlands (2013),
Switzerland (2042).
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The ``target date'' approach would need to assume a beginning date
for a new repository program. NRC believes that it is reasonable to
select 2025 as the starting point, the current outer date of the
Commission's prediction of repository availability. It is reasonable to
assume that it will be known by 2025 whether a repository is available
at the YM site. If it is not available, it seems reasonable to assume
that a new repository program would get underway around that time. The
need for a new repository program would not necessarily be the result
of an NRC denial of the license application; it could result from a
change in national policy for HLW disposal, a court reversal of a
Commission licensing action, or other factors. The assumption of a need
for a new repository program would be based on an assumption that the
proposed YM repository does not become available, and not on an
assumption that NRC determines that facility to be technically
unacceptable. In sum, the Commission would be saying that it will
remove its expectation that a repository will be available by 2025 but,
even in the event that the YM repository does not become available, it
retains confidence that spent fuel can be safely stored with no
significant environmental impact until a repository can reasonably be
expected to be available and that the Commission has a target date for
the availability of the repository in that circumstance.
If it is assumed that a new repository program begins around the
year 2025, then setting a target date for the
[[Page 59559]]
availability of a repository becomes a matter of examining the
technical and institutional problems DOE would need to resolve to
achieve the target date. The technical problems should be the same as
the ones NRC examined in the earlier Waste Confidence reviews, namely,
how long it would take DOE to locate a suitable site and how long it
would take to develop a waste package and engineered barriers for that
site. For the reasons explained in our evaluation of Finding 1, the
Commission continues to have reasonable assurance that disposal in a
geologic repository is technically feasible. That is the approach being
taken in all the countries identified previously which have set target
dates for the availability of a repository. It is also the approach of
14 other countries which have HLW disposal programs, but which have not
set target dates.\12\ In addition when Congress amended NWPA in 1987 to
focus exclusively on the YM site, it did so for budgetary reasons and
not because the sites DOE was considering at the time were discovered
to be technically unacceptable. The research being done nationally and
internationally strongly suggests that potentially acceptable sites
exist and can be identified.
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\12\ These countries are: Brazil, Canada, Hungary, Lithuania,
Romania, South Korea, Slovak Republic, Spain (direct disposal of
SNF); Bulgaria, India, Italy, Russia, United Kingdom, Ukraine
(disposal of reprocessed SNF/HLW).
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The amount of time DOE might need to develop an alternative
repository site would depend upon the context of any enabling
legislation, budgetary constraints, and the degree of similarity
between a candidate site and other well-characterized sites with
similar HLW disposal concepts. DOE began characterization of the YM
site in 1982, made its suitability determination in 2002, and submitted
a license application in 2008. However, the history of potential
repository development at YM may be a poor indicator of the amount of
time needed to develop a new repository. Many problems extraneous to
site characterization activities adversely impacted DOE's repository
program, such as changes in enabling legislation, public confidence
issues, funding in Congressional appropriations, and significant delay
in issuing environmental standards. In terms of the technical work
alone, a lot would depend on whether Congress established a program
involving characterization of many sites preliminary to the
recommendation of a single site (similar to the 1982 NWPA) or a program
focused on a single site (similar to the amended NWPA). The former
would likely take longer but might have a better chance of success if
problems developed with the single site. Much would also depend on
whether the site(s) chosen for characterization is similar to sites in
this or other countries for which much information is available or
whether the site(s) would present novel challenges for which much
fundamental knowledge would have to be developed. An alternative site
with a disposal approach that is similar to that used in other
international repository programs could make use of the extensive
knowledge from those international programs to gain efficiencies in the
alternative repository development program.
In addition, there should be a certain amount of ``lessons
learned'' from the YM repository program that could help to shorten the
length of a new program. For example, performance assessment techniques
have improved significantly over the past 20 years (e.g., the Goldsim
software package of DOE's Total System Performance Assessment was not
available 20 years ago and represents a significant improvement over
the FORTRAN language of years past) such that performance assessment
models are easier to develop and more reliable from what was available
20 years ago. Similarly, operational and manufacturing aspects
developed during the YM program (e.g., manufacturing of waste packages,
excavation of drifts, waste handling), would be applicable to another
program. Also, regulatory issues considered during the YM program
(e.g., burn-up credit for nuclear fuel and seismic performance
analysis) should provide information useful for setting new standards
or revising current standards.\13\
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\13\ Both NRC's Part 63 and EPA's Part 197 are applicable only
for a repository at YM. NRC and EPA have in place standards for a
repository at a different site, but these standards would likely be
revised in a new repository program.
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Whether waste package and engineered barrier information developed
during the YM repository program would be transferable to a new program
depends heavily on the degree of similarity between an alternative site
and YM. The fundamental physical characteristics of the potential YM
repository are significantly different from other potential repository
sites that were considered in the U.S. repository program before 1987.
If YM does not become available, DOE could select an alternative
candidate site that was similar to YM in important physical
characteristics (such as oxidizing conditions, drifts above the water
table with low amounts of water infiltration, water chemistry buffered
by volcanic tuff rocks). In this instance, much of the existing
knowledge for engineered barrier performance at YM might be
transferable to a different site. Nevertheless, much of DOE's current
research on engineered barriers for YM could be inapplicable if an
alternative site had significantly different characteristics than the
YM site, such as an emplacement horizon in reducing conditions below
the water table. In this instance, research from additional programs by
DOE, industry, and other countries might provide important information
on engineered barriers, provided DOE's alternative was analogous to
sites and engineered ba