Branch Technical Position on Concentration Averaging and Encapsulation, 34411-34414 [2012-14084]
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[NRC–2011–0022]
Branch Technical Position on
Concentration Averaging and
Encapsulation
34411
You may access information
and comment submissions related to
this document, which the NRC
possesses and are publicly available, by
searching on https://www.regulations.gov
under Docket ID NRC–2011–0022. You
may submit comments by any of the
following methods:
• Federal Rulemaking Web site: Go to
https://www.regulations.gov and search
for Docket ID NRC–2011–0022. Address
questions about NRC dockets to Carol
Gallagher; telephone: (301) 492–3668;
email: Carol.Gallagher@nrc.gov.
• Mail comments to: Cindy Bladey,
Chief, Rules, Announcements, and
Directives Branch (RADB), Office of
Administration, Mail Stop: TWB–05–
B01M, U.S. Nuclear Regulatory
Commission, Washington, DC 20555–
0001.
• Fax comments to: RADB at 301–
492–3446.
For additional direction on accessing
information and submitting comments,
see ‘‘Accessing Information and
Submitting Comments’’ in the
SUPPLEMENTARY INFORMATION section of
this document.
FOR FURTHER INFORMATION CONTACT:
James Kennedy, Office of Federal and
State Materials and Environmental
Management Programs, U.S. Nuclear
Regulatory Commission, Washington,
DC 20555–0001; telephone: 301–415–
6668; email: James.Kennedy@nrc.gov.
SUPPLEMENTARY INFORMATION:
ADDRESSES:
Nuclear Regulatory
Commission.
ACTION: Draft Branch Technical Position;
request for comment.
I. Accessing Information and
Submitting Comments
The U.S. Nuclear Regulatory
Commission (NRC or the Commission)
is soliciting public comments on a
revised draft Revision 1 of its Branch
Technical Position on Concentration
Averaging and Encapsulation (CA BTP).
An earlier draft was completed in
August 2011 and made available to the
public in September 2011 (ADAMS
Accession No. ML112061191). The NRC
staff held a workshop in Albuquerque,
New Mexico, on October 20, 2011, to
receive public comments. This revised
draft addresses the stakeholder
comments received at the workshop,
and others received after the workshop.
After receiving and addressing public
comments on this revised draft, the staff
will finalize the CA BTP to replace the
1995 version now in effect.
DATES: Submit comments by October 8,
2012. Comments received after this date
will be considered if it is practical to do
so, but the NRC is able to assure
consideration only for comments
received on or before this date.
Please refer to Docket ID NRC–2011–
0022 when contacting the NRC about
the availability of information regarding
this document. You may access
information related to this document,
which the NRC possesses and are
publicly available, by any of the
following methods:
• Federal Rulemaking Web Site: Go to
https://www.regulations.gov and search
for Docket ID NRC–2011–0022.
• NRC’s Agencywide Documents
Access and Management System
(ADAMS): You may access publiclyavailable documents online in the NRC
Library at https://www.nrc.gov/readingrm/adams.html. To begin the search,
select ‘‘ADAMS Public Documents’’ and
then select ‘‘Begin Web-based ADAMS
Search.’’ For problems with ADAMS,
please contact the NRC’s Public
Document Room (PDR) reference staff at
1–800–397–4209, 301–415–4737, or by
email to pdr.resource@nrc.gov. The
ADAMS accession number for each
document referenced in this document
AGENCY:
SUMMARY:
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A. Accessing Information
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is provided the first time that a
document is referenced.
• NRC’s PDR: You may examine and
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B. Submitting Comments
Please include Docket ID NRC–2011–
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comment submission, in order to ensure
that the NRC is able to make your
comment submission available to the
public in this docket.
The NRC cautions you not to include
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you do not want to be publicly
disclosed in your comment submission.
The NRC will post all comment
submissions at https://
www.regulations.gov, as well as enter
the comment submissions into ADAMS,
and the NRC does not routinely edit
comment submissions to remove
identifying or contact information.
If you are requesting or aggregating
comments from other persons for
submission to the NRC, then you should
inform those persons not to include
identifying or contact information that
they do not want to be publicly
disclosed in their comment submission.
Your request should state that the NRC
does not routinely edit comment
submissions to remove such information
before making the comment
submissions available to the public or
entering the comment submissions into
ADAMS.
II. Background
Revising the CA BTP was ranked as a
high priority in the NRC staff’s
Commission paper, SECY–07–0180,
‘‘Strategic Assessment of Low-Level
Radioactive Waste Regulatory Program,’’
ADAMS Accession No. ML071350291.
The existing version of the CA BTP,
published in 1995, (ADAMS Accession
No. ML033630732) is not fully riskinformed and performance-based, and
does not always describe the bases for
its concentration averaging positions. It
also needs to be revised to incorporate
new provisions related to blending of
low-level waste (LLW), as directed by
the Commission in its Staff
Requirements Memorandum for SECY–
10–0043, ‘‘Blending of Low-Level
Radioactive Waste,’’ (ADAMS Accession
No. ML102861764).
The NRC’s regulations at Title 10 of
the Code of Federal Regulations (10
CFR) Part 61, ‘‘Licensing Requirements
for Land Disposal of Radioactive
Waste,’’ establishes a waste
classification system based on the
concentration of specific radionuclides
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contained in the waste. The regulations
in 10 CFR 61.55(a)(8) state that ‘‘[t]he
concentration of a radionuclide [in
waste] may be averaged over the volume
of the waste, or weight of the waste if
the units [on the values tabulated in the
concentration tables] are expressed as
nanocuries per gram.’’ The purpose of
the waste classification system is to
contribute to protection of individuals
that inadvertently intrude into a waste
disposal facility, a requirement in the
NRC’s disposal regulations at 10 CFR
61.42. Waste is classified according to
the hazard it presents to an inadvertent
intruder, and risk to the intruder is
managed by having increased disposal
facility control measures, such as depth
of disposal, as the hazard increases. The
concentration averaging provisions of
the 1995 CA BTP were specifically
developed to ensure that individual
items (e.g., disused sealed sources or
other radiological ‘‘hot spots’’) with
significantly greater radioactivity than
the average activity in a package are
safely disposed. Constraints on
radiological hot spots are needed to
ensure intruder protection, and the CA
BTP identifies these constraints.
The NRC staff initially developed a
technical position on radioactive waste
classification in May 1983 (ADAMS
Accession No. ML033630755). That
technical position paper described
overall procedures acceptable to NRC
staff which could be used by licensees
to determine the presence and
concentrations of the radionuclides
listed in 10 CFR 61.55, and thereby
classify waste for near-surface disposal.
In 1995, the NRC staff published the CA
BTP, expanding on Section C.3,
‘‘Concentration Volumes and Masses,’’
(i.e., concentration averaging) of the
1983 Technical Position. The 1995 CA
BTP recommended constraints on
averaging of homogeneous waste types 1
(e.g., ion exchange resins, soil, ash),
mixtures of discrete items (such as
irradiated reactor hardware) and sealed
sources for the purposes of ensuring
intruder protection against hot spots, as
well as constraining the amount of
averaging that licensees could perform
that would lower the classification of
wastes.
There have been a number of changes
in the LLW program since the 1995 CA
BTP was published; these changes were
drivers for the current revision. First,
the Commission reviewed the CA BTP’s
position on blending of LLW. The 1995
version constrained the concentration of
1 Waste in which the concentrations of
radionuclides of concern are likely to approach
uniformity in the context of reasonably foreseeable
intruder scenarios.
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input waste streams to mixtures of
mixable wastes (i.e., waste that is not
composed of discrete items) to within a
factor of 10 of the average concentration
of the final mixture. Also, the 1995
version does not constrain mixing of
these wastes if operational efficiency or
worker exposures were affected by the
blending. The Commission directed the
staff to implement a risk-informed,
performance-based approach for LLW
blending that made the hazard (i.e., the
radioactivity concentration) of the final
mixture, the primary consideration for
averaging constraints. Second, the NRC
adopted a risk-informed, performancebased regulatory approach for its
programs in the late 1990’s, after the
1995 CA BTP was published. This new
revision of the CA BTP more fully
reflects that regulatory approach, not
just for the blending positions, but for
all of the other topics it addresses as
well. Finally, the 1995 CA BTP
significantly constrained disposal of
encapsulated sealed sources below the
Class B and C limits in the 10 CFR 61.55
waste classification tables. The threat of
a radiological dispersal device using
sealed radioactive sources caused the
staff to re-examine the 1995
assumptions underlying the
radioactivity constraints on sealed
source disposal, and to better balance
the risk associated with inadvertent
intrusion with national security and
safety issues associated with sealed
sources that have no disposal pathway.
Licensees must store sealed sources for
potentially long periods of time if there
is no disposal option, and the sources
are subject to loss or abandonment. The
CA BTP’s revised positions will allow
for disposal of more sealed sources than
the 1995 CA BTP which will enhance
national security by ensuring that the
safest and most secure method to
manage them is available to licensees.
III. Stakeholder Comments on the
August 2011 Draft CA BTP
The draft Revision 1 of the CA BTP
that is being made available for public
comment is a revision to an August
2011 draft that was provided to the
NRC’s Advisory Committee on Reactor
Safeguards (ACRS) for review and
comment. The NRC staff briefed the
ACRS on October 4 and December 1,
2011, and the ACRS provided their
views to the Commission in a December
13, 2011, letter (ADAMS Accession No.
ML11354A407). The NRC staff also held
a public meeting to solicit comments on
the August 2011 draft in Albuquerque,
New Mexico, on October 20, 2011. The
meeting summary is in ADAMS
Accession No. ML113330167. At that
meeting, stakeholders requested that
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NRC staff revise the existing version to
address their comments before
publishing it for public comment again.
The staff agreed to that request.
In addition, the staff met with the
Low-Level Radioactive Waste Forum’s
(LLW Forum) Disused Source Working
Group on February 9, 2012, in Dallas,
Texas, to explain the bases for the
revised CA BTP and to answer
questions. The Agreement States that
regulate the four active LLW disposal
sites (Texas, South Carolina, Utah, and
Washington) and that are members of
the Disused Source Working Group
provided formal comments on the
August 2011 draft.2 The LLW Forum
also provided written comments
(ADAMS Accession No. ML120530573).
All of these comments, from the
ACRS; stakeholders at the October 20,
2011, workshop; and the members of the
Disused Source Working Group—have
been considered in the revised draft that
is being made available in this
document. Appendices D, E, and H of
draft Revision 1 contain the staff’s
analysis and responses to comments
from stakeholders at the October 20,
2011, workshop; from members of the
LLW Forum’s Disused Source Working
Group; and from the ACRS,
respectively. Several other stakeholders
also provided additional comments in
February and April 2012 (ADAMS
Accession Nos. ML120520558,
ML120890046, and ML121220126), and
these were considered to the extent
possible in developing this revised
draft. The staff did not document
responses to their comments because of
schedule constraints. For any of these
comments that the staff has not fully
responded to, the staff will address
them in preparing the final version of
the CA BTP. A redline-strikeout
comparison between the May 2012 draft
and the August 2011 draft is contained
in ADAMS Accession No.
ML12137A262.
The staff is interested in stakeholder
views on all responses to issues that
were raised in the above comments, but
is particularly interested in stakeholder
views on the following topics:
Selection of inadvertent intruder
exposure scenarios: In the original and
revised CA BTP, the staff postulated
generic exposure scenarios to evaluate
the doses to an inadvertent intruder
exposed to radiological hot spots in
2 Texas Commission on Environmental Quality,
ADAMS Accession No. ML120530077; South
Carolina Department of Health and Environmental
Control, ADAMS Accession No. ML120520496;
Utah Department of Environmental Conservation,
ADAMS Accession No. ML120520498; Washington
Office of Radiation Protection, ADAMS Accession
No. ML120520505)
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mixable wastes and in individual items
to establish concentration averaging
constraints. Because it is not possible to
predict human behavior with complete
accuracy over the time frames
associated with the hazard from LLW,
the staff has used what it believes to be
reasonable, yet conservative scenarios,
such as well drilling into waste. The
ACRS and others have commented on
the selection of scenarios. The staff is
interested in receiving public input on
the specific scenarios used for this
revised draft, as well as factors to be
considered in selection of generic
radiation exposure scenarios for an
inadvertent intruder. Information on the
selection of scenarios is provided in the
CA BTP in Appendix B; Appendix D
(responses to comments 1(c) and 6(a);
and the staff’s February 3, 2012,
response (ADAMS Accession No.
ML120090314) 3 to the ACRS letter
(ADAMS Accession No.
ML11354A407).4 An important impact
of scenario selection is the constraint on
the activity of sealed sources for
disposal under the CA BTP. The revised
CA BTP uses a new scenario that would
allow for disposal of higher activity
sources to be disposed of in commercial
LLW disposal sites that would result in
these sources no longer posing a threat
to national security. Some stakeholders,
including ACRS, have argued for the use
of scenarios that would result in fewer
constraints on sources, and higher
activities for disposal than what the staff
has proposed.
Other ACRS recommendations and
issues: The ACRS and staff were in
agreement on a number of positions in
the revised CA BTP, such as blending of
LLW, and the new Alternative
Approaches section. However, the
ACRS had a number of
recommendations that could potentially
significantly change the CA BTP,
including allowing for reliance on
perpetual care funds for institutional
controls to prevent or mitigate the
impacts of inadvertent intrusion and
using probability of intrusion in
developing averaging positions. The
staff is interested in stakeholder views
on the pros and cons of the ACRS
recommendations, given their
potentially significant impacts on
current practices. The ACRS letter to the
Commission (ADAMS Accession No.
ML11354A407) is contained in
Appendix G of the revised CA BTP.
Classification of cartridge filters as a
homogeneous waste: Cartridge filters are
3 The February 3, 2012, staff response is
contained in Appendix H of the CA BTP.
4 The December 13, 2011, ACRS letter is
contained in Appendix G of the CA BTP.
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34413
used to remove radioactive solids from
various systems in a nuclear power
plant. Filters are typically composed of
thin metal or plastic frames with a
corrugated or wound paper or synthetic
filter media enclosed within the frame.
Although the frames and filter media are
contained in fairly robust metal
housings, the housing is perforated so
that radioactivity from the filters could
be dislodged during handling by an
inadvertent intruder. In addition,
although filters may contain high levels
of non-gamma emitting radionuclides,
they typically contain low amounts of
long-lived gamma radionuclides that
would pose a hazard to an intruder
handling a discrete item. The current
CA BTP classifies cartridge filters as
discrete wastes, so that each filter must
be individually characterized for the
concentrations and amounts of
radionuclides that may affect waste
classification. Several stakeholders have
argued that the characteristics of
cartridge filters previously described are
significantly different from discrete
items such as sealed sources or
activated metal and justify their
treatment as homogeneous wastes.
Homogeneous wastes are subject to less
stringent averaging constraints. The
revised CA BTP continues to classify
filters as discrete wastes, but provides
an option for licensees to document
justifications for treatment of them as
homogeneous wastes. Section 4.3.4,
‘‘Cartridge Filters as Homogeneous
Waste,’’ and the staff’s response to
comment 3(a) in Appendix D describes
the revised position on cartridge filters
and its basis. The staff is specifically
seeking stakeholder views on this
revision to the previous draft.
Homogeneity Test for Mixable Wastes:
The staff received significant comments
on the proposed testing for homogeneity
of blended waste in the August 2011
draft Revision 1 of CA BTP. The staff
has addressed these comments and
made significant revisions. See Section
4.2.2 of the revised CA BTP,
‘‘Homogeneity of Mixable Waste,’’ as
well as Section 4.9, ‘‘Alternative
Approaches.’’ See also responses to
comments 1(c) and 1(g) in Appendix D.
Specification of Waste to Binder Ratio
and Not Container Size for
Encapsulation of LLW: The 1995 CA
BTP provided for encapsulation of
discrete, higher-activity items in a nonradioactive medium such as concrete,
and averaging the activity in the discrete
item over a 55 gallon drum volume. The
amount of non-radioactive material over
which averaging could take place was
constrained to 55 gallons, so that
extreme averaging measures would not
be employed. Several stakeholders
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requested that the waste-to-binder ratio
be specified so that larger volumes
could be employed. The constraints
would be based on the average activity
of the encapsulated package, and the
ratio of the volume of the radioactive
item to the volume of the encapsulating
media. Such an approach would still
constrain the use of non-radioactive
materials in averaging. This approach
had been approved by the NRC in a
topical report for encapsulating and
averaging cartridge filters. The staff has
addressed this comment in revisions to
Section 4.5, ‘‘Encapsulation of Sealed
Sources and Other Solid Low-Level
Radioactive Wastes,’’ and in response to
comment 7(a) in Appendix D.
Dated at Rockville, Maryland, this 30th day
of May, 2012.
For the Nuclear Regulatory Commission.
Andrew Persinko,
Acting Director, Division of Waste
Management and Environmental Protection,
Office of Federal and State Materials and
Environmental Management Programs.
[FR Doc. 2012–14084 Filed 6–8–12; 8:45 am]
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Agency: Retirement Operations,
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Title: Annuitant’s Report of Earned
Income.
OMB Number: 3206–0034.
Frequency: On occasion.
Affected Public: Individuals or
Households.
Number of Respondents: 21,000.
Estimated Time per Respondent: 35
minutes.
Total Burden Hours: 12,250.
John Berry,
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Management.
[FR Doc. 2012–14134 Filed 6–8–12; 8:45 am]
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Request
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Commission, Office of Investor
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Extension:
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Notice is hereby given that, pursuant
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The federal securities laws generally
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dealer from delivering a security for sale
unless a prospectus meeting certain
requirements accompanies or precedes
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under the Securities Act of 1933 (15
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Under rule 154, a prospectus is
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See Securities Act sections 2(a)(10), 4(1), 4(3), 5(b)
[15 U.S.C. 77b(a)(10), 77d(1), 77d(3), 77e(b); see
also rule 174 under the Securities Act (17 CFR
230.174) (regarding the prospectus delivery
obligation of dealers); rule 15c2–8 under the
Securities Exchange Act of 1934 (17 CFR 240.15c2–
8) (prospectus delivery obligations of brokers and
dealers).
2 Rule 154 permits the householding of
prospectuses that are delivered electronically to
investors only if delivery is made to a shared
electronic address and the investors give written
consent to householding. Implied consent is not
permitted in such a situation. See rule 154(b)(4).
E:\FR\FM\11JNN1.SGM
11JNN1
Agencies
[Federal Register Volume 77, Number 112 (Monday, June 11, 2012)]
[Notices]
[Pages 34411-34414]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2012-14084]
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NUCLEAR REGULATORY COMMISSION
[NRC-2011-0022]
Branch Technical Position on Concentration Averaging and
Encapsulation
AGENCY: Nuclear Regulatory Commission.
ACTION: Draft Branch Technical Position; request for comment.
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SUMMARY: The U.S. Nuclear Regulatory Commission (NRC or the Commission)
is soliciting public comments on a revised draft Revision 1 of its
Branch Technical Position on Concentration Averaging and Encapsulation
(CA BTP). An earlier draft was completed in August 2011 and made
available to the public in September 2011 (ADAMS Accession No.
ML112061191). The NRC staff held a workshop in Albuquerque, New Mexico,
on October 20, 2011, to receive public comments. This revised draft
addresses the stakeholder comments received at the workshop, and others
received after the workshop. After receiving and addressing public
comments on this revised draft, the staff will finalize the CA BTP to
replace the 1995 version now in effect.
DATES: Submit comments by October 8, 2012. Comments received after this
date will be considered if it is practical to do so, but the NRC is
able to assure consideration only for comments received on or before
this date.
ADDRESSES: You may access information and comment submissions related
to this document, which the NRC possesses and are publicly available,
by searching on https://www.regulations.gov under Docket ID NRC-2011-
0022. You may submit comments by any of the following methods:
Federal Rulemaking Web site: Go to https://www.regulations.gov and search for Docket ID NRC-2011-0022. Address
questions about NRC dockets to Carol Gallagher; telephone: (301) 492-
3668; email: Carol.Gallagher@nrc.gov.
Mail comments to: Cindy Bladey, Chief, Rules,
Announcements, and Directives Branch (RADB), Office of Administration,
Mail Stop: TWB-05-B01M, U.S. Nuclear Regulatory Commission, Washington,
DC 20555-0001.
Fax comments to: RADB at 301-492-3446.
For additional direction on accessing information and submitting
comments, see ``Accessing Information and Submitting Comments'' in the
SUPPLEMENTARY INFORMATION section of this document.
FOR FURTHER INFORMATION CONTACT: James Kennedy, Office of Federal and
State Materials and Environmental Management Programs, U.S. Nuclear
Regulatory Commission, Washington, DC 20555-0001; telephone: 301-415-
6668; email: James.Kennedy@nrc.gov.
SUPPLEMENTARY INFORMATION:
I. Accessing Information and Submitting Comments
A. Accessing Information
Please refer to Docket ID NRC-2011-0022 when contacting the NRC
about the availability of information regarding this document. You may
access information related to this document, which the NRC possesses
and are publicly available, by any of the following methods:
Federal Rulemaking Web Site: Go to https://www.regulations.gov and search for Docket ID NRC-2011-0022.
NRC's Agencywide Documents Access and Management System
(ADAMS): You may access publicly-available documents online in the NRC
Library at https://www.nrc.gov/reading-rm/adams.html. To begin the
search, select ``ADAMS Public Documents'' and then select ``Begin Web-
based ADAMS Search.'' For problems with ADAMS, please contact the NRC's
Public Document Room (PDR) reference staff at 1-800-397-4209, 301-415-
4737, or by email to pdr.resource@nrc.gov. The ADAMS accession number
for each document referenced in this document
[[Page 34412]]
is provided the first time that a document is referenced.
NRC's PDR: You may examine and purchase copies of public
documents at the NRC's PDR, Room O1-F21, One White Flint North, 11555
Rockville Pike, Rockville, Maryland 20852.
B. Submitting Comments
Please include Docket ID NRC-2011-0022 in the subject line of your
comment submission, in order to ensure that the NRC is able to make
your comment submission available to the public in this docket.
The NRC cautions you not to include identifying or contact
information that you do not want to be publicly disclosed in your
comment submission. The NRC will post all comment submissions at https://www.regulations.gov, as well as enter the comment submissions into
ADAMS, and the NRC does not routinely edit comment submissions to
remove identifying or contact information.
If you are requesting or aggregating comments from other persons
for submission to the NRC, then you should inform those persons not to
include identifying or contact information that they do not want to be
publicly disclosed in their comment submission. Your request should
state that the NRC does not routinely edit comment submissions to
remove such information before making the comment submissions available
to the public or entering the comment submissions into ADAMS.
II. Background
Revising the CA BTP was ranked as a high priority in the NRC
staff's Commission paper, SECY-07-0180, ``Strategic Assessment of Low-
Level Radioactive Waste Regulatory Program,'' ADAMS Accession No.
ML071350291. The existing version of the CA BTP, published in 1995,
(ADAMS Accession No. ML033630732) is not fully risk-informed and
performance-based, and does not always describe the bases for its
concentration averaging positions. It also needs to be revised to
incorporate new provisions related to blending of low-level waste
(LLW), as directed by the Commission in its Staff Requirements
Memorandum for SECY-10-0043, ``Blending of Low-Level Radioactive
Waste,'' (ADAMS Accession No. ML102861764).
The NRC's regulations at Title 10 of the Code of Federal
Regulations (10 CFR) Part 61, ``Licensing Requirements for Land
Disposal of Radioactive Waste,'' establishes a waste classification
system based on the concentration of specific radionuclides contained
in the waste. The regulations in 10 CFR 61.55(a)(8) state that ``[t]he
concentration of a radionuclide [in waste] may be averaged over the
volume of the waste, or weight of the waste if the units [on the values
tabulated in the concentration tables] are expressed as nanocuries per
gram.'' The purpose of the waste classification system is to contribute
to protection of individuals that inadvertently intrude into a waste
disposal facility, a requirement in the NRC's disposal regulations at
10 CFR 61.42. Waste is classified according to the hazard it presents
to an inadvertent intruder, and risk to the intruder is managed by
having increased disposal facility control measures, such as depth of
disposal, as the hazard increases. The concentration averaging
provisions of the 1995 CA BTP were specifically developed to ensure
that individual items (e.g., disused sealed sources or other
radiological ``hot spots'') with significantly greater radioactivity
than the average activity in a package are safely disposed. Constraints
on radiological hot spots are needed to ensure intruder protection, and
the CA BTP identifies these constraints.
The NRC staff initially developed a technical position on
radioactive waste classification in May 1983 (ADAMS Accession No.
ML033630755). That technical position paper described overall
procedures acceptable to NRC staff which could be used by licensees to
determine the presence and concentrations of the radionuclides listed
in 10 CFR 61.55, and thereby classify waste for near-surface disposal.
In 1995, the NRC staff published the CA BTP, expanding on Section C.3,
``Concentration Volumes and Masses,'' (i.e., concentration averaging)
of the 1983 Technical Position. The 1995 CA BTP recommended constraints
on averaging of homogeneous waste types \1\ (e.g., ion exchange resins,
soil, ash), mixtures of discrete items (such as irradiated reactor
hardware) and sealed sources for the purposes of ensuring intruder
protection against hot spots, as well as constraining the amount of
averaging that licensees could perform that would lower the
classification of wastes.
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\1\ Waste in which the concentrations of radionuclides of
concern are likely to approach uniformity in the context of
reasonably foreseeable intruder scenarios.
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There have been a number of changes in the LLW program since the
1995 CA BTP was published; these changes were drivers for the current
revision. First, the Commission reviewed the CA BTP's position on
blending of LLW. The 1995 version constrained the concentration of
input waste streams to mixtures of mixable wastes (i.e., waste that is
not composed of discrete items) to within a factor of 10 of the average
concentration of the final mixture. Also, the 1995 version does not
constrain mixing of these wastes if operational efficiency or worker
exposures were affected by the blending. The Commission directed the
staff to implement a risk-informed, performance-based approach for LLW
blending that made the hazard (i.e., the radioactivity concentration)
of the final mixture, the primary consideration for averaging
constraints. Second, the NRC adopted a risk-informed, performance-based
regulatory approach for its programs in the late 1990's, after the 1995
CA BTP was published. This new revision of the CA BTP more fully
reflects that regulatory approach, not just for the blending positions,
but for all of the other topics it addresses as well. Finally, the 1995
CA BTP significantly constrained disposal of encapsulated sealed
sources below the Class B and C limits in the 10 CFR 61.55 waste
classification tables. The threat of a radiological dispersal device
using sealed radioactive sources caused the staff to re-examine the
1995 assumptions underlying the radioactivity constraints on sealed
source disposal, and to better balance the risk associated with
inadvertent intrusion with national security and safety issues
associated with sealed sources that have no disposal pathway. Licensees
must store sealed sources for potentially long periods of time if there
is no disposal option, and the sources are subject to loss or
abandonment. The CA BTP's revised positions will allow for disposal of
more sealed sources than the 1995 CA BTP which will enhance national
security by ensuring that the safest and most secure method to manage
them is available to licensees.
III. Stakeholder Comments on the August 2011 Draft CA BTP
The draft Revision 1 of the CA BTP that is being made available for
public comment is a revision to an August 2011 draft that was provided
to the NRC's Advisory Committee on Reactor Safeguards (ACRS) for review
and comment. The NRC staff briefed the ACRS on October 4 and December
1, 2011, and the ACRS provided their views to the Commission in a
December 13, 2011, letter (ADAMS Accession No. ML11354A407). The NRC
staff also held a public meeting to solicit comments on the August 2011
draft in Albuquerque, New Mexico, on October 20, 2011. The meeting
summary is in ADAMS Accession No. ML113330167. At that meeting,
stakeholders requested that
[[Page 34413]]
NRC staff revise the existing version to address their comments before
publishing it for public comment again. The staff agreed to that
request.
In addition, the staff met with the Low-Level Radioactive Waste
Forum's (LLW Forum) Disused Source Working Group on February 9, 2012,
in Dallas, Texas, to explain the bases for the revised CA BTP and to
answer questions. The Agreement States that regulate the four active
LLW disposal sites (Texas, South Carolina, Utah, and Washington) and
that are members of the Disused Source Working Group provided formal
comments on the August 2011 draft.\2\ The LLW Forum also provided
written comments (ADAMS Accession No. ML120530573).
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\2\ Texas Commission on Environmental Quality, ADAMS Accession
No. ML120530077; South Carolina Department of Health and
Environmental Control, ADAMS Accession No. ML120520496; Utah
Department of Environmental Conservation, ADAMS Accession No.
ML120520498; Washington Office of Radiation Protection, ADAMS
Accession No. ML120520505)
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All of these comments, from the ACRS; stakeholders at the October
20, 2011, workshop; and the members of the Disused Source Working
Group--have been considered in the revised draft that is being made
available in this document. Appendices D, E, and H of draft Revision 1
contain the staff's analysis and responses to comments from
stakeholders at the October 20, 2011, workshop; from members of the LLW
Forum's Disused Source Working Group; and from the ACRS, respectively.
Several other stakeholders also provided additional comments in
February and April 2012 (ADAMS Accession Nos. ML120520558, ML120890046,
and ML121220126), and these were considered to the extent possible in
developing this revised draft. The staff did not document responses to
their comments because of schedule constraints. For any of these
comments that the staff has not fully responded to, the staff will
address them in preparing the final version of the CA BTP. A redline-
strikeout comparison between the May 2012 draft and the August 2011
draft is contained in ADAMS Accession No. ML12137A262.
The staff is interested in stakeholder views on all responses to
issues that were raised in the above comments, but is particularly
interested in stakeholder views on the following topics:
Selection of inadvertent intruder exposure scenarios: In the
original and revised CA BTP, the staff postulated generic exposure
scenarios to evaluate the doses to an inadvertent intruder exposed to
radiological hot spots in mixable wastes and in individual items to
establish concentration averaging constraints. Because it is not
possible to predict human behavior with complete accuracy over the time
frames associated with the hazard from LLW, the staff has used what it
believes to be reasonable, yet conservative scenarios, such as well
drilling into waste. The ACRS and others have commented on the
selection of scenarios. The staff is interested in receiving public
input on the specific scenarios used for this revised draft, as well as
factors to be considered in selection of generic radiation exposure
scenarios for an inadvertent intruder. Information on the selection of
scenarios is provided in the CA BTP in Appendix B; Appendix D
(responses to comments 1(c) and 6(a); and the staff's February 3, 2012,
response (ADAMS Accession No. ML120090314) \3\ to the ACRS letter
(ADAMS Accession No. ML11354A407).\4\ An important impact of scenario
selection is the constraint on the activity of sealed sources for
disposal under the CA BTP. The revised CA BTP uses a new scenario that
would allow for disposal of higher activity sources to be disposed of
in commercial LLW disposal sites that would result in these sources no
longer posing a threat to national security. Some stakeholders,
including ACRS, have argued for the use of scenarios that would result
in fewer constraints on sources, and higher activities for disposal
than what the staff has proposed.
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\3\ The February 3, 2012, staff response is contained in
Appendix H of the CA BTP.
\4\ The December 13, 2011, ACRS letter is contained in Appendix
G of the CA BTP.
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Other ACRS recommendations and issues: The ACRS and staff were in
agreement on a number of positions in the revised CA BTP, such as
blending of LLW, and the new Alternative Approaches section. However,
the ACRS had a number of recommendations that could potentially
significantly change the CA BTP, including allowing for reliance on
perpetual care funds for institutional controls to prevent or mitigate
the impacts of inadvertent intrusion and using probability of intrusion
in developing averaging positions. The staff is interested in
stakeholder views on the pros and cons of the ACRS recommendations,
given their potentially significant impacts on current practices. The
ACRS letter to the Commission (ADAMS Accession No. ML11354A407) is
contained in Appendix G of the revised CA BTP.
Classification of cartridge filters as a homogeneous waste:
Cartridge filters are used to remove radioactive solids from various
systems in a nuclear power plant. Filters are typically composed of
thin metal or plastic frames with a corrugated or wound paper or
synthetic filter media enclosed within the frame. Although the frames
and filter media are contained in fairly robust metal housings, the
housing is perforated so that radioactivity from the filters could be
dislodged during handling by an inadvertent intruder. In addition,
although filters may contain high levels of non-gamma emitting
radionuclides, they typically contain low amounts of long-lived gamma
radionuclides that would pose a hazard to an intruder handling a
discrete item. The current CA BTP classifies cartridge filters as
discrete wastes, so that each filter must be individually characterized
for the concentrations and amounts of radionuclides that may affect
waste classification. Several stakeholders have argued that the
characteristics of cartridge filters previously described are
significantly different from discrete items such as sealed sources or
activated metal and justify their treatment as homogeneous wastes.
Homogeneous wastes are subject to less stringent averaging constraints.
The revised CA BTP continues to classify filters as discrete wastes,
but provides an option for licensees to document justifications for
treatment of them as homogeneous wastes. Section 4.3.4, ``Cartridge
Filters as Homogeneous Waste,'' and the staff's response to comment
3(a) in Appendix D describes the revised position on cartridge filters
and its basis. The staff is specifically seeking stakeholder views on
this revision to the previous draft.
Homogeneity Test for Mixable Wastes: The staff received significant
comments on the proposed testing for homogeneity of blended waste in
the August 2011 draft Revision 1 of CA BTP. The staff has addressed
these comments and made significant revisions. See Section 4.2.2 of the
revised CA BTP, ``Homogeneity of Mixable Waste,'' as well as Section
4.9, ``Alternative Approaches.'' See also responses to comments 1(c)
and 1(g) in Appendix D.
Specification of Waste to Binder Ratio and Not Container Size for
Encapsulation of LLW: The 1995 CA BTP provided for encapsulation of
discrete, higher-activity items in a non-radioactive medium such as
concrete, and averaging the activity in the discrete item over a 55
gallon drum volume. The amount of non-radioactive material over which
averaging could take place was constrained to 55 gallons, so that
extreme averaging measures would not be employed. Several stakeholders
[[Page 34414]]
requested that the waste-to-binder ratio be specified so that larger
volumes could be employed. The constraints would be based on the
average activity of the encapsulated package, and the ratio of the
volume of the radioactive item to the volume of the encapsulating
media. Such an approach would still constrain the use of non-
radioactive materials in averaging. This approach had been approved by
the NRC in a topical report for encapsulating and averaging cartridge
filters. The staff has addressed this comment in revisions to Section
4.5, ``Encapsulation of Sealed Sources and Other Solid Low-Level
Radioactive Wastes,'' and in response to comment 7(a) in Appendix D.
Dated at Rockville, Maryland, this 30th day of May, 2012.
For the Nuclear Regulatory Commission.
Andrew Persinko,
Acting Director, Division of Waste Management and Environmental
Protection, Office of Federal and State Materials and Environmental
Management Programs.
[FR Doc. 2012-14084 Filed 6-8-12; 8:45 am]
BILLING CODE 7590-01-P