Criteria for the Certification and Recertification of the Waste Isolation Pilot Plant's Compliance With the Disposal Regulations; Panel Closure Redesign, 72612-72620 [2013-28240]
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state of Michigan. The Wisconsin
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submitted on July 15, 2013 a negative
declaration certifying that there are no
HMIWI units currently operating in the
state of Wisconsin.
DATES: Comments must be received on
or before January 2, 2014.
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identified by Docket ID No. EPA–R05–
OAR–2013–0678, by one of the
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1. www.regulations.gov: Follow the
on-line instructions for submitting
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2. Email: nash.carlton@epa.gov.
3. Fax: (312) 692–2543.
4. Mail: Carlton T. Nash, Chief, Toxics
and Global Atmosphere Section, Air
Toxics and Assessment Branch (AT–
18J), U.S. Environmental Protection
Agency, 77 West Jackson Boulevard,
Chicago, Illinois 60604.
5. Hand Delivery: Carlton T. Nash,
Chief, Toxics and Global Atmosphere
Section, Air Toxics and Assessment
Branch (AT–18J), U.S. Environmental
Protection Agency, 77 West Jackson
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instructions on how to submit
comments.
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FOR FURTHER INFORMATION CONTACT:
Margaret Sieffert, Environmental
Engineer, Environmental Protection
Agency, Region 5, 77 West Jackson
Boulevard (AT–18J), Chicago, Illinois
60604, (312) 353–1151,
sieffert.margaret@epa.gov.
SUPPLEMENTARY INFORMATION: In the
Rules section of this Federal Register,
EPA is amending 40 CFR part 62 to
reflect the States’ submittals of the
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Any parties interested in commenting
on this action should do so at this time.
Please note that if EPA receives adverse
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if that provision may be severed from
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information, see the direct final rule
which is located in the Rules section of
this Federal Register.
Dated: November 8, 2013.
Susan Hedman,
Regional Administrator, Region 5.
[FR Doc. 2013–28964 Filed 12–2–13; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 194
[EPA–HQ–OAR–2013–0684; FRL–9903–38–
OAR]
Criteria for the Certification and
Recertification of the Waste Isolation
Pilot Plant’s Compliance With the
Disposal Regulations; Panel Closure
Redesign
Environmental Protection
Agency.
ACTION: Proposed rule.
AGENCY:
With this notice, the U.S.
Environmental Protection Agency (EPA,
or the Agency) proposes to approve the
U.S. Department of Energy’s (DOE, or
the Department) planned change request
to implement the Run-of-Mine Panel
Closure System (ROMPCS) at the Waste
Isolation Pilot Plant (WIPP) and to
amend the WIPP Compliance Criteria to
allow an EPA-approved panel closure
other than the currently-required Option
D design. Technical analyses
demonstrate that, with the modified
panel closure design, WIPP remains in
compliance with the release limits set
by the ‘‘Environmental Standards for the
Management and Disposal of Spent
Nuclear Fuel, High-Level and
Transuranic (TRU) Radioactive Waste.’’
The proposed changes do not lessen the
requirements for complying with the
Compliance Criteria, nor do these
changes impact the technical approach
that the EPA will employ when
considering any future planned changes
to the panel closure system. Compliance
with environmental or public health
regulations other than the EPA’s
disposal regulations and WIPP
Compliance Criteria is not addressed by
today’s action. Today’s notice marks the
beginning of a 60-day public comment
period on this proposed action.
SUMMARY:
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Comments must be received on
or before February 3, 2014.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–HQ–
OAR–2013–0684, by one of the
following methods—
• www.regulations.gov: Follow the
on-line instructions for submitting
comments.
• Email: to a-and-r-docket@epa.gov;
Docket ID No. EPA–HQ–OAR–2013–
0684.
• Fax: (202) 566–1741.
• Mail: Air and Radiation Docket and
Information Center, Environmental
Protection Agency, Mail Code: 6102T,
1200 Pennsylvania Ave. NW.,
Washington, DC 20460.
Instructions: Direct your comments to
Attn: Docket ID No. EPA–HQ–OAR–
2013–0684. The Agency’s policy is that
all comments received will be included
in the public docket without change and
may be made available online at
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through www.regulations.gov
or email. The www.regulations.gov Web
site is an ‘‘anonymous access’’ system,
which means the EPA will not know
your identity or contact information
unless you provide it in the body of
your comment. If you send an email
comment directly to the EPA without
going through www.regulations.gov,
your email address will be
automatically captured and included as
part of the comment that is placed in the
public docket and made available on the
Internet. If you submit an electronic
comment, the EPA recommends that
you include your name and other
contact information in the body of your
comment and with any disk or CD–ROM
you submit. If the EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
the Agency may not be able to consider
your comment. Electronic files should
avoid the use of special characters or
any form of encryption and be free of
any defects or viruses. For additional
information about the EPA’s public
docket, visit the EPA Docket Center
homepage at https://www.epa.gov/
epahome/dockets.htm.
Docket: All documents in the docket
are listed in the www.regulations.gov
index. Although listed in the index,
some information is not publicly
available, e.g., CBI or other information
whose disclosure is restricted by statute.
DATES:
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Certain other material, such as
copyrighted material, will be publicly
available only in hard copy. The EPA
has established a docket for this action
under Docket ID No. [EPA–HQ–OAR–
2013–0684; FRL–9903–38–OAR].
Publicly available docket materials
related to this action (e.g., the Technical
Support document [TSD]) are available
either electronically through
www.regulations.gov, on the Agency’s
WIPP Web site (https://www.epa.gov/
radiation/wipp) or in hard copy at the
Air and Radiation Docket in the EPA
Docket Center, (EPA/DC) EPA West,
Room 3334, 1301 Constitution Ave.
NW., Washington, DC 20004. The EPA
Docket Center Public Reading Room is
open from 8:30 a.m. to 4:30 p.m.,
Monday through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744
and the telephone number for the Air
and Radiation Docket is (202) 566–1742.
In accordance with the EPA’s
regulations at 40 CFR part 2 and in
accordance with normal EPA docket
procedures, if copies of any docket
materials are requested, a reasonable fee
may be charged for photocopying.
FOR FURTHER INFORMATION CONTACT: Ray
Lee or Jonathan Walsh, Radiation
Protection Division, Mail Code 6608J,
U.S. Environmental Protection Agency,
1200 Pennsylvania Avenue,
Washington, DC 20460; telephone
number: 202–343–9463 or 202–343–
9238; fax number: 202–343–2305; email
address: lee.raymond@epa.gov or
walsh.jonathan@epa.gov.
SUPPLEMENTARY INFORMATION:
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Preamble Acronyms and Abbreviations:
Several acronyms and terms used to
describe components of the WIPP
disposal system and performance
assessment computer models are
included in this preamble. To ease the
reading of this preamble and for
reference purposes, the following terms
are defined here:
BRAGFLO Computer model used to
simulate brine and gas flow
CBFO Carlsbad Field Office
CCA Compliance Certification Application
CCDF Complementary Cumulative
Distribution Function
CFR Code of Federal Regulations
DBR Direct Brine Release
DOE U.S. Department of Energy
DRZ Disturbed Rock Zone
EPA U.S. Environmental Protection Agency
FEPs Features, Events and Processes
LWA Land Withdrawal Act
MSHA Mine Safety and Health
Administration
NMED New Mexico Environment
Department
OPC Ordinary Portland Cement
PA Performance Assessment
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PABC Performance Assessment Baseline
Calculation
PAVT Performance Assessment Verification
Test
PCS Panel Closure System
PCS–2012 Panel Closure System 2012
Performance Assessment
PCR Planned Change Request
PC3R Panel Closure Redesign and
Repository Reconfiguration Performance
Assessment
PMR Permit Modification Request
RCRA Resource Conservation and Recovery
Act
ROM Run-of-Mine
ROMPC, or
ROMPCS6 Run-of-Mine Salt Panel Closure
System
SMC Salado Mass Concrete
SNL Sandia National Laboratories
TRU Transuranic
TSD Technical Support Document
VOC Volatile Organic Compound
WIPP Waste Isolation Pilot Plant
Table of Contents
I. General Information
A. What should I consider as I prepare my
comments for the EPA?
II. What is the WIPP?
III. What is the purpose of today’s proposed
action?
IV. How is the EPA responding to the DOE’s
planned change request?
A. What are the EPA’s requirements for the
panel closure design?
B. What changes are proposed to the panel
closure design?
C. How has the EPA reached its decision?
V. How is the EPA revising Appendix A,
Condition 1?
A. What are the current requirements of
Appendix A, Condition 1?
B. What changes are proposed to Appendix
A, Condition 1?
C. What did the EPA consider when
making its decision?
VI. How has the EPA involved the public?
VII. Administrative Requirements
A. Executive Order 12866
B. Regulatory Flexibility Act
C. Paperwork Reduction Act
D. Unfunded Mandates Reform Act
E. Executive Order 12898
F. National Technology Transfer &
Advancement Act of 1995
G. Executive Order 13045: Children’s
Health Protection
H. Executive Order 13132: Federalism
I. Executive Order 13175: Consultation and
Coordination With Indian Tribal
Governments
J. Executive Order 13211: Energy Effects
I. General Information
A. What should I consider as I prepare
my comments for the EPA?
1. Submitting Confidential Business
Information (CBI):
Do not submit this information to the
EPA through www.regulations.gov or
email. Clearly mark all of the
information that you claim to be CBI.
For CBI information in a disk or CD
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ROM that you mail to the EPA, mark the
outside of the disk or CD ROM as CBI
and then identify electronically within
the disk or CD ROM the specific
information that is claimed as CBI. In
addition to one complete version of the
comment that includes information
claimed as CBI, a copy of the comment
that does not contain the information
claimed as CBI must be submitted for
inclusion in the public docket.
Information marked as CBI will not be
disclosed except in accordance with
procedures set forth in 40 CFR part 2.
2. Tips for Preparing Your Comments:
When submitting comments,
remember to—
• Identify the rulemaking by docket
number, subject heading, Federal
Register date and page number.
• Follow directions—the EPA may
ask you to respond to specific questions
or organize comments by referencing the
chapter number.
• Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
• Describe any assumptions and
provide any technical information and/
or data that you used.
• If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow it to be reproduced.
• Illustrate your concerns with
specific examples and suggest
alternatives.
• Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
• Make sure to submit your
comments by the comment period
deadline identified.
II. What is the WIPP?
The WIPP is a disposal system for
defense-related transuranic (TRU)
radioactive waste. Developed by the
DOE, the WIPP is located near Carlsbad
in southeastern New Mexico. At the
WIPP, radioactive waste is disposed of
2,150 feet underground in an ancient
formation of salt which will eventually
‘‘creep’’ and encapsulate the waste. The
WIPP has a total capacity of 6.2 million
cubic feet of waste.
Congress authorized the development
and construction of the WIPP in 1980
‘‘for the express purpose of providing a
research and development facility to
demonstrate the safe disposal of
radioactive wastes resulting from the
defense activities and programs of the
United States.’’ 1 Waste which may be
1 Department of Energy National Security and
Military Applications of Nuclear Energy
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emplaced in the WIPP is limited to TRU
radioactive waste generated by defense
activities associated with nuclear
weapons; no high-level waste or spent
nuclear fuel from commercial power
plants may be disposed of at the WIPP.
TRU waste is defined as materials
containing alpha-emitting radioisotopes,
with half lives greater than twenty years
and atomic numbers above 92, in
concentrations greater than 100 nanocuries per gram of waste.2 Most TRU
waste proposed for disposal at the WIPP
consists of items that have become
contaminated as a result of activities
associated with the production of
nuclear weapons (or with the clean-up
of weapons production facilities), e.g.,
rags, equipment, tools, protective gear,
soil and organic or inorganic sludges.
Some TRU waste is mixed with
hazardous chemicals. The waste
proposed for disposal at the WIPP is
currently located at federal facilities
across the United States, including
locations in California, Idaho, Illinois,
New Mexico, Nevada, Ohio, South
Carolina, Tennessee and Washington.
The WIPP Land Withdrawal Act
(LWA), initially passed by Congress in
1992 and amended in 1996, provides
the EPA authority to oversee and
regulate the WIPP. The WIPP LWA
delegated to the EPA three main tasks,
to be completed sequentially, for
reaching an initial compliance
certification decision. First, the Agency
was required to finalize general
regulations which apply to all sites—
except Yucca Mountain—for the
disposal of highly radioactive waste.3
These disposal regulations, located at
Subparts B and C of 40 CFR part 191,
were originally published in the Federal
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Authorization Act of 1980, Public Law 96–164,
section 213.
2 WIPP Land Withdrawal Act, Pub. L. 102–579,
section 2(18), as amended by the 1996 WIPP LWA
Amendments, Pub. L. 104–201.
3 WIPP LWA, section 8(b).
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Register in 1985 and amended in 1993.4
Second, the EPA was to develop criteria,
by rulemaking, to implement and
interpret the general radioactive waste
disposal regulations specifically for the
WIPP. In 1996, the Agency issued the
WIPP Compliance Criteria, which are
found at 40 CFR part 194.5 The EPA
made changes to the Compliance
Criteria via rulemaking in July 2004 (69
FR 42571–42583). These new provisions
provide equivalent or improved
oversight and better prioritization of
technical issues in EPA inspections to
evaluate waste characterization
activities at DOE WIPP waste generator
sites, and offer more direct public input
into the Agency’s decisions about what
waste can be disposed of at the WIPP.
Third, the EPA was to review the
information submitted by the DOE and
publish a certification decision.6 The
Agency issued its certification decision
on May 18, 1998, as required by Section
8 of the WIPP LWA (63 FR 27354–
27406) determining that the WIPP met
the standards for radioactive waste
disposal. The complete record and basis
for the EPA’s 1998 certification decision
can be found in Air Docket A–93–02.
Condition 1, concerning the panel
closure system, was appended to 40
CFR part 194 as part of the certification
decision.
Section 8(f) of the WIPP LWA requires
that within five years of initial receipt
of waste at the WIPP, and every five
years thereafter, the DOE is to submit to
the EPA and the State of New Mexico
documentation of continued compliance
with the part 191 radioactive waste
disposal regulations. The Agency
recertified the WIPP facility for the first
time on March 29, 2006 (71 FR 18010–
18021) and again on November 18, 2010
(75 FR 70584–70595).
4 50 FR 38066–38089 (September 19, 1985) and
58 FR 66398–66416 (December 20, 1993).
5 61 FR 5224–5245 (February 9, 1996).
6 WIPP LWA, section 8(d).
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The Department submitted the design
of the WIPP repository in Chapter 3 of
the 1996 Compliance Certification
Application (CCA). The EPA’s
certification is based upon this design.
The underground waste disposal region
at WIPP is divided into panels. A panel
is a group of rooms mined into the salt,
connected by tunnels called drifts.
When all of the rooms of a panel are
filled with waste, the DOE intends to
seal the drifts with engineered
structures called panel closures. The
EPA certified the WIPP based on a panel
closure design that sealed the drift using
a concrete block wall and a poured
concrete monolith. The DOE proposes to
change this design and close the drift
using two steel bulkheads and mined
salt. Both panel closure designs are
discussed in detail in Section IV of this
document.
III. What is the purpose of today’s
proposed action?
This action is being taken in response
to the DOE’s September 2011 Planned
Change Request (PCR) to alter the design
of the panel closures used at the WIPP.
The WIPP underground waste disposal
area is divided into ten groups of rooms,
or panels. A waste panel is a group of
mined rooms connected by drifts that
provide both access and ventilation to
the rooms. Following completion of
waste disposal activities in each panel,
the DOE intends to seal these drifts with
engineered structures called panel
closures. 40 CFR part 194, Criteria for
the Certification and Recertification of
the Waste Isolation Pilot Plant’s
Compliance with the 40 CFR part 191
Disposal Regulations, did not originally
require panel closures for the purpose of
long-term compliance with release
limits for radionuclides. Panel closures
have, however, always been included in
the design of the repository, and
therefore incorporated into modeling of
the WIPP system as a feature of the
repository.
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Although the Agency determined that
the DOE met all of the applicable
requirements of the WIPP Compliance
Criteria in its compliance certification
decision (63 FR 27354–27406; May 18,
1998), the EPA amended the WIPP
Compliance Criteria, 40 CFR part 194,
and appended four explicit conditions
to its certification of compliance to
ensure that the measures actually
implemented at the WIPP (and thus the
circumstances expected to exist there)
were consistent with the DOE’s
Compliance Certification Application
(CCA) and with the basis for the EPA’s
compliance certification. Condition 1 of
the certification applies to the panel
closure system.7 In the CCA, the
7 Conditions 2 and 3 of the final certification
decision apply to activities conducted at waste
generator sites that produce TRU waste proposed
for disposal at WIPP (§§ 194.22 and 194.24), and
Condition 4 of the certification applies to passive
institutional controls (PICs), records and physical
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Department presented four options for
the design of the panel closure system,
but did not specify which would be
constructed at the WIPP facility. The
Agency based its certification decision
on the DOE’s use of the most robust
design, referred to in the CCA as
‘‘Option D’’.
At the time of the 1998 certification
decision, there were indications that the
DOE would seek to change the design of
the panel closure system selected by the
EPA. As stated in the original
certification:
Nothing in this condition precludes DOE
from reassessing the engineering of the panel
seals at any time. Should DOE determine at
any time that improvements in materials or
construction techniques warrant changes to
the panel seal design, DOE must inform EPA.
markers to warn future societies about the location
and contents of the disposal system and thus to
deter inadvertent intrusion into the WIPP
(§ 194.43).
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If EPA concurs, and determines that such
changes constitute a significant departure
from the design on which certification is
based, the Agency is authorized under
§ 194.65 to initiate a rulemaking to
appropriately modify the certification.’’ (63
FR 27354, 27362; May 18, 1998.)
In 2002, the Agency approved the
DOE’s request to install only the
explosion wall, and to extend the panel
closure installation schedule until a
new design is approved. In January
2007, the DOE requested that
installation of the explosion walls also
be delayed until a new design could be
approved, and proposed to monitor gas
generation in Panels 3 and 4 of the
repository. The EPA approved this
request in February 2007. Today’s
action represents the first time that the
Agency has considered an alteration to
the panel closure design itself.
The Department submitted a PCR to
the EPA on September 28, 2011. Citing
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experience and data gained since the
CCA, the DOE’s PCR states that the
Option D panel closure would be
extremely difficult and costly to install,
and that the highly engineered design is
unnecessary for either worker safety or
environmental protection during the
operational period. The DOE instead
proposed a new panel closure design,
the Run-of-Mine Salt Panel Closure
System (ROMPCS), which consists of
mined salt emplaced between steel
bulkheads.
The EPA has completed its technical
review of the DOE’s PCR and supporting
documentation. The goal of the
Agency’s technical review process was
to determine whether, with the new
design, the WIPP adequately
demonstrates compliance with the
requirements of 40 CFR part 194 and the
release limits of 40 CFR part 191
Subparts B and C. The process the EPA
applied to support this proposed action
entailed (1) a review of all materials
submitted by the DOE, (2) requests for
additional information including a full
performance assessment, and (3) the
independent performance of additional
confirmatory calculations by the
Agency. This process is fully
documented in the EPA’s TSD, ‘‘Review
of the DOE’s Planned Change Request to
Modify the WIPP Panel Closure
System,’’ (EPA–HQ–OAR–2013–0684–
0002) and discussed in the following
sections. Based on this process, the
Agency concludes that the WIPP will
remain in compliance with its release
limits with the ROMPCS design. The
Agency therefore proposes to approve
the DOE’s PCR to implement the
redesigned panel closure at the WIPP,
and to modify 40 CFR part 194
Appendix A, Condition 1 to allow a
panel closure design other than Option
D. Section IV, below, discusses the
Agency’s consideration of the proposed
panel closure modification. Section V
describes the Agency’s approach to
modifying Condition 1.
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IV. How is the EPA responding to the
DOE’s planned change request?
A. What are the EPA’s requirements for
the panel closure design?
During the operational period of the
repository, the panel closure system was
intended to prevent access to closed
waste panels, to mitigate the release of
volatile organic compounds (VOCs) and
to protect site workers from a
hypothetical methane or hydrogen
explosion inside a filled waste panel.
These functions are addressed by the
New Mexico Environment Department
(NMED), and DOE has submitted a
separate Resource Conservation and
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Recovery Act (RCRA) Permit
Modification Request (PMR) stating that
the new panel closure design will
adequately protect workers and the
public during the operational period of
the WIPP.
The EPA’s Compliance Criteria at 40
CFR part 194 originally did not require
a panel closure of any kind to be
installed in the repository for the
purpose of long-term compliance with
release limits for radionuclides. The
purpose of 40 CFR part 194 is to
demonstrate compliance with the
disposal regulations at 40 CFR part 191
for containment of radionuclides. The
containment requirements at 40 CFR
191.13 specify that releases of
radionuclides to the accessible
environment must be unlikely to exceed
specific release limits for 10,000 years
after disposal, based on the amount of
waste in the repository at the time of
closure (§ 194.31). Assessment of the
likelihood that the WIPP will not exceed
release limits is accomplished through a
process called performance assessment,
or PA. The WIPP PA process culminates
in a series of computer simulations that
model the physical attributes of the
disposal system (e.g., site
characteristics, waste forms and
quantities, engineered features) in a
manner that captures the behaviors and
interactions among its various
components. The computer simulations
require the development of conceptual
models that represent physical
attributes of the repository based on
features, events and processes (FEPs)
that may impact the disposal system.
The conceptual models are then
expressed as mathematical
relationships, which are solved with
iterative numerical models, which are
then translated into computer codes
(§ 194.23). Numerous simulations are
performed using sampled values for
material properties and processes whose
values are uncertain. The results of the
simulations are intended to calculate
possible releases of radioactive
materials from the disposal system to
the accessible environment over the
10,000-year regulatory period, and are
used to demonstrate compliance with
the containment requirements in 40 CFR
191.13. Because the radionuclide release
limits are based on the amount of waste
in the repository at the time of closure,
the containment requirements are
expressed in terms of ‘‘normalized
releases.’’ The results of the PA are
assembled into complementary
cumulative distribution functions
(CCDFs), which indicate the probability
of exceeding various levels of
normalized releases (§ 194.34).
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At the time of the CCA, given limited
information on how the different panel
closure designs could influence
performance, the Agency contended that
the panel closures constructed in the
repository should have physical
properties similar to those that had been
used to represent them in the compliant
performance assessment. As stated in
the WIPP certification:
EPA based its certification decision on DOE’s
use of the most robust design (referred to in
the CCA as ‘‘Option D’’). The Agency found
the Option D design to be adequate, but also
determined that the use of Salado mass
concrete—using brine rather than fresh
water—would produce concrete seal
permeabilities in the repository more
consistent with the values used in DOE’s
performance assessment. Therefore,
Condition 1 of EPA’s certification requires
DOE to implement the Option D panel
closure system at WIPP, with Salado mass
concrete replacing fresh water concrete. (63
FR 27355)
Because the Agency based its
certification of the WIPP’s compliance
with the disposal regulations on the
accurate representation of the repository
in performance assessment, Condition 1
was appended to 40 CFR Part 194
during the certification of the WIPP. No
other design feature of the repository is
required by the Compliance Criteria in
a similarly explicit way.
B. What changes are proposed to the
panel closure design?
The Option D panel closure design
consists of a 12-foot thick ‘‘explosionisolation wall’’ constructed of solid
concrete blocks filling the drift on the
waste disposal side, a short section of
open drift called an ‘‘isolation zone’’
and a monolithic concrete barrier on the
side of the open drift. Fractured rock in
the immediate vicinity of the drift—
called the disturbed rock zone, or
DRZ—would be removed, and the
resulting void space filled by the
concrete monolith. In its current PCR,
the DOE states that ‘‘large scale testing
has demonstrated that using SMC
[Salado Mass Concrete] cannot meet the
design and performance requirements
for the panel closures as specified in the
CCA.’’ Even if the Option D monolith
could be constructed as planned, the
Agency acknowledges that it would be
installed at significant cost to the
Department, that additional
occupational hazards would be incurred
by moving and pouring large amounts of
concrete in the underground and that
disposal operations would be
significantly disrupted.
The DOE’s new panel closure design,
the ROMPCS, consists primarily of runof-mine (ROM) salt—impure halite that
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has been mined in the course of normal
repository operations and not subjected
to additional processing or grading. The
ROMPCS design consists of two
standard steel ventilation bulkheads
with a minimum of 100 feet of run-ofmine (ROM) salt between them, filling
the drift from floor to ceiling. In Panels
1, 2 and 5, where explosion walls have
already been constructed, salt will be
placed directly against the explosion
wall and a standard steel ventilation
bulkhead placed on the outer end of the
panel closure. The DOE has stated that
the ROMPCS will provide adequate
protection during the operational
period. Upon initial emplacement, the
run-of-mine salt will exhibit the
properties of a loosely consolidated or
unconsolidated material. Over time, as
the open areas of the repository close
due to salt creep, the panel closures will
consolidate and eventually heal to a
state resembling intact salt.
The EPA’s technical review process is
summarized below in Section C. Based
on the results of performance
assessment, the Agency concludes that
the WIPP will continue to comply with
the EPA’s disposal standards with the
ROMPCS. Therefore, the Agency
proposes to approve the DOE’s PCR and
allow the implementation of the
ROMPCS design at the WIPP.
C. How has the EPA reached its
decision?
As in the past, the Agency’s
consideration of the panel closure
system focused on its inclusion and
accurate representation in repository
performance assessment, so that the
EPA can ultimately certify the WIPP’s
ability to meet long-term performance
standards.
In support of its panel closure PCR,
the DOE initially submitted a
performance assessment calculation
called the Panel Closure Redesign and
Repository Reconfiguration (PC3R) PA,
which incorporated multiple planned
changes. The Agency determined that to
approve the PCR, it was necessary to
isolate the impacts, if any, of the change
in panel closure design. In response, the
DOE prepared the PCS–2012 PA, with
the explicit goal of changing only those
aspects of the current baseline PA that
are directly related to the change in the
panel closure design. Thus, results of
the PCS–2012 PA may be directly
compared to results of the current
Performance Assessment Baseline
Calculation (PABC–09) to see the impact
of changes in the panel closure on
modeled releases from the facility.
The majority of the technical effort
expended by the Agency was spent
determining how the changes in the
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panel closures should be represented in
the performance assessment models.
This review process involved
interactions with the DOE and DOE
contractor staff and is documented in
the Agency’s TSD, ‘‘Review of DOE’s
Planned Change Request to Modify the
WIPP Panel Closure System.’’ (EPA–
HQ–OAR–2013–0684–0002) The
process began by identifying the
universe of changes which might have
taken place within the performance
assessment. The conclusion of the
features, events and processes (FEPs)
review found that the required changes
to the models were limited to the
properties of the panel closure and of
the disturbed rock zone immediately
surrounding it. In performance
assessment, these materials are
represented in the BRAGFLO computer
model, which simulates the flow of
brine and gas in the repository over the
10,000-year period of performance.
Some modeling changes, such as
differences between the physical
dimensions of the panel closure designs,
were relatively simple for the DOE to
implement. The most significant change
between panel closure designs, and the
greatest modeling challenge, was the
dynamic nature of the ROMPCS’s
material properties. The Option D
design called for the excavation of the
DRZ, and the installation of a rigid
concrete monolith which would
effectively prevent further fracturing.
Thus, the properties of the panel closure
and surrounding DRZ were not expected
to change significantly over time, and
were represented in PA by constant
values. The ROMPCS will be emplaced
in a loose form, surrounded by a
fractured DRZ. As the panel closure
system consolidates due to repository
creep closure, it will decrease in
porosity, and its permeability to fluids
will decrease. Based on measurements
taken in the underground, laboratory
data and geomechanical modeling, it is
expected that this consolidation process
will be complete approximately 200
years after the closure of the repository.
The DOE represents the ROMPCS
using three time periods. Two time
periods of one hundred years each are
used to represent the gradual
reconsolidation of the panel closure
system. A third time period, extending
from 200 years after closure to the end
of the 10,000-year performance period,
represents the final healed state of the
PCS. The consolidation of the ROMPC
is modeled by sampling its porosity
from a range of possible values for each
time period. The permeability of the
panel closure to fluids during each time
period is then calculated using a
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correlation between the porosity and
permeability of salt, developed by the
DOE using existing experimental data.
The DRZ surrounding the panel closure
is modeled so that it is more permeable
to fluids during the first 200 years after
closure, and less permeable when the
system has reached a steady state.
Parameter values representing other
material properties of the ROM salt were
directly adopted from parameters that
were developed during the CCA to
describe the crushed salt component of
the shaft seals. The parameters used to
represent the changes in performance
assessment were finalized by the DOE in
a memorandum dated May 3, 2012.
After the EPA’s concurrence with the
representation of the panel closure, the
DOE executed the PCS–2012 PA
calculation. Results of the PCS–2012 PA
are discussed in detail in TSD Section
4.5. Compared to the PABC–2009
baseline, calculated mean total releases
from the PCS–2012 PA did not
appreciably increase at a probability of
0.1, and increased at a probability of
0.001, from 1.1 to 1.51 EPA units. (See
TSD, EPA–HQ–OAR–2013–0684–0002,
Table 3.7.) Thus, the mean total release,
as well as the 90th percentile and upper
95% confidence limit of the mean, fell
significantly below the Agency’s
regulatory limits of 1 EPA unit for a
probability of 0.1, and 10 EPA units for
a probability of 0.001.
Modeled releases from the repository
principally result from the penetration
of the repository waste by a hypothetical
oil or gas borehole. Specific release
mechanisms include cuttings and
cavings releases, direct brine releases
(DBRs), spallings releases and releases
up a borehole to the Culebra dolomite.
The increase in calculated releases in
the PCS–2012 PA is primarily due to
increases in direct brine releases,
resulting from changes in pressure and
brine saturation in the waste panels (See
TSD, EPA–HQ–OAR–2013–0684–0002,
Section 3.5). Compared to the Option D
PCS design, the ROMPCS is expected to
be more permeable to fluids upon
installation, and less permeable after it
has consolidated. The initial conditions
of the WIPP model make a significant
amount of brine available in the
repository at the time of closure. The
higher initial permeability of the
ROMPCS allows early-time brine
inflows into the waste panels, resulting
in generally higher brine saturations and
higher rates of gas generation in the
modeled waste panel. When the
permeability of the panel closures
decreases after 200 years, both brine and
gas can be retained in the panel,
increasing the brine saturations and gas
pressures encountered by borehole
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penetrations of the repository. Those
increases in turn result in increases in
mean DBR and spallings releases.
Cuttings and cavings are important
contributors to total releases, but are not
affected by waste panel pressure and
brine saturation. Releases through the
Culebra are essentially unchanged from
those calculated using the Option D
design.
The EPA considers this analysis
important to its understanding of the
disposal system. The Agency concludes
that the changes to the panel closure
system do not have a significant impact
on the long-term performance of the
disposal system.
V. How is the EPA revising Appendix
A, Condition 1?
A. What are the current requirements of
Appendix A, Condition 1?
The Option D panel closure is
currently required by 40 CFR part 194,
Appendix A, Condition 1.
As described in Section III, the EPA
certified the WIPP’s performance based
on the properties of the Option D panel
closure. It is the only engineered aspect
of the repository design that is explicitly
required by rule.
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B. What changes are proposed for
Appendix A, Condition 1?
As described above in Section IV, the
EPA is proposing to accept a redesigned
panel closure. Acceptance of the PCR
requires modification of Condition 1.
The Agency does not believe that the
design must be specified by the
condition, because there is no evidence
to suggest that the panel closure has a
disproportionate ability to impact longterm performance when compared to
other design features of the repository.
This change does not grant the DOE the
ability to alter the panel closure design
at will. As with any engineered
component of the disposal system, a
departure from the current, approved
design must be submitted to the Agency
as a planned change request as required
by § 194.4(b)(3)(i). The EPA would
expect any such request to be supported
by complete technical documentation,
including information concerning ‘‘the
geology, hydrology, hydrogeology, and
geochemistry of the WIPP disposal
system’’ and ‘‘WIPP materials of
construction, standards applied to
design and construction,’’ as required by
§ 194.14, Content of certification
applications. The Agency would use
this information to determine whether
or not the WIPP remains in compliance
with the disposal standards. As with
any other planned change, based on the
potential impact to the WIPP’s
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compliance, the EPA will determine
whether the change ‘‘departs
significantly from the most recent
compliance application,’’ and must be
addressed by rule in accordance with
§ 194.65.
C. What did the EPA consider when
making its decision?
In 1998, the EPA certified the WIPP
conditionally based on the Option D
panel closure design. At that time, the
DOE had not specified which design it
planned to implement, and limited
performance assessment results were
available to indicate the impact of the
panel closure design on repository
performance. In contrast, the
Department has now proposed a single
panel closure design to be installed in
all waste panels. Due to the evolution of
the WIPP PA since the CCA, the DOE
and the EPA have gained a greater
understanding of panel closures’
influence on PA results.
The Agency initially chose the Option
D panel closure partly to match the
physical properties of the panel closure
to the modeled parameters of the
generic panel closure represented in the
CCA. This representation of the panel
closure was refined in the 2002
Technical Baseline Migration PA to
reflect the dimensions of the Option D
design and include impacts of a rigid
structure on the surrounding DRZ.
These changes did not result in a
significant impact on predicted releases,
and were included in PAs which
supported both WIPP recertifications.
The changes made in the PCS–2012 PA
altered the panel closure properties
substantially, without significantly
affecting the WIPP’s ability to comply
with the release limits. The DOE’s
sensitivity analysis indicates that
several sampled parameters related to
the panel closures contributed to the
overall results, but their contributions
were dwarfed by the effect of other
parameters, such as the waste shear
strength and actinide solubility.
Additionally, the Agency carried out
confirmatory studies as part of its
technical review which analyzed how
different representations of the DRZ
surrounding the panel closure could
potentially influence modeled results.
The conclusion that the Agency draws
from all of these studies is that although
the panel closures can influence
modeled results to a degree, there is no
evidence that modifications to the panel
closure or its representation in PA could
jeopardize the WIPP’s ability to comply
with the disposal requirements. Because
panel closures do not exercise a
disproportionate impact on the WIPP’s
ability to isolate radionuclides from the
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accessible environment, the EPA does
not believe that it is necessary for the
specific design of the panel closure to
remain as a condition of certification.
Rather, panel closures can be treated in
a similar manner as any other
engineered feature of the repository. As
described in Section IV, the DOE must
still submit a PCR if it wishes to alter
the design from the approved ROMPCS.
VI. How has the EPA involved the
public?
In order to guide its technical process,
the EPA held informal public meetings
in Carlsbad, New Mexico, on December
5, 2012, and Santa Fe, New Mexico, on
December 6, 2012. The purpose of these
meetings was to provide the public with
background on the DOE’s panel closure
system planned change request, and to
give the public the opportunity to raise
any technical issues that the Agency
should consider in its decision. At both
meetings, many comments were in favor
of approving the panel closure planned
change request based on its scientific
and economic merits. Specifically,
commenters expressed confidence in
the ability of salt creep to compress the
ROMPCS and form an adequate panel
closure, and emphasized the greater
operational safety when installing the
revised design. In Santa Fe, one
commenter expressed the view that the
lack of a cost analysis for building the
Option D panel closures, and the failure
to explicitly consider other designs are
deficiencies in the PCR. Other
commenters asked questions regarding
the likelihood of gas generation and
explosions in the closed panels. No
technical comments were submitted.
Additional public meetings will be
held in Carlsbad and Albuquerque in
December 2013. Details and summaries
of these meetings will be published on
the EPA’s WIPP Web site at https://
www.epa.gov/radiation/wipp.
VII. Administrative Requirements
A. Executive Order 12866
Under Executive Order 12866, (58 FR
51735; October 4, 1993), the Agency
must determine whether the regulatory
action is ‘‘significant’’ and therefore
subject to OMB review and the
requirements of the Executive Order.
The Order defines ‘‘significant
regulatory action’’ as one that is likely
to result in a rule that may: (1) Have an
annual effect on the economy of $100
million or more or adversely affect in a
material way the economy, a sector of
the economy, productivity, competition,
jobs, the environment, public health or
safety, or state, local, or tribal
governments or communities; (2) create
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a serious inconsistency or otherwise
interfere with an action taken or
planned by another Agency; (3)
materially alter the budgetary impact of
entitlements, grants, user fees or loan
programs or the rights and obligations of
recipients thereof; or (4) raise novel
legal or policy issues arising out of legal
mandates, the President’s priorities or
the principles set forth in the Executive
Order. Pursuant to the terms of
Executive Order 12866, it has been
determined that this rule is not a
‘‘significant regulatory action.’’
B. Regulatory Flexibility Act
The Regulatory Flexibility Act
(‘‘RFA’’) generally requires any federal
agency to conduct a regulatory
flexibility analysis of any rule subject to
notice and comment rulemaking
requirements unless they certify that the
rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small not-forprofit enterprises and small
governmental jurisdictions. This
proposed rule will not have a significant
impact on a substantial number of small
entities because it sets forth
requirements which apply only to
federal agencies. Therefore, this action
will not have a significant economic
impact on a substantial number of small
entities.
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C. Paperwork Reduction Act
This proposed action does not impose
an information collection burden under
the provisions of the Paper Reduction
Act, 44 U.S.C. 3501 et seq. The
Compliance Criteria in 40 CFR part 194
requirements are applicable only to the
DOE and the EPA and do not establish
any form of collection of information
from the public.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (‘‘UMRA’’), Public
Law 104–4, establishes requirements for
federal agencies to assess the effects of
their regulatory actions on state, local
and tribal governments and the private
sector. Pursuant to Title II of the UMRA,
we have determined that this regulatory
action is not subject to the requirements
of sections 202 and 205, because this
action does not contain any ‘‘federal
mandates’’ for state, local or tribal
governments or for the private sector.
This rule applies only to federal
agencies.
E. Executive Order 12898
Pursuant to Executive Order 12898
(59 FR 7629; February 16, 1994),
entitled ‘‘Federal Actions to Address
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Environmental Justice in Minority
Populations and Low-Income
Populations,’’ the Agency has
considered environmental justice
related issues with regard to the
potential impacts of this action on the
environmental and health conditions in
low-income, minority and NativeAmerican communities. We have
complied with this mandate. However,
the requirements specifically set forth
by the Congress in the Waste Isolation
Pilot Plant Land Withdrawal Act (Pub.
L. 102–579), which prescribes the EPA’s
role at the WIPP, did not provide
authority for the Agency to examine
impacts in the communities in which
wastes are produced, stored and
transported, and Congress did not
delegate to the EPA the authority to
consider the issue of alternative
locations for the WIPP. During the
development of the existing provisions
in 40 CFR part 194, the EPA involved
minority and low income populations
early in the rulemaking process. In
1993, the EPA representatives met with
New Mexico residents and government
officials to identify the key issues that
concern them, the types of information
they wanted from the Agency and the
best ways to communicate with
different sectors of the New Mexico
public. The feedback provided by this
group of citizens formed the basis for
the EPA’s WIPP communications and
consultation plan. To help citizens
(including a significant Hispanic
population in Carlsbad and the nearby
Mescalero Indian Reservation) stay
abreast of the EPA’s WIPP-related
activities, the Agency developed many
informational products and services.
The EPA translated several documents
regarding WIPP into Spanish, including
educational materials and fact sheets
describing the EPA’s WIPP oversight
role and the radioactive waste disposal
standards. The Agency established a
toll-free WIPP Information Line,
recorded in both English and Spanish,
providing the latest information on
upcoming public meetings, publications
and other WIPP-related activities. The
EPA also developed a mailing list,
which includes many low-income,
minority and Native-American groups,
to systematically provide interested
parties with copies of EPA’s public
information documents and other
materials. Even after the final rule, in
1998, the EPA has continued to
implement outreach services to all WIPP
communities based on the needs
determined during the certification. The
Agency has established a WIPP–NEWS
email listserv to facilitate
communications with interested
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stakeholders not only in New Mexico
and surrounding areas, but nationally
and internationally as well. The EPA’s
WIPP Web site is also continuously
updated with relevant news and
updates on current and future WIPP
activities.
F. National Technology Transfer &
Advancement Act of 1995
Section 12 of the National Technology
Transfer & Advancement Act of 1995 is
intended to avoid ‘‘re-inventing the
wheel.’’ It aims to reduce costs to the
private and public sectors by requiring
federal agencies to draw upon any
existing, suitable technical standards
used in commerce or industry. To
comply with the Act, the EPA must
consider and use ‘‘voluntary consensus
standards,’’ if available and applicable,
when implementing policies and
programs, unless doing so would be
‘‘inconsistent with applicable law or
otherwise impractical.’’ We have
determined that this regulatory action is
not subject to the requirements of
National Technology Transfer &
Advancement Act of 1995 as this
rulemaking is not setting any technical
standards.
G. Executive Order 13045: Children’s
Health Protection
This rule is not subject to Executive
Order 13045, entitled ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885;
April 23, 1997) because it does not
involve decisions on environmental
health risks or safety risks that may
disproportionately affect children.
H. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255; August 10,
1999), requires the EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by state
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.’’ This
proposed rule does not have federalism
implications. It will not have substantial
direct effects on the states, on the
relationship between the national
government and the states or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. This proposed
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action revises a specific condition of the
Compliance Criteria in 40 CFR part 194.
These criteria are applicable only to the
DOE (operator) and the EPA (regulator)
of the WIPP disposal facility. Thus,
Executive Order 13132 does not apply
to this rule. In the spirit of Executive
Order 13132, and consistent with the
Agency’s policy to promote
communications between the EPA and
state and local governments, the EPA
specifically solicits comment on this
proposed rule from state and local
officials.
Authority: Pub. L. 102–579, 106 Stat. 4777,
as amended by Public Law 104–201, 110 Stat.
2422; Reorganization Plan No. 3 of 1970, 35
FR 15623, Oct. 6, 1970, 5 U.S.C. app. 1;
Atomic Energy Act of 1954, as amended, 42
U.S.C. 2011–2296 and 10101–10270.
I. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
*
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249; November 9, 2000), requires the
EPA to develop an accountable process
to ensure ‘‘meaningful and timely input
by tribal officials in the development of
regulatory policies that have tribal
implications.’’ This proposed rule does
not have tribal implications, as specified
in Executive Order 13175. This
proposed action revises a condition of
the Compliance Criteria in 40 CFR part
194. The Compliance Criteria are
applicable only to Federal agencies.
Thus, Executive Order 13175 does not
apply to this rule. In the spirit of
Executive Order 13175, and consistent
with the EPA policy to promote
consultation and coordination with
Indian Tribal Governments, the Agency
specifically solicits comment on this
proposed rule from Tribal officials.
2. Amend Appendix A to Part 194 by
revising Condition 1: § 194.14(b) to read
as follows:
■
Appendix A to Part 194—Certification
of the Waste Isolation Pilot Plant’s
Compliance With the 40 CFR Part 191
Disposal Regulations and the 40 CFR
Part 194 Compliance Criteria
*
*
*
*
Condition 1: § 194.14(b), Disposal system
design, panel closure system. The
Department shall close filled waste panels in
a manner that has been specifically approved
by the Agency. Any modification to the
approved panel closure design must be
submitted by the DOE as a planned change
request pursuant to § 194.4(b)(3)(i), and
include supporting information required by
§ 194.14, Content of compliance certification
application. The Administrator or
Administrator’s authorized representative
will determine whether the planned change
differs significantly from the design included
in the most recent compliance certification,
and whether the planned change would
require modification of the compliance
criteria. The EPA’s approval of a panel
closure change request requires that
performance assessment calculations
adequately represent the waste panel closure
design, and that those calculations
demonstrate the WIPP’s compliance with the
release standards set by 40 CFR part 191,
Subpart B in accordance with § 194.34,
Results of performance assessments.
*
*
*
*
*
[FR Doc. 2013–28240 Filed 12–2–13; 8:45 am]
BILLING CODE 6560–50–P
J. Executive Order 13211: Energy Effects
This proposed rule is not subject to
Executive Order 13211, ‘‘Actions
Concerning Regulations That
Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355; May
22, 2001) because it is not a significant
regulatory action under Executive Order
12866.
DEPARTMENT OF DEFENSE
GENERAL SERVICES
ADMINISTRATION
NATIONAL AERONAUTICS AND
SPACE ADMINISTRATION
48 CFR Parts 44, 46, and 52
For the reasons set out in the
preamble, 40 CFR part 194 is proposed
to be amended as follows:
emcdonald on DSK67QTVN1PROD with PROPOSALS
Dated: November 18, 2013.
Janet G. McCabe,
Acting Assistant Administrator, Office of Air
and Radiation.
RIN 9000–AM65
PART 194—CRITERIA FOR THE
CERTIFICATION AND
RECERTIFICATION OF THE WASTE
ISOLATION PILOT PLANT’S
COMPLIANCE WITH THE 40 CFR PART
191 DISPOSAL REGULATIONS
1. The authority citation for part 194
continues to read as follows:
■
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[FAR Case 2012–032; Docket No. 2012–
0032; Sequence No. 1]
Federal Acquisition Regulation;
Higher-Level Contract Quality
Requirements
Department of Defense (DoD),
General Services Administration (GSA),
and National Aeronautics and Space
Administration (NASA).
ACTION: Proposed rule.
AGENCY:
DoD, GSA, and NASA are
proposing to amend the Federal
SUMMARY:
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Acquisition Regulation (FAR) to clarify
when to use higher-level quality
standards in solicitations and contracts,
and to update the examples of higherlevel quality standards by revising
obsolete standards and adding two new
industry standards that pertain to
quality assurance for avoidance of
counterfeit items. These standards will
be used to help minimize and mitigate
counterfeit items or suspect counterfeit
items in Government contracting.
DATES: Interested parties should submit
written comments to the Regulatory
Secretariat at one of the addressees
shown below on or before February 3,
2014 to be considered in the formation
of the final rule.
ADDRESSES: Submit comments in
response to FAR Case 2012–032 by any
of the following methods:
• Regulations.gov: https://
www.regulations.gov. Submit comments
via the Federal eRulemaking portal by
searching for ‘‘FAR Case 2012–032.’’
Select the link ‘‘Submit a Comment’’
that corresponds with ‘‘FAR Case 2012–
032.’’ Follow the instructions provided
at the ‘‘Submit a Comment’’ screen.
Please include your name, company
name (if any), and ‘‘FAR Case 2012–
032’’ on your attached document.
• Fax: 202–501–4067.
• Mail: General Services
Administration, Regulatory Secretariat
(MVCB), ATTN: Hada Flowers, 1800 F
Street NW., 2nd Floor, Washington, DC
20405–0001.
Instructions: Please submit comments
only and cite FAR Case 2012–032, in all
correspondence related to this case. All
comments received will be posted
without change to https://
www.regulations.gov, including any
personal and/or business confidential
information provided.
FOR FURTHER INFORMATION CONTACT: Ms.
Marissa Petrusek, Procurement Analyst,
at 202–501–0136, for clarification of
content. For information pertaining to
status or publication schedules, contact
the Regulatory Secretariat at 202–501–
4755. Please cite FAR Case 2012–032.
SUPPLEMENTARY INFORMATION:
I. Background
DoD, GSA, and NASA are proposing
to amend the Federal Acquisition
Regulation (FAR) to revise FAR subpart
46.2, Contract Quality Requirements, to
ensure that agencies assess the risk of
nonconforming items when determining
whether higher-level quality standards
should be used by the Government and
relied on by contractors. These quality
standards must be designated in the
solicitation and resultant contract. The
contractor must also ensure its
E:\FR\FM\03DEP1.SGM
03DEP1
Agencies
[Federal Register Volume 78, Number 232 (Tuesday, December 3, 2013)]
[Proposed Rules]
[Pages 72612-72620]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2013-28240]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 194
[EPA-HQ-OAR-2013-0684; FRL-9903-38-OAR]
Criteria for the Certification and Recertification of the Waste
Isolation Pilot Plant's Compliance With the Disposal Regulations; Panel
Closure Redesign
AGENCY: Environmental Protection Agency.
ACTION: Proposed rule.
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SUMMARY: With this notice, the U.S. Environmental Protection Agency
(EPA, or the Agency) proposes to approve the U.S. Department of
Energy's (DOE, or the Department) planned change request to implement
the Run-of-Mine Panel Closure System (ROMPCS) at the Waste Isolation
Pilot Plant (WIPP) and to amend the WIPP Compliance Criteria to allow
an EPA-approved panel closure other than the currently-required Option
D design. Technical analyses demonstrate that, with the modified panel
closure design, WIPP remains in compliance with the release limits set
by the ``Environmental Standards for the Management and Disposal of
Spent Nuclear Fuel, High-Level and Transuranic (TRU) Radioactive
Waste.'' The proposed changes do not lessen the requirements for
complying with the Compliance Criteria, nor do these changes impact the
technical approach that the EPA will employ when considering any future
planned changes to the panel closure system. Compliance with
environmental or public health regulations other than the EPA's
disposal regulations and WIPP Compliance Criteria is not addressed by
today's action. Today's notice marks the beginning of a 60-day public
comment period on this proposed action.
DATES: Comments must be received on or before February 3, 2014.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-HQ-
OAR-2013-0684, by one of the following methods--
www.regulations.gov: Follow the on-line instructions for
submitting comments.
Email: to a-and-r-docket@epa.gov; Docket ID No. EPA-HQ-
OAR-2013-0684.
Fax: (202) 566-1741.
Mail: Air and Radiation Docket and Information Center,
Environmental Protection Agency, Mail Code: 6102T, 1200 Pennsylvania
Ave. NW., Washington, DC 20460.
Instructions: Direct your comments to Attn: Docket ID No. EPA-HQ-
OAR-2013-0684. The Agency's policy is that all comments received will
be included in the public docket without change and may be made
available online at www.regulations.gov, including any personal
information provided, unless the comment includes information claimed
to be Confidential Business Information (CBI) or other information
whose disclosure is restricted by statute. Do not submit information
that you consider to be CBI or otherwise protected through
www.regulations.gov or email. The www.regulations.gov Web site is an
``anonymous access'' system, which means the EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an email comment directly to the EPA without
going through www.regulations.gov, your email address will be
automatically captured and included as part of the comment that is
placed in the public docket and made available on the Internet. If you
submit an electronic comment, the EPA recommends that you include your
name and other contact information in the body of your comment and with
any disk or CD-ROM you submit. If the EPA cannot read your comment due
to technical difficulties and cannot contact you for clarification, the
Agency may not be able to consider your comment. Electronic files
should avoid the use of special characters or any form of encryption
and be free of any defects or viruses. For additional information about
the EPA's public docket, visit the EPA Docket Center homepage at https://www.epa.gov/epahome/dockets.htm.
Docket: All documents in the docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute.
[[Page 72613]]
Certain other material, such as copyrighted material, will be publicly
available only in hard copy. The EPA has established a docket for this
action under Docket ID No. [EPA-HQ-OAR-2013-0684; FRL-9903-38-OAR].
Publicly available docket materials related to this action (e.g., the
Technical Support document [TSD]) are available either electronically
through www.regulations.gov, on the Agency's WIPP Web site (https://www.epa.gov/radiation/wipp) or in hard copy at the Air and Radiation
Docket in the EPA Docket Center, (EPA/DC) EPA West, Room 3334, 1301
Constitution Ave. NW., Washington, DC 20004. The EPA Docket Center
Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding legal holidays. The telephone number for the Public
Reading Room is (202) 566-1744 and the telephone number for the Air and
Radiation Docket is (202) 566-1742. In accordance with the EPA's
regulations at 40 CFR part 2 and in accordance with normal EPA docket
procedures, if copies of any docket materials are requested, a
reasonable fee may be charged for photocopying.
FOR FURTHER INFORMATION CONTACT: Ray Lee or Jonathan Walsh, Radiation
Protection Division, Mail Code 6608J, U.S. Environmental Protection
Agency, 1200 Pennsylvania Avenue, Washington, DC 20460; telephone
number: 202-343-9463 or 202-343-9238; fax number: 202-343-2305; email
address: lee.raymond@epa.gov or walsh.jonathan@epa.gov.
SUPPLEMENTARY INFORMATION:
Preamble Acronyms and Abbreviations:
Several acronyms and terms used to describe components of the WIPP
disposal system and performance assessment computer models are included
in this preamble. To ease the reading of this preamble and for
reference purposes, the following terms are defined here:
BRAGFLO Computer model used to simulate brine and gas flow
CBFO Carlsbad Field Office
CCA Compliance Certification Application
CCDF Complementary Cumulative Distribution Function
CFR Code of Federal Regulations
DBR Direct Brine Release
DOE U.S. Department of Energy
DRZ Disturbed Rock Zone
EPA U.S. Environmental Protection Agency
FEPs Features, Events and Processes
LWA Land Withdrawal Act
MSHA Mine Safety and Health Administration
NMED New Mexico Environment Department
OPC Ordinary Portland Cement
PA Performance Assessment
PABC Performance Assessment Baseline Calculation
PAVT Performance Assessment Verification Test
PCS Panel Closure System
PCS-2012 Panel Closure System 2012 Performance Assessment
PCR Planned Change Request
PC3R Panel Closure Redesign and Repository Reconfiguration
Performance Assessment
PMR Permit Modification Request
RCRA Resource Conservation and Recovery Act
ROM Run-of-Mine
ROMPC, or
ROMPCS6 Run-of-Mine Salt Panel Closure System
SMC Salado Mass Concrete
SNL Sandia National Laboratories
TRU Transuranic
TSD Technical Support Document
VOC Volatile Organic Compound
WIPP Waste Isolation Pilot Plant
Table of Contents
I. General Information
A. What should I consider as I prepare my comments for the EPA?
II. What is the WIPP?
III. What is the purpose of today's proposed action?
IV. How is the EPA responding to the DOE's planned change request?
A. What are the EPA's requirements for the panel closure design?
B. What changes are proposed to the panel closure design?
C. How has the EPA reached its decision?
V. How is the EPA revising Appendix A, Condition 1?
A. What are the current requirements of Appendix A, Condition 1?
B. What changes are proposed to Appendix A, Condition 1?
C. What did the EPA consider when making its decision?
VI. How has the EPA involved the public?
VII. Administrative Requirements
A. Executive Order 12866
B. Regulatory Flexibility Act
C. Paperwork Reduction Act
D. Unfunded Mandates Reform Act
E. Executive Order 12898
F. National Technology Transfer & Advancement Act of 1995
G. Executive Order 13045: Children's Health Protection
H. Executive Order 13132: Federalism
I. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
J. Executive Order 13211: Energy Effects
I. General Information
A. What should I consider as I prepare my comments for the EPA?
1. Submitting Confidential Business Information (CBI):
Do not submit this information to the EPA through
www.regulations.gov or email. Clearly mark all of the information that
you claim to be CBI. For CBI information in a disk or CD ROM that you
mail to the EPA, mark the outside of the disk or CD ROM as CBI and then
identify electronically within the disk or CD ROM the specific
information that is claimed as CBI. In addition to one complete version
of the comment that includes information claimed as CBI, a copy of the
comment that does not contain the information claimed as CBI must be
submitted for inclusion in the public docket. Information marked as CBI
will not be disclosed except in accordance with procedures set forth in
40 CFR part 2.
2. Tips for Preparing Your Comments:
When submitting comments, remember to--
Identify the rulemaking by docket number, subject heading,
Federal Register date and page number.
Follow directions--the EPA may ask you to respond to
specific questions or organize comments by referencing the chapter
number.
Explain why you agree or disagree; suggest alternatives
and substitute language for your requested changes.
Describe any assumptions and provide any technical
information and/or data that you used.
If you estimate potential costs or burdens, explain how
you arrived at your estimate in sufficient detail to allow it to be
reproduced.
Illustrate your concerns with specific examples and
suggest alternatives.
Explain your views as clearly as possible, avoiding the
use of profanity or personal threats.
Make sure to submit your comments by the comment period
deadline identified.
II. What is the WIPP?
The WIPP is a disposal system for defense-related transuranic (TRU)
radioactive waste. Developed by the DOE, the WIPP is located near
Carlsbad in southeastern New Mexico. At the WIPP, radioactive waste is
disposed of 2,150 feet underground in an ancient formation of salt
which will eventually ``creep'' and encapsulate the waste. The WIPP has
a total capacity of 6.2 million cubic feet of waste.
Congress authorized the development and construction of the WIPP in
1980 ``for the express purpose of providing a research and development
facility to demonstrate the safe disposal of radioactive wastes
resulting from the defense activities and programs of the United
States.'' \1\ Waste which may be
[[Page 72614]]
emplaced in the WIPP is limited to TRU radioactive waste generated by
defense activities associated with nuclear weapons; no high-level waste
or spent nuclear fuel from commercial power plants may be disposed of
at the WIPP. TRU waste is defined as materials containing alpha-
emitting radioisotopes, with half lives greater than twenty years and
atomic numbers above 92, in concentrations greater than 100 nano-curies
per gram of waste.\2\ Most TRU waste proposed for disposal at the WIPP
consists of items that have become contaminated as a result of
activities associated with the production of nuclear weapons (or with
the clean-up of weapons production facilities), e.g., rags, equipment,
tools, protective gear, soil and organic or inorganic sludges. Some TRU
waste is mixed with hazardous chemicals. The waste proposed for
disposal at the WIPP is currently located at federal facilities across
the United States, including locations in California, Idaho, Illinois,
New Mexico, Nevada, Ohio, South Carolina, Tennessee and Washington.
---------------------------------------------------------------------------
\1\ Department of Energy National Security and Military
Applications of Nuclear Energy Authorization Act of 1980, Public Law
96-164, section 213.
\2\ WIPP Land Withdrawal Act, Pub. L. 102-579, section 2(18), as
amended by the 1996 WIPP LWA Amendments, Pub. L. 104-201.
---------------------------------------------------------------------------
The WIPP Land Withdrawal Act (LWA), initially passed by Congress in
1992 and amended in 1996, provides the EPA authority to oversee and
regulate the WIPP. The WIPP LWA delegated to the EPA three main tasks,
to be completed sequentially, for reaching an initial compliance
certification decision. First, the Agency was required to finalize
general regulations which apply to all sites--except Yucca Mountain--
for the disposal of highly radioactive waste.\3\ These disposal
regulations, located at Subparts B and C of 40 CFR part 191, were
originally published in the Federal Register in 1985 and amended in
1993.\4\ Second, the EPA was to develop criteria, by rulemaking, to
implement and interpret the general radioactive waste disposal
regulations specifically for the WIPP. In 1996, the Agency issued the
WIPP Compliance Criteria, which are found at 40 CFR part 194.\5\ The
EPA made changes to the Compliance Criteria via rulemaking in July 2004
(69 FR 42571-42583). These new provisions provide equivalent or
improved oversight and better prioritization of technical issues in EPA
inspections to evaluate waste characterization activities at DOE WIPP
waste generator sites, and offer more direct public input into the
Agency's decisions about what waste can be disposed of at the WIPP.
Third, the EPA was to review the information submitted by the DOE and
publish a certification decision.\6\ The Agency issued its
certification decision on May 18, 1998, as required by Section 8 of the
WIPP LWA (63 FR 27354-27406) determining that the WIPP met the
standards for radioactive waste disposal. The complete record and basis
for the EPA's 1998 certification decision can be found in Air Docket A-
93-02. Condition 1, concerning the panel closure system, was appended
to 40 CFR part 194 as part of the certification decision.
---------------------------------------------------------------------------
\3\ WIPP LWA, section 8(b).
\4\ 50 FR 38066-38089 (September 19, 1985) and 58 FR 66398-66416
(December 20, 1993).
\5\ 61 FR 5224-5245 (February 9, 1996).
\6\ WIPP LWA, section 8(d).
---------------------------------------------------------------------------
Section 8(f) of the WIPP LWA requires that within five years of
initial receipt of waste at the WIPP, and every five years thereafter,
the DOE is to submit to the EPA and the State of New Mexico
documentation of continued compliance with the part 191 radioactive
waste disposal regulations. The Agency recertified the WIPP facility
for the first time on March 29, 2006 (71 FR 18010-18021) and again on
November 18, 2010 (75 FR 70584-70595).
The Department submitted the design of the WIPP repository in
Chapter 3 of the 1996 Compliance Certification Application (CCA). The
EPA's certification is based upon this design. The underground waste
disposal region at WIPP is divided into panels. A panel is a group of
rooms mined into the salt, connected by tunnels called drifts. When all
of the rooms of a panel are filled with waste, the DOE intends to seal
the drifts with engineered structures called panel closures. The EPA
certified the WIPP based on a panel closure design that sealed the
drift using a concrete block wall and a poured concrete monolith. The
DOE proposes to change this design and close the drift using two steel
bulkheads and mined salt. Both panel closure designs are discussed in
detail in Section IV of this document.
III. What is the purpose of today's proposed action?
This action is being taken in response to the DOE's September 2011
Planned Change Request (PCR) to alter the design of the panel closures
used at the WIPP. The WIPP underground waste disposal area is divided
into ten groups of rooms, or panels. A waste panel is a group of mined
rooms connected by drifts that provide both access and ventilation to
the rooms. Following completion of waste disposal activities in each
panel, the DOE intends to seal these drifts with engineered structures
called panel closures. 40 CFR part 194, Criteria for the Certification
and Recertification of the Waste Isolation Pilot Plant's Compliance
with the 40 CFR part 191 Disposal Regulations, did not originally
require panel closures for the purpose of long-term compliance with
release limits for radionuclides. Panel closures have, however, always
been included in the design of the repository, and therefore
incorporated into modeling of the WIPP system as a feature of the
repository.
[[Page 72615]]
[GRAPHIC] [TIFF OMITTED] TP03DE13.010
Although the Agency determined that the DOE met all of the
applicable requirements of the WIPP Compliance Criteria in its
compliance certification decision (63 FR 27354-27406; May 18, 1998),
the EPA amended the WIPP Compliance Criteria, 40 CFR part 194, and
appended four explicit conditions to its certification of compliance to
ensure that the measures actually implemented at the WIPP (and thus the
circumstances expected to exist there) were consistent with the DOE's
Compliance Certification Application (CCA) and with the basis for the
EPA's compliance certification. Condition 1 of the certification
applies to the panel closure system.\7\ In the CCA, the Department
presented four options for the design of the panel closure system, but
did not specify which would be constructed at the WIPP facility. The
Agency based its certification decision on the DOE's use of the most
robust design, referred to in the CCA as ``Option D''.
---------------------------------------------------------------------------
\7\ Conditions 2 and 3 of the final certification decision apply
to activities conducted at waste generator sites that produce TRU
waste proposed for disposal at WIPP (Sec. Sec. 194.22 and 194.24),
and Condition 4 of the certification applies to passive
institutional controls (PICs), records and physical markers to warn
future societies about the location and contents of the disposal
system and thus to deter inadvertent intrusion into the WIPP (Sec.
194.43).
---------------------------------------------------------------------------
At the time of the 1998 certification decision, there were
indications that the DOE would seek to change the design of the panel
closure system selected by the EPA. As stated in the original
certification:
Nothing in this condition precludes DOE from reassessing the
engineering of the panel seals at any time. Should DOE determine at
any time that improvements in materials or construction techniques
warrant changes to the panel seal design, DOE must inform EPA. If
EPA concurs, and determines that such changes constitute a
significant departure from the design on which certification is
based, the Agency is authorized under Sec. 194.65 to initiate a
rulemaking to appropriately modify the certification.'' (63 FR
27354, 27362; May 18, 1998.)
In 2002, the Agency approved the DOE's request to install only the
explosion wall, and to extend the panel closure installation schedule
until a new design is approved. In January 2007, the DOE requested that
installation of the explosion walls also be delayed until a new design
could be approved, and proposed to monitor gas generation in Panels 3
and 4 of the repository. The EPA approved this request in February
2007. Today's action represents the first time that the Agency has
considered an alteration to the panel closure design itself.
The Department submitted a PCR to the EPA on September 28, 2011.
Citing
[[Page 72616]]
experience and data gained since the CCA, the DOE's PCR states that the
Option D panel closure would be extremely difficult and costly to
install, and that the highly engineered design is unnecessary for
either worker safety or environmental protection during the operational
period. The DOE instead proposed a new panel closure design, the Run-
of-Mine Salt Panel Closure System (ROMPCS), which consists of mined
salt emplaced between steel bulkheads.
The EPA has completed its technical review of the DOE's PCR and
supporting documentation. The goal of the Agency's technical review
process was to determine whether, with the new design, the WIPP
adequately demonstrates compliance with the requirements of 40 CFR part
194 and the release limits of 40 CFR part 191 Subparts B and C. The
process the EPA applied to support this proposed action entailed (1) a
review of all materials submitted by the DOE, (2) requests for
additional information including a full performance assessment, and (3)
the independent performance of additional confirmatory calculations by
the Agency. This process is fully documented in the EPA's TSD, ``Review
of the DOE's Planned Change Request to Modify the WIPP Panel Closure
System,'' (EPA-HQ-OAR-2013-0684-0002) and discussed in the following
sections. Based on this process, the Agency concludes that the WIPP
will remain in compliance with its release limits with the ROMPCS
design. The Agency therefore proposes to approve the DOE's PCR to
implement the redesigned panel closure at the WIPP, and to modify 40
CFR part 194 Appendix A, Condition 1 to allow a panel closure design
other than Option D. Section IV, below, discusses the Agency's
consideration of the proposed panel closure modification. Section V
describes the Agency's approach to modifying Condition 1.
IV. How is the EPA responding to the DOE's planned change request?
A. What are the EPA's requirements for the panel closure design?
During the operational period of the repository, the panel closure
system was intended to prevent access to closed waste panels, to
mitigate the release of volatile organic compounds (VOCs) and to
protect site workers from a hypothetical methane or hydrogen explosion
inside a filled waste panel. These functions are addressed by the New
Mexico Environment Department (NMED), and DOE has submitted a separate
Resource Conservation and Recovery Act (RCRA) Permit Modification
Request (PMR) stating that the new panel closure design will adequately
protect workers and the public during the operational period of the
WIPP.
The EPA's Compliance Criteria at 40 CFR part 194 originally did not
require a panel closure of any kind to be installed in the repository
for the purpose of long-term compliance with release limits for
radionuclides. The purpose of 40 CFR part 194 is to demonstrate
compliance with the disposal regulations at 40 CFR part 191 for
containment of radionuclides. The containment requirements at 40 CFR
191.13 specify that releases of radionuclides to the accessible
environment must be unlikely to exceed specific release limits for
10,000 years after disposal, based on the amount of waste in the
repository at the time of closure (Sec. 194.31). Assessment of the
likelihood that the WIPP will not exceed release limits is accomplished
through a process called performance assessment, or PA. The WIPP PA
process culminates in a series of computer simulations that model the
physical attributes of the disposal system (e.g., site characteristics,
waste forms and quantities, engineered features) in a manner that
captures the behaviors and interactions among its various components.
The computer simulations require the development of conceptual models
that represent physical attributes of the repository based on features,
events and processes (FEPs) that may impact the disposal system. The
conceptual models are then expressed as mathematical relationships,
which are solved with iterative numerical models, which are then
translated into computer codes (Sec. 194.23). Numerous simulations are
performed using sampled values for material properties and processes
whose values are uncertain. The results of the simulations are intended
to calculate possible releases of radioactive materials from the
disposal system to the accessible environment over the 10,000-year
regulatory period, and are used to demonstrate compliance with the
containment requirements in 40 CFR 191.13. Because the radionuclide
release limits are based on the amount of waste in the repository at
the time of closure, the containment requirements are expressed in
terms of ``normalized releases.'' The results of the PA are assembled
into complementary cumulative distribution functions (CCDFs), which
indicate the probability of exceeding various levels of normalized
releases (Sec. 194.34).
At the time of the CCA, given limited information on how the
different panel closure designs could influence performance, the Agency
contended that the panel closures constructed in the repository should
have physical properties similar to those that had been used to
represent them in the compliant performance assessment. As stated in
the WIPP certification:
EPA based its certification decision on DOE's use of the most robust
design (referred to in the CCA as ``Option D''). The Agency found
the Option D design to be adequate, but also determined that the use
of Salado mass concrete--using brine rather than fresh water--would
produce concrete seal permeabilities in the repository more
consistent with the values used in DOE's performance assessment.
Therefore, Condition 1 of EPA's certification requires DOE to
implement the Option D panel closure system at WIPP, with Salado
mass concrete replacing fresh water concrete. (63 FR 27355)
Because the Agency based its certification of the WIPP's compliance
with the disposal regulations on the accurate representation of the
repository in performance assessment, Condition 1 was appended to 40
CFR Part 194 during the certification of the WIPP. No other design
feature of the repository is required by the Compliance Criteria in a
similarly explicit way.
B. What changes are proposed to the panel closure design?
The Option D panel closure design consists of a 12-foot thick
``explosion-isolation wall'' constructed of solid concrete blocks
filling the drift on the waste disposal side, a short section of open
drift called an ``isolation zone'' and a monolithic concrete barrier on
the side of the open drift. Fractured rock in the immediate vicinity of
the drift--called the disturbed rock zone, or DRZ--would be removed,
and the resulting void space filled by the concrete monolith. In its
current PCR, the DOE states that ``large scale testing has demonstrated
that using SMC [Salado Mass Concrete] cannot meet the design and
performance requirements for the panel closures as specified in the
CCA.'' Even if the Option D monolith could be constructed as planned,
the Agency acknowledges that it would be installed at significant cost
to the Department, that additional occupational hazards would be
incurred by moving and pouring large amounts of concrete in the
underground and that disposal operations would be significantly
disrupted.
The DOE's new panel closure design, the ROMPCS, consists primarily
of run-of-mine (ROM) salt--impure halite that
[[Page 72617]]
has been mined in the course of normal repository operations and not
subjected to additional processing or grading. The ROMPCS design
consists of two standard steel ventilation bulkheads with a minimum of
100 feet of run-of-mine (ROM) salt between them, filling the drift from
floor to ceiling. In Panels 1, 2 and 5, where explosion walls have
already been constructed, salt will be placed directly against the
explosion wall and a standard steel ventilation bulkhead placed on the
outer end of the panel closure. The DOE has stated that the ROMPCS will
provide adequate protection during the operational period. Upon initial
emplacement, the run-of-mine salt will exhibit the properties of a
loosely consolidated or unconsolidated material. Over time, as the open
areas of the repository close due to salt creep, the panel closures
will consolidate and eventually heal to a state resembling intact salt.
The EPA's technical review process is summarized below in Section
C. Based on the results of performance assessment, the Agency concludes
that the WIPP will continue to comply with the EPA's disposal standards
with the ROMPCS. Therefore, the Agency proposes to approve the DOE's
PCR and allow the implementation of the ROMPCS design at the WIPP.
C. How has the EPA reached its decision?
As in the past, the Agency's consideration of the panel closure
system focused on its inclusion and accurate representation in
repository performance assessment, so that the EPA can ultimately
certify the WIPP's ability to meet long-term performance standards.
In support of its panel closure PCR, the DOE initially submitted a
performance assessment calculation called the Panel Closure Redesign
and Repository Reconfiguration (PC3R) PA, which incorporated multiple
planned changes. The Agency determined that to approve the PCR, it was
necessary to isolate the impacts, if any, of the change in panel
closure design. In response, the DOE prepared the PCS-2012 PA, with the
explicit goal of changing only those aspects of the current baseline PA
that are directly related to the change in the panel closure design.
Thus, results of the PCS-2012 PA may be directly compared to results of
the current Performance Assessment Baseline Calculation (PABC-09) to
see the impact of changes in the panel closure on modeled releases from
the facility.
The majority of the technical effort expended by the Agency was
spent determining how the changes in the panel closures should be
represented in the performance assessment models. This review process
involved interactions with the DOE and DOE contractor staff and is
documented in the Agency's TSD, ``Review of DOE's Planned Change
Request to Modify the WIPP Panel Closure System.'' (EPA-HQ-OAR-2013-
0684-0002) The process began by identifying the universe of changes
which might have taken place within the performance assessment. The
conclusion of the features, events and processes (FEPs) review found
that the required changes to the models were limited to the properties
of the panel closure and of the disturbed rock zone immediately
surrounding it. In performance assessment, these materials are
represented in the BRAGFLO computer model, which simulates the flow of
brine and gas in the repository over the 10,000-year period of
performance. Some modeling changes, such as differences between the
physical dimensions of the panel closure designs, were relatively
simple for the DOE to implement. The most significant change between
panel closure designs, and the greatest modeling challenge, was the
dynamic nature of the ROMPCS's material properties. The Option D design
called for the excavation of the DRZ, and the installation of a rigid
concrete monolith which would effectively prevent further fracturing.
Thus, the properties of the panel closure and surrounding DRZ were not
expected to change significantly over time, and were represented in PA
by constant values. The ROMPCS will be emplaced in a loose form,
surrounded by a fractured DRZ. As the panel closure system consolidates
due to repository creep closure, it will decrease in porosity, and its
permeability to fluids will decrease. Based on measurements taken in
the underground, laboratory data and geomechanical modeling, it is
expected that this consolidation process will be complete approximately
200 years after the closure of the repository.
The DOE represents the ROMPCS using three time periods. Two time
periods of one hundred years each are used to represent the gradual
reconsolidation of the panel closure system. A third time period,
extending from 200 years after closure to the end of the 10,000-year
performance period, represents the final healed state of the PCS. The
consolidation of the ROMPC is modeled by sampling its porosity from a
range of possible values for each time period. The permeability of the
panel closure to fluids during each time period is then calculated
using a correlation between the porosity and permeability of salt,
developed by the DOE using existing experimental data. The DRZ
surrounding the panel closure is modeled so that it is more permeable
to fluids during the first 200 years after closure, and less permeable
when the system has reached a steady state. Parameter values
representing other material properties of the ROM salt were directly
adopted from parameters that were developed during the CCA to describe
the crushed salt component of the shaft seals. The parameters used to
represent the changes in performance assessment were finalized by the
DOE in a memorandum dated May 3, 2012.
After the EPA's concurrence with the representation of the panel
closure, the DOE executed the PCS-2012 PA calculation. Results of the
PCS-2012 PA are discussed in detail in TSD Section 4.5. Compared to the
PABC-2009 baseline, calculated mean total releases from the PCS-2012 PA
did not appreciably increase at a probability of 0.1, and increased at
a probability of 0.001, from 1.1 to 1.51 EPA units. (See TSD, EPA-HQ-
OAR-2013-0684-0002, Table 3.7.) Thus, the mean total release, as well
as the 90th percentile and upper 95% confidence limit of the mean, fell
significantly below the Agency's regulatory limits of 1 EPA unit for a
probability of 0.1, and 10 EPA units for a probability of 0.001.
Modeled releases from the repository principally result from the
penetration of the repository waste by a hypothetical oil or gas
borehole. Specific release mechanisms include cuttings and cavings
releases, direct brine releases (DBRs), spallings releases and releases
up a borehole to the Culebra dolomite. The increase in calculated
releases in the PCS-2012 PA is primarily due to increases in direct
brine releases, resulting from changes in pressure and brine saturation
in the waste panels (See TSD, EPA-HQ-OAR-2013-0684-0002, Section 3.5).
Compared to the Option D PCS design, the ROMPCS is expected to be more
permeable to fluids upon installation, and less permeable after it has
consolidated. The initial conditions of the WIPP model make a
significant amount of brine available in the repository at the time of
closure. The higher initial permeability of the ROMPCS allows early-
time brine inflows into the waste panels, resulting in generally higher
brine saturations and higher rates of gas generation in the modeled
waste panel. When the permeability of the panel closures decreases
after 200 years, both brine and gas can be retained in the panel,
increasing the brine saturations and gas pressures encountered by
borehole
[[Page 72618]]
penetrations of the repository. Those increases in turn result in
increases in mean DBR and spallings releases. Cuttings and cavings are
important contributors to total releases, but are not affected by waste
panel pressure and brine saturation. Releases through the Culebra are
essentially unchanged from those calculated using the Option D design.
The EPA considers this analysis important to its understanding of
the disposal system. The Agency concludes that the changes to the panel
closure system do not have a significant impact on the long-term
performance of the disposal system.
V. How is the EPA revising Appendix A, Condition 1?
A. What are the current requirements of Appendix A, Condition 1?
The Option D panel closure is currently required by 40 CFR part
194, Appendix A, Condition 1.
As described in Section III, the EPA certified the WIPP's
performance based on the properties of the Option D panel closure. It
is the only engineered aspect of the repository design that is
explicitly required by rule.
B. What changes are proposed for Appendix A, Condition 1?
As described above in Section IV, the EPA is proposing to accept a
redesigned panel closure. Acceptance of the PCR requires modification
of Condition 1. The Agency does not believe that the design must be
specified by the condition, because there is no evidence to suggest
that the panel closure has a disproportionate ability to impact long-
term performance when compared to other design features of the
repository. This change does not grant the DOE the ability to alter the
panel closure design at will. As with any engineered component of the
disposal system, a departure from the current, approved design must be
submitted to the Agency as a planned change request as required by
Sec. 194.4(b)(3)(i). The EPA would expect any such request to be
supported by complete technical documentation, including information
concerning ``the geology, hydrology, hydrogeology, and geochemistry of
the WIPP disposal system'' and ``WIPP materials of construction,
standards applied to design and construction,'' as required by Sec.
194.14, Content of certification applications. The Agency would use
this information to determine whether or not the WIPP remains in
compliance with the disposal standards. As with any other planned
change, based on the potential impact to the WIPP's compliance, the EPA
will determine whether the change ``departs significantly from the most
recent compliance application,'' and must be addressed by rule in
accordance with Sec. 194.65.
C. What did the EPA consider when making its decision?
In 1998, the EPA certified the WIPP conditionally based on the
Option D panel closure design. At that time, the DOE had not specified
which design it planned to implement, and limited performance
assessment results were available to indicate the impact of the panel
closure design on repository performance. In contrast, the Department
has now proposed a single panel closure design to be installed in all
waste panels. Due to the evolution of the WIPP PA since the CCA, the
DOE and the EPA have gained a greater understanding of panel closures'
influence on PA results.
The Agency initially chose the Option D panel closure partly to
match the physical properties of the panel closure to the modeled
parameters of the generic panel closure represented in the CCA. This
representation of the panel closure was refined in the 2002 Technical
Baseline Migration PA to reflect the dimensions of the Option D design
and include impacts of a rigid structure on the surrounding DRZ. These
changes did not result in a significant impact on predicted releases,
and were included in PAs which supported both WIPP recertifications.
The changes made in the PCS-2012 PA altered the panel closure
properties substantially, without significantly affecting the WIPP's
ability to comply with the release limits. The DOE's sensitivity
analysis indicates that several sampled parameters related to the panel
closures contributed to the overall results, but their contributions
were dwarfed by the effect of other parameters, such as the waste shear
strength and actinide solubility. Additionally, the Agency carried out
confirmatory studies as part of its technical review which analyzed how
different representations of the DRZ surrounding the panel closure
could potentially influence modeled results.
The conclusion that the Agency draws from all of these studies is
that although the panel closures can influence modeled results to a
degree, there is no evidence that modifications to the panel closure or
its representation in PA could jeopardize the WIPP's ability to comply
with the disposal requirements. Because panel closures do not exercise
a disproportionate impact on the WIPP's ability to isolate
radionuclides from the accessible environment, the EPA does not believe
that it is necessary for the specific design of the panel closure to
remain as a condition of certification. Rather, panel closures can be
treated in a similar manner as any other engineered feature of the
repository. As described in Section IV, the DOE must still submit a PCR
if it wishes to alter the design from the approved ROMPCS.
VI. How has the EPA involved the public?
In order to guide its technical process, the EPA held informal
public meetings in Carlsbad, New Mexico, on December 5, 2012, and Santa
Fe, New Mexico, on December 6, 2012. The purpose of these meetings was
to provide the public with background on the DOE's panel closure system
planned change request, and to give the public the opportunity to raise
any technical issues that the Agency should consider in its decision.
At both meetings, many comments were in favor of approving the panel
closure planned change request based on its scientific and economic
merits. Specifically, commenters expressed confidence in the ability of
salt creep to compress the ROMPCS and form an adequate panel closure,
and emphasized the greater operational safety when installing the
revised design. In Santa Fe, one commenter expressed the view that the
lack of a cost analysis for building the Option D panel closures, and
the failure to explicitly consider other designs are deficiencies in
the PCR. Other commenters asked questions regarding the likelihood of
gas generation and explosions in the closed panels. No technical
comments were submitted.
Additional public meetings will be held in Carlsbad and Albuquerque
in December 2013. Details and summaries of these meetings will be
published on the EPA's WIPP Web site at https://www.epa.gov/radiation/wipp.
VII. Administrative Requirements
A. Executive Order 12866
Under Executive Order 12866, (58 FR 51735; October 4, 1993), the
Agency must determine whether the regulatory action is ``significant''
and therefore subject to OMB review and the requirements of the
Executive Order. The Order defines ``significant regulatory action'' as
one that is likely to result in a rule that may: (1) Have an annual
effect on the economy of $100 million or more or adversely affect in a
material way the economy, a sector of the economy, productivity,
competition, jobs, the environment, public health or safety, or state,
local, or tribal governments or communities; (2) create
[[Page 72619]]
a serious inconsistency or otherwise interfere with an action taken or
planned by another Agency; (3) materially alter the budgetary impact of
entitlements, grants, user fees or loan programs or the rights and
obligations of recipients thereof; or (4) raise novel legal or policy
issues arising out of legal mandates, the President's priorities or the
principles set forth in the Executive Order. Pursuant to the terms of
Executive Order 12866, it has been determined that this rule is not a
``significant regulatory action.''
B. Regulatory Flexibility Act
The Regulatory Flexibility Act (``RFA'') generally requires any
federal agency to conduct a regulatory flexibility analysis of any rule
subject to notice and comment rulemaking requirements unless they
certify that the rule will not have a significant economic impact on a
substantial number of small entities. Small entities include small
businesses, small not-for-profit enterprises and small governmental
jurisdictions. This proposed rule will not have a significant impact on
a substantial number of small entities because it sets forth
requirements which apply only to federal agencies. Therefore, this
action will not have a significant economic impact on a substantial
number of small entities.
C. Paperwork Reduction Act
This proposed action does not impose an information collection
burden under the provisions of the Paper Reduction Act, 44 U.S.C. 3501
et seq. The Compliance Criteria in 40 CFR part 194 requirements are
applicable only to the DOE and the EPA and do not establish any form of
collection of information from the public.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates Reform Act of 1995 (``UMRA''),
Public Law 104-4, establishes requirements for federal agencies to
assess the effects of their regulatory actions on state, local and
tribal governments and the private sector. Pursuant to Title II of the
UMRA, we have determined that this regulatory action is not subject to
the requirements of sections 202 and 205, because this action does not
contain any ``federal mandates'' for state, local or tribal governments
or for the private sector. This rule applies only to federal agencies.
E. Executive Order 12898
Pursuant to Executive Order 12898 (59 FR 7629; February 16, 1994),
entitled ``Federal Actions to Address Environmental Justice in Minority
Populations and Low-Income Populations,'' the Agency has considered
environmental justice related issues with regard to the potential
impacts of this action on the environmental and health conditions in
low-income, minority and Native-American communities. We have complied
with this mandate. However, the requirements specifically set forth by
the Congress in the Waste Isolation Pilot Plant Land Withdrawal Act
(Pub. L. 102-579), which prescribes the EPA's role at the WIPP, did not
provide authority for the Agency to examine impacts in the communities
in which wastes are produced, stored and transported, and Congress did
not delegate to the EPA the authority to consider the issue of
alternative locations for the WIPP. During the development of the
existing provisions in 40 CFR part 194, the EPA involved minority and
low income populations early in the rulemaking process. In 1993, the
EPA representatives met with New Mexico residents and government
officials to identify the key issues that concern them, the types of
information they wanted from the Agency and the best ways to
communicate with different sectors of the New Mexico public. The
feedback provided by this group of citizens formed the basis for the
EPA's WIPP communications and consultation plan. To help citizens
(including a significant Hispanic population in Carlsbad and the nearby
Mescalero Indian Reservation) stay abreast of the EPA's WIPP-related
activities, the Agency developed many informational products and
services. The EPA translated several documents regarding WIPP into
Spanish, including educational materials and fact sheets describing the
EPA's WIPP oversight role and the radioactive waste disposal standards.
The Agency established a toll-free WIPP Information Line, recorded in
both English and Spanish, providing the latest information on upcoming
public meetings, publications and other WIPP-related activities. The
EPA also developed a mailing list, which includes many low-income,
minority and Native-American groups, to systematically provide
interested parties with copies of EPA's public information documents
and other materials. Even after the final rule, in 1998, the EPA has
continued to implement outreach services to all WIPP communities based
on the needs determined during the certification. The Agency has
established a WIPP-NEWS email listserv to facilitate communications
with interested stakeholders not only in New Mexico and surrounding
areas, but nationally and internationally as well. The EPA's WIPP Web
site is also continuously updated with relevant news and updates on
current and future WIPP activities.
F. National Technology Transfer & Advancement Act of 1995
Section 12 of the National Technology Transfer & Advancement Act of
1995 is intended to avoid ``re-inventing the wheel.'' It aims to reduce
costs to the private and public sectors by requiring federal agencies
to draw upon any existing, suitable technical standards used in
commerce or industry. To comply with the Act, the EPA must consider and
use ``voluntary consensus standards,'' if available and applicable,
when implementing policies and programs, unless doing so would be
``inconsistent with applicable law or otherwise impractical.'' We have
determined that this regulatory action is not subject to the
requirements of National Technology Transfer & Advancement Act of 1995
as this rulemaking is not setting any technical standards.
G. Executive Order 13045: Children's Health Protection
This rule is not subject to Executive Order 13045, entitled
``Protection of Children from Environmental Health Risks and Safety
Risks'' (62 FR 19885; April 23, 1997) because it does not involve
decisions on environmental health risks or safety risks that may
disproportionately affect children.
H. Executive Order 13132: Federalism
Executive Order 13132, entitled ``Federalism'' (64 FR 43255; August
10, 1999), requires the EPA to develop an accountable process to ensure
``meaningful and timely input by state and local officials in the
development of regulatory policies that have federalism implications.''
``Policies that have federalism implications'' is defined in the
Executive Order to include regulations that have ``substantial direct
effects on the States, on the relationship between the national
government and the States, or on the distribution of power and
responsibilities among the various levels of government.'' This
proposed rule does not have federalism implications. It will not have
substantial direct effects on the states, on the relationship between
the national government and the states or on the distribution of power
and responsibilities among the various levels of government, as
specified in Executive Order 13132. This proposed
[[Page 72620]]
action revises a specific condition of the Compliance Criteria in 40
CFR part 194. These criteria are applicable only to the DOE (operator)
and the EPA (regulator) of the WIPP disposal facility. Thus, Executive
Order 13132 does not apply to this rule. In the spirit of Executive
Order 13132, and consistent with the Agency's policy to promote
communications between the EPA and state and local governments, the EPA
specifically solicits comment on this proposed rule from state and
local officials.
I. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
Executive Order 13175, entitled ``Consultation and Coordination
with Indian Tribal Governments'' (65 FR 67249; November 9, 2000),
requires the EPA to develop an accountable process to ensure
``meaningful and timely input by tribal officials in the development of
regulatory policies that have tribal implications.'' This proposed rule
does not have tribal implications, as specified in Executive Order
13175. This proposed action revises a condition of the Compliance
Criteria in 40 CFR part 194. The Compliance Criteria are applicable
only to Federal agencies. Thus, Executive Order 13175 does not apply to
this rule. In the spirit of Executive Order 13175, and consistent with
the EPA policy to promote consultation and coordination with Indian
Tribal Governments, the Agency specifically solicits comment on this
proposed rule from Tribal officials.
J. Executive Order 13211: Energy Effects
This proposed rule is not subject to Executive Order 13211,
``Actions Concerning Regulations That Significantly Affect Energy
Supply, Distribution, or Use'' (66 FR 28355; May 22, 2001) because it
is not a significant regulatory action under Executive Order 12866.
Dated: November 18, 2013.
Janet G. McCabe,
Acting Assistant Administrator, Office of Air and Radiation.
For the reasons set out in the preamble, 40 CFR part 194 is
proposed to be amended as follows:
PART 194--CRITERIA FOR THE CERTIFICATION AND RECERTIFICATION OF THE
WASTE ISOLATION PILOT PLANT'S COMPLIANCE WITH THE 40 CFR PART 191
DISPOSAL REGULATIONS
0
1. The authority citation for part 194 continues to read as follows:
Authority: Pub. L. 102-579, 106 Stat. 4777, as amended by Public
Law 104-201, 110 Stat. 2422; Reorganization Plan No. 3 of 1970, 35
FR 15623, Oct. 6, 1970, 5 U.S.C. app. 1; Atomic Energy Act of 1954,
as amended, 42 U.S.C. 2011-2296 and 10101-10270.
0
2. Amend Appendix A to Part 194 by revising Condition 1: Sec.
194.14(b) to read as follows:
Appendix A to Part 194--Certification of the Waste Isolation Pilot
Plant's Compliance With the 40 CFR Part 191 Disposal Regulations and
the 40 CFR Part 194 Compliance Criteria
* * * * *
Condition 1: Sec. 194.14(b), Disposal system design, panel
closure system. The Department shall close filled waste panels in a
manner that has been specifically approved by the Agency. Any
modification to the approved panel closure design must be submitted
by the DOE as a planned change request pursuant to Sec.
194.4(b)(3)(i), and include supporting information required by Sec.
194.14, Content of compliance certification application. The
Administrator or Administrator's authorized representative will
determine whether the planned change differs significantly from the
design included in the most recent compliance certification, and
whether the planned change would require modification of the
compliance criteria. The EPA's approval of a panel closure change
request requires that performance assessment calculations adequately
represent the waste panel closure design, and that those
calculations demonstrate the WIPP's compliance with the release
standards set by 40 CFR part 191, Subpart B in accordance with Sec.
194.34, Results of performance assessments.
* * * * *
[FR Doc. 2013-28240 Filed 12-2-13; 8:45 am]
BILLING CODE 6560-50-P