Rule To Reduce Interstate Transport of Fine Particulate Matter and Ozone (Clean Air Interstate Rule): Reconsideration, 72268-72282 [05-23501]
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Federal Register / Vol. 70, No. 231 / Friday, December 2, 2005 / Proposed Rules
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(f) Effective date. The mortality tables
described in this section apply for plan
years beginning on or after January 1,
2007.
ENVIRONMENTAL PROTECTION
AGENCY
Age
Mark E. Matthews,
Deputy Commissioner for Services and
Enforcement.
[FR Doc. E5–6742 Filed 12–1–05; 8:45 am]
BILLING CODE 4830–01–P
40 CFR Parts 51 and 96
[OAR 2003–0053; FRL–8003–7]
Rule To Reduce Interstate Transport of
Fine Particulate Matter and Ozone
(Clean Air Interstate Rule):
Reconsideration
Environmental Protection
Agency (EPA).
AGENCY:
VerDate Aug<31>2005
14:49 Dec 01, 2005
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Notice of reconsideration;
request for comment; notice of public
hearing.
ACTION:
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SUMMARY: On May 12, 2005, EPA
published in the Federal Register the
final ‘‘Rule to Reduce Interstate
Transport of Fine Particulate Matter and
Ozone’’ (Clean Air Interstate Rule or
CAIR). The CAIR requires certain
upwind States to reduce emissions of
nitrogen oxides (NOX) and/or sulfur
dioxide (SO2) that significantly
contribute to nonattainment of, or
interfere with maintenance by,
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Federal Register / Vol. 70, No. 231 / Friday, December 2, 2005 / Proposed Rules
downwind States with respect to the
fine particle and/or 8-hour ozone
national ambient air quality standards
(NAAQS). Subsequently, EPA received
11 petitions for reconsideration of the
final rule. In this notice, EPA is
announcing its decision to reconsider
four specific issues in the CAIR and is
requesting comment on those issues.
The EPA is seeking comment only on
the aspects of the CAIR specifically
identified in this notice. We will not
respond to comments addressing other
provisions of the CAIR or any related
rulemakings.
Comments must be received on
or before January 13, 2006. A public
hearing will be held on December 14,
2005 in Washington, DC. For additional
information on the public hearing, see
the SUPPLEMENTARY INFORMATION section
of this preamble.
ADDRESSES: Submit your comments,
identified by Docket ID No. OAR–2003–
0053, by one of the following methods:
• Federal Rulemaking Portal: https://
www.regulations.gov. Follow the on-line
instructions for submitting comments.
Attention E-Docket No. OAR–2003–
0053.
• Agency Web site: https://
www.epa.gov/edocket. EDOCKET, EPA’s
electronic public docket and comment
system, is EPA’s preferred method for
receiving comments. Follow the on-line
instructions for submitting comments.
Attention E-Docket No. OAR–2003–
0053.
• E-mail: A-and-R-Docket@epa.gov.
Attention E-Docket No. OAR–2003–
0053.
• Fax: The fax number of the Air
Docket is (202) 566–1741. Attention EDocket No. OAR–2003–0053.
• Mail: EPA Docket Center, EPA West
(Air Docket), Attention E-Docket No.
OAR–2003–0053, Environmental
Protection Agency, Mail Code: 6102T,
1200 Pennsylvania Ave., NW.,
Washington, DC 20460.
• Hand Delivery: EPA Docket Center
(Air Docket), Attention E-Docket No.
OAR–2003–0053, Environmental
Protection Agency, 1301 Constitution
Avenue, NW., Room B102, Washington,
DC. Such deliveries are only accepted
during the Docket’s normal hours of
operation, and special arrangements
should be made for deliveries of boxed
information.
Instructions: Direct your comments to
Docket ID No. OAR–2003–0053. The
EPA’s policy is that all comments
received will be included in the public
docket without change and may be
made available on-line at https://
www.epa.gov/edocket, including any
personal information provided, unless
DATES:
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14:49 Dec 01, 2005
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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 EDOCKET,
regulations.gov, or e-mail. (For
instructions on submitting CBI, see
below under SUPPLEMENTARY
INFORMATION.)
The EPA EDOCKET and the Federal
regulations.gov Web sites are
‘‘anonymous access’’ systems, which
means EPA will not know your identity
or contact information unless you
provide it in the body of your comment.
If you send an e-mail comment directly
to EPA without going through
EDOCKET or 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, 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 EPA cannot read your
comment due to technical difficulties
and cannot contact you for clarification,
EPA may not be able to consider your
comment. Electronic files should avoid
the use of special characters, any form
of encryption, and be free of any defects
or viruses. For additional information
about EPA’s public docket visit
EDOCKET on-line or see the Federal
Register of May 31, 2002 (67 FR 38102).
For additional information on
submitting comments, go to the
SUPPLEMENTARY INFORMATION section of
this document.
Docket: All documents in the docket
are listed in the EDOCKET index at
https://www.epa.gov/edocket. Although
listed in the index, some information is
not publicly available, i.e., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
is not placed on the Internet and will be
publicly available only in hard copy
form. Publicly available docket
materials are available either
electronically in EDOCKET or in hard
copy at the EPA Docket Center (Air
Docket), EPA/DC, EPA West, Room
B102, 1301 Constitution Ave., NW.,
Washington, DC. The 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)
566–1742 and the fax number is (202)
566–1741.
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72269
For
general questions concerning today’s
action, please contact Carla Oldham,
U.S. EPA, Office of Air Quality Planning
and Standards, Air Quality Strategies
and Standards Division, Mail Code
C539–02, Research Triangle Park, NC
27711, phone number (919) 541–3347,
e-mail addressoldham.carla@epa.gov.
For questions concerning the analyses
described in section III of this notice,
please contact Chitra Kumar, U.S. EPA,
Office of Atmospheric Programs, Clean
Air Markets Division, Mail Code 6204J,
1200 Pennsylvania Avenue, NW.,
Washington, DC 20460, telephone (202)
343–9128, e-mail address
kumar.chitra@epa.gov. For legal
questions, please contact Sonja Rodman,
U.S. EPA, Office of General Counsel,
Mail Code 2344A, 1200 Pennsylvania
Avenue, NW., Washington, DC 20460,
telephone 202–564–4079, e-mail
address rodman.sonja@epa.gov.
For information concerning the public
hearing, please contact Jo Ann Allman,
U.S. EPA, Office of Air Quality Planning
and Standards, Air Quality Strategies
and Standards Division, Mail Code
C539–02, Research Triangle Park, NC
27711, phone number (919) 541–1815,
e-mail address allman.joann@epa.gov.
SUPPLEMENTARY INFORMATION:
FOR FURTHER INFORMATION CONTACT:
Does This Action Apply to Me?
The CAIR does not directly regulate
emissions sources. Instead, it requires
States to develop, adopt, and submit SIP
revisions that would achieve the
necessary SO2 and NOX emissions
reductions, and leaves to the States the
task of determining how to obtain those
reductions, including which entities to
regulate.
Public Hearing. On December 14,
2005, EPA will hold a public hearing on
today’s notice at EPA Headquarters,
1310 L Street (closest cross street is 13th
Street), 1st floor conference rooms 152
and 154, Washington, DC. The closest
Metro stop is McPherson Square
(Orange and Blue lines)—take 14th
Street/Franklin Square Exit. Because the
hearing will be held at a U.S.
government facility, everyone planning
to attend should be prepared to show
valid picture identification to the
security staff in order to gain access to
the meeting room.
The hearing will begin at 9 a.m. and
end at 12 noon. Persons wishing to
speak at the public hearing should
contact Jo Ann Allman by December 9
at telephone number (919) 541–1815 or
by e-mail at allman.joann@epa.gov. The
hearing will be limited to the subject
matter of this document. Oral testimony
will be limited to 5 minutes. The EPA
encourages commenters to provide
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written versions of their oral testimonies
either electronically (on computer disk
or CD–ROM) or in paper copy. The
public hearing schedule, including the
list of speakers, will be posted on EPA’s
Web site at: www.epa.gov/cair. Verbatim
transcripts and written statements will
be included in the rulemaking docket.
The public hearings will provide
interested parties the opportunity to
present data, views, or arguments
concerning the proposed rules. The EPA
may ask clarifying questions during the
oral presentations, but will not respond
to the presentations or comments at that
time. Written statements and supporting
information submitted during the
comment period will be considered
with the same weight as any oral
comments and supporting information
presented at a public hearing.
Because of the need to resolve the
issues in this document in a timely
manner, EPA will not grant requests for
extensions of the public comment
period.
What Should I Consider as I Prepare
My Comments for EPA?
ii. Follow directions—The agency
may ask you to respond to specific
questions or organize comments by
referencing a Code of Federal
Regulations (CFR) part or section
number.
iii. Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
iv. Describe any assumptions and
provide any technical information and/
or data that you used.
v. If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
vi. Provide specific examples to
illustrate your concerns, and suggest
alternatives.
vii. Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
viii. Make sure to submit your
comments by the comment period
deadline identified.
Availability of Related Information
Note that general instructions for
submitting comments are provided
above under the ADDRESSES section.
Submitting CBI. Do not submit
comments that include CBI to EPA
through EDOCKET, regulations.gov or email. Clearly mark the part or all of the
information that you claim to be CBI.
For CBI information in a disk or CD
ROM that you mail to 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 so marked will not be
disclosed except in accordance with
procedures set forth in 40 CFR part 2.
Send or deliver information identified
as CBI only to the following address:
Roberto Morales, U.S. EPA, Office of Air
Quality Planning and Standards, Mail
Code C404–02, Research Triangle Park,
NC 27711, telephone (919) 541–0880, email at morales.roberto@epa.gov,
Attention Docket ID No. OAR–2003–
0053.
Tips for Preparing Your Comments.
When submitting comments, remember
to:
i. Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
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14:49 Dec 01, 2005
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Documents related to the CAIR are
available for inspection in docket OAR–
2003–0053 at the address and times
given above. The EPA has established a
Web site for the CAIR at https://
www.epa.gov/cleanairinterstaterule or
more simply https://www.epa.gov/cair/.
Outline
I. Background
II. Today’s Action
A. Grant of Reconsideration
B. Schedule for Reconsideration
III. Discussion of Issues
A. SO2 Allocation Methodology in the
CAIR Model Trading Rules
B. Fuel Adjustment Factors Used To Set
State NOX Budgets
C. PM2.5 Modeling for Minnesota
D. Inclusion of Florida in the CAIR Region
for Ozone
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution or Use
I. National Technology Transfer
Advancement Act
J. Executive Order 12898: Federal Actions
To Address Environmental Justice in
Minority Populations and Low Income
Populations
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I. Background
On May 12, 2005, the EPA (Agency or
we) promulgated the final ‘‘Rule to
Reduce Interstate Transport of Fine
Particulate Matter and Ozone’’ (Clean
Air Interstate Rule or CAIR) (70 FR
25162). In this action, EPA found that
28 States and the District of Columbia
contribute significantly to
nonattainment of, or interfere with
maintenance by, downwind States with
respect to the NAAQS for fine particles
(PM2.5) and/or 8-hour ozone. The CAIR
requires these upwind States to revise
their State implementation plans (SIPs)
to include control measures to reduce
emissions of SO2 and/or NOX. Sulfur
dioxide is a precursor to PM2.5
formation and NOX is a precursor to
PM2.5 and ozone formation. By reducing
upwind emissions of SO2 and NOX,
CAIR will assist downwind PM2.5 and 8hour ozone nonattainment areas in
achieving the NAAQS.
The EPA promulgated the CAIR based
on the ‘‘good neighbor’’ provision of the
Clean Air Act (CAA), section
110(a)(2)(D), which establishes State
obligations to address interstate
transport of pollution. The EPA
conducted extensive air modeling to
determine the extent to which emissions
from certain upwind States were
impacting downwind nonattainment
areas. All States found to contribute
significantly to downwind PM2.5
nonattainment or maintenance problems
are included in the CAIR region for
PM2.5 and are required to reduce annual
emissions of SO2 and NOX. All States
found to contribute significantly to
downwind 8-hour ozone nonattainment
are included in the CAIR region for
ozone and required to reduce NOX
emissions during the 5-month ozone
season (May–September). The CAIR
establishes regional emission reduction
requirements for annual SO2 and NOX
emissions and seasonal NOX emissions.
The reduction requirements are based
on control technologies known to be
highly cost effective for electric
generating units (EGUs). The first phase
of NOX reductions starts in 2009
(covering 2009–2014) and the first phase
of SO2 reductions starts in 2010
(covering 2010–2014). The second phase
of both SO2 and NOX reductions starts
in 2015 (covering 2015 and thereafter).
Each State covered by CAIR may
independently determine which
emission sources to control, and which
control measures to adopt. States that
choose to base their programs on
emissions reductions from EGUs may
allow their EGUs to participate in an
EPA-administered cap and trade
program. The CAIR includes model
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rules for multi-State cap and trade
programs for annual SO2 and NOX
emissions, and seasonal NOX emissions.
States may choose to adopt these rules
to meet the required emissions
reductions in a flexible and highly costeffective manner. To learn more about
the CAIR and its impacts, the reader is
encouraged to read the preamble to the
CAIR (70 FR 25162; May 10, 2005).
The CAIR was promulgated through a
process that involved significant public
participation. The EPA published a
notice of proposed rulemaking on
January 30, 2004 (69 FR 4566) and a
notice of supplemental rulemaking on
June 10, 2004 (69 FR 32684). The EPA
also published a notice of data
availability on August 6, 2004 (69 FR
47828). The Agency held public
hearings on the January 2004 proposed
rule on February 25 and 26, 2004, and
an additional hearing on the
supplemental proposal on June 3, 2004.
In addition, the EPA received thousands
of comments on the proposals. We
responded to all significant public
comments in the preamble to the final
rule and the final response to comments
document available in the CAIR docket
(Docket No. OAR–2003–0053–2172).
Following publication of the final rule
on May 12, 2005, the Administrator
received eleven petitions requesting
reconsideration of certain aspects of the
final CAIR. These petitions were filed
pursuant to section 307(d)(7)(B) of the
CAA. Under this provision, the
Administrator is to initiate
reconsideration proceedings if the
petitioner can show that an objection is
of central relevance to the rule and that
it was impracticable to raise the
objection to the rule within the public
comment period or that the grounds for
the objection arose after the public
comment period but before the time for
judicial review had run. The petitions
for reconsideration of the CAIR ask EPA
to reconsider several specific aspects of
the final rule, and many of the petitions
make similar requests. This notice
addresses four of the issues raised in
those petitions. The EPA expects to
issue decisions on all remaining issues
raised in the petitions for
reconsideration by March 15, 2006. The
complete petitions are available in the
docket for the CAIR.1
1 Petitions for reconsideration were filed by: State
of North Carolina (OAR–2003–0053–2192); FPL
Group OAR–2003–0053–2201); Florida Association
of Electric Utilities (OAR–2003–0053–2200);
Entergy Corporation (OAR–2003–0053–2195 and
2198 (attachment 1)); Massachusetts Department of
Environmental Protection (OAR–2003–0053–2199);
Integrated Waste Services Association (OAR–2003–
0053–2193); Texas Commision on Environmental
Quality (OAR–2003–0053–2212); Northern Indiana
Public Service Corporation (OAR–2003–0053–2194
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In addition, fourteen petitions for
judicial review of the final rule were
filed with the U.S. Court of Appeals for
the District of Columbia.2 The fourteen
cases have been consolidated into a
single case, State of North Carolina v.
EPA (No. 05–1244) (D.C. Cir). Many of
the parties who petitioned EPA for
reconsideration of the CAIR also
petitioned for judicial review of the
rule.
By letters dated August 1, 2005, EPA
granted reconsideration of the definition
of ‘‘electric generating unit’’ or ‘‘EGU’’
as it relates to solid waste incinerators
(and particularly municipal waste
incinerators).3 The EPA explained that
the issue would be addressed in the
proposed rule signed the same day. That
proposed rule, entitled ‘‘Rulemaking on
Section 126 Petition from North
Carolina to Reduce Interstate Transport
of Fine Particulate Matter and Ozone;
Federal Implementation Plans to Reduce
Interstate Transport of Fine Particulate
Matter and Ozone; Revisions to the
Clean Air Interstate Rule; Revisions to
the Acid Rain Program; Proposed Rule,’’
was published on August 24, 2005 (70
FR 49708). In that proposed rule, EPA
reconsidered the definition of ‘‘EGU’’ in
the final CAIR as it relates to solid waste
incinerators (70 FR 49738). We
proposed revisions to the definition of
‘‘EGU’’ and requested comment on this
issue. In that action, we did not address
any other issues raised in the petitions
for reconsideration of the CAIR. Today’s
action does not reopen for comment any
aspect of the August 24, 2005, proposed
rule.
The EPA also received two requests to
stay the implementation of the CAIR in
limited geographic areas pending
resolution of this reconsideration
process. One petitioner requested a stay
of implementation of the CAIR in the
State of Florida, and one petitioner
and 2213 (supplemental petition)); City of Amarillo,
Texas, El Paso Electric Company, Occidental
Permian Ltd, and Southwestern Public Service
Company d/b/a/ Xcel Energy (OAR–2003–0053–
2196 and 2197 (attachment 1) and 2205–2207
(attachments 2–4)); Connecticut Business and
Industry Ass’n (OAR–2003–0053–2203); and
Minnesota Power, a division of ALLETE. Inc.
(OAR–2003–0053–2212).
2 State of North Carolina v. EPA (No. 05–1244);
Minnesota Power v. EPA (No. 05–1246); ARIPPA v.
EPA (No. 05–1249); South Carolina Public Service
Authority et al. v. EPA (No. 05–1250); Entergy Corp.
v. EPA (No. 05–1251); Florida Ass’n of Electric
Utilities (No. 05–1252); FPL Group v. EPA (No. 05–
1253); Northern Indiana Public Service Co. v. EPA
(No. 05–1254); South Carolina Electric & Gas Co. v.
EPA (No. 05–1256); Integrated Waste Services Ass’n
v. EPA (No. 05–1257); AES Corp v. EPA (No. 05–
1259); City of Amarillo, Texas et al. v. EPA (No. 05–
1260); Appalachian Mountain Club et al. v. EPA
(No. 05–1246); Duke Energy v. EPA (No. 05–1246).
3 These letters are available in the CAIR Docket.
(OAR–2003–0053–2209 and 2210).
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requested a stay of implementation of
the CAIR in the State of Minnesota. By
letter dated August 1, 2005, EPA
declined to stay implementation of the
CAIR in Florida.4 The EPA has not yet
acted on the request to stay
implementation of the CAIR in
Minnesota.
By letters dated November 21, 2005,
we informed several petitioners of our
intent to grant reconsideration on one or
more issues addressed in their petitions
for reconsideration. We indicated in
those letters that we would initiate the
reconsideration process by publishing
this notice.
II. Today’s Action
A. Grant of Reconsideration
In this notice, EPA is announcing its
decision to grant reconsideration on
four issues raised in the petitions for
reconsideration. This notice initiates
that reconsideration process and
requests comment on the issues to be
addressed. Given the intense public
interest in this rule, EPA has decided to
provide this additional opportunity for
public comment. At this time, however,
EPA does not believe that any of the
information submitted to date
demonstrates that EPA’s final decisions
were erroneous or inappropriate.
Therefore, we are not proposing any
modifications to the final CAIR.
The first issue on which EPA is
requesting comment relates to analysis
done by EPA to address petitioner’s
claims regarding alleged inequities
resulting from the application of the SO2
allowance allocation methodology that
States choosing to participate in the
trading program would use to allocate
SO2 allowances to sources. The second
issue relates to EPA’s use of specific fuel
adjustment factors to establish NOX
budgets for each State. The third issue
relates to modeling inputs used by EPA
to determine whether emissions from
Minnesota should be included in the
CAIR region for PM2.5. And the fourth
issue relates to EPA’s determination that
the State of Florida should be included
in the CAIR region for ozone. Each issue
is described in greater detail in Section
III of this notice.
The EPA is requesting comment only
on the issues specifically described in
Section III. We are not taking comment
on any other provisions in the CAIR or
otherwise reopening any other issues
decided in the CAIR for reconsideration
or comment.
4 This letter is also available in the CAIR Docket
(OAR–2003–0053–2208).
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B. Schedule for Reconsideration
For the four issues addressed in this
notice, EPA expects to take final action
on reconsideration by March 15, 2006.
By that date, EPA will finalize the
process of reconsideration by issuing a
final rule or proposing a new approach.
EPA also expects, by March 15, 2006, to
issue decisions on all remaining issues
raised in the petitions for
reconsideration.
III. Discussion of Issues
A. SO2 Allocation Methodology in the
CAIR Model Trading Rules
One petitioner argues that the SO2
allowance allocation methodology in
the CAIR model trading rules is
unreasonable and inequitable, and asks
EPA to establish a different approach.
According to the petitioner, the
methodology is inequitable because it
results in owners of units that have
lower emission rates, historically,
buying allowances from historically
higher emitting units that install new
emission controls. EPA does not accept
the petitioner’s characterization of this
issue. EPA continues to believe that the
methodology selected is reasonable for
the reasons explained in the final rule
and further outlined below.
Furthermore, numerous opportunities
for public comment on this issue were
provided, and a full discussion of the
allowance allocation options occurred
during the rule development process.
Nonetheless, given the intense public
interest in this issue, EPA has decided
to grant the Petition for Reconsideration
insofar as it raises issues regarding
alleged inequities resulting from the
application of the SO2 allowance
allocation.
As explained below, EPA has
conducted additional analyses
concerning the impact of the SO2
allowance allocation approach adopted
in the model rules, comparing this
approach to various other alternatives
considered during the rulemaking
process. These analyses further
illustrate that the approach selected
produces a reasonable result, not the
inequities alleged in the Petition for
Reconsideration. Therefore EPA is not
proposing any changes to the CAIR SO2
allocation approach as part of this
reconsideration notice. We are taking
comment on the analyses conducted
and our discussion of the petitioner’s
concerns.
Title IV and CAIR
The CAIR model SO2 trading program
relies on the use of title IV SO2
allowances for compliance with the
allowance-holding requirements of
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CAIR. Title IV SO2 allowances have
already been allocated on a unit-by-unit
basis in perpetuity, based on formulas
set forth in section 405 and 406 of title
IV, which were implemented through
final regulations issued in 1998 (Sec 42
U.S.C. 7651d and 7651e; and 18 CFR
73.10(b)). The statutory formula for SO2
allocations was generally based on unit
data for 1985–1987 and, for some units,
data for years up to 1995. For the title
IV SO2 trading program, each allowance
authorizes one ton of SO2 emissions.
For the CAIR SO2 trading program,
SO2 reductions would be achieved by
generally requiring CAIR sources to
retire more than one title IV allowance
for each ton of their SO2 emissions for
2010 and thereafter. Specifically, each
title IV SO2 allowance issued for 2009
or earlier would be used for compliance
by CAIR sources at a ratio of one
allowance per ton of SO2 emissions and
would authorize one ton of SO2
emissions. Each title IV allowance of
vintage 2010 through 2014 would be
used for compliance under CAIR at a
two-to-one ratio and authorize 0.5 tons
of SO2 emissions. Each title IV
allowance of vintage 2015 and later
would be used at a 2.86-to-1 ratio and
authorize 0.35 tons of SO2 emissions.
See discussion in the preamble to the
final CAIR in section VII (70 FR 25255–
25273) and section IX (70 FR 25290–
25291).
SO2 Allocation Options in CAIR
A variety of SO2 allowance allocation
methodologies were raised and analyzed
during the rulemaking process,
including the one EPA selected.
Alternative methodologies analyzed
included allocating on the basis of
historic tonnage emissions, heat input
(with alternatives based on heat input
from all fossil generation, and heat
input from coal- and oil-fired generation
only) and output (with alternatives
based on all generation and all fossilfired generation). While every allocation
methodology suggested by commenters
during the rulemaking process has its
advantages and disadvantages for
different companies and States, EPA
explained in the final rule that its
chosen methodology is reasonable on
several grounds. First, EPA believes that
‘‘achieving SO2 reductions for EGUs
using the title IV allowances is
necessary in order to ensure the
preservation of a viable title IV
program’’ (Response to Comments (RTC)
at page 511, section X.A.26, 2005). See
also discussion in preamble to the final
CAIR in section IX (70 FR 25290–
25291). Second, in using the title IV
allowances, EPA relied on the selection
by Congress of the permanent allocation
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methodology established in title IV for
purposes of reducing SO2 emissions. As
stated in the RTC (page 512), ‘‘Congress
clearly did not choose a policy to
regularly revisit and revise these
allocations, believing that its allocations
methodology for title IV allowances
would be appropriate for future time
periods.’’
Third, title IV allowance allocations
provide a logical and well understood
starting point from which additional
EGU SO2 emission reductions can be
achieved for Acid Rain units, which
account for over 90% of the SO2
emissions from CAIR EGUs. Finally,
EPA’s State-by-State analysis of several
methods for SO2 allocations shows that
the use of title IV allowances to develop
state budgets creates a reasonable result
(See RTC, section X.A.26). The policy
decision to base the CAIR SO2 budgets
on the existing title IV allowance
system, and EPA’s demonstration that
the result of using the system is
reasonable fully support the use of an
allocation system based on title IV
allowances.
Analysis of SO2 Allocation Options
As a part of this reconsideration, EPA
performed additional analyses,
explained below, to evaluate the SO2
allocation methodology in the final
CAIR rule in light of the petitioner’s
concerns. In these analyses, EPA
compared three alternative SO2
allowance allocation methodologies to
the methodology in the final CAIR to see
how companies fared in terms of the
amount of allowances allocated relative
to their projected SO2 emissions. The
allocation allowance methodologies
evaluated by EPA were the ones referred
to by the petitioner in the Petition for
Reconsideration. EPA believes that, for
purposes of evaluating the various
allocation methodologies, computing
allocations on a company-by-company
basis is more appropriate than
comparing allocations on a unit-by-unit
basis. This is because, while one unit
could be allocated fewer allowances
under one methodology, another unit
owned by the same company could be
allocated more allowances, which may
offset the smaller allocation of the first
unit.
The three alternative allowance
allocation methodologies EPA analyzed
were suggested by various commenters
during the rulemaking process. Also
note that methodologies 2 and 3 were
suggested by the petitioner. These
methodologies are:
1. Allocating allowances based on
more recent heat input data;
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2. Allocating allowances based on
more recent heat input data adjusted for
fuel type (e.g., coal, oil and gas);
3. Allocating allowances based on
more recent heat input data adjusted
both for fuel type (e.g., coal, oil and gas)
and for coal type (e.g., bituminous, subbituminous and lignite).
In comparing the CAIR final SO2
allocation methodology and the three
alternative methodologies, EPA took
into account certain factors that are
applicable to the CAIR final allocation
methodology but not to the three
alternative methodologies. For all four
methodologies, EPA analyzed the
resulting total allowance allocations,
and the total projected emissions, for
companies’ sources located in the States
subject to CAIR. In addition, for all the
methodologies, EPA analyzed the
relationship between allowances and
emissions in two ways. In the first, EPA
calculated the ratio of allowances to
total projected emissions before CAIR
controls (base case). This measures how
much each company falls short of
allowance needs. Then, in the second
approach, EPA calculated the ratio of
allowances to total projected emissions
with CAIR controls installed (control
case). This way measures how many
allowances a company would need to
purchase after controls are installed.
For the CAIR final methodology, EPA
also considered both the allowance
allocations and emissions for
companies’ sources both in the CAIR
region and outside the CAIR region.
EPA believes that this is appropriate
because, under the CAIR final
methodology, if a company’s sources
outside the CAIR region have more title
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IV allowances than needed to cover
their emissions under the Acid Rain
Program, the company could transfer, at
little or no net cost, excess allowances
to the company’s sources in the CAIR
region for use to cover emissions under
the CAIR trading program. Under the
three alternative methodologies, which
would require creating new CAIR SO2
allowances independent of the existing
title IV allocations, CAIR sources could
not use title IV for compliance with the
CAIR SO2 allowance holding
requirements.
Further, in the analysis of the CAIR
final methodology, EPA considered the
allocation of title IV allowances to CAIR
region units that are not currently in the
Acid Rain Program but that could opt
into the Acid Rain Program and receive
title IV allowances (see 42 U.S.C. 7651i
and 18 CFR part 74). This analysis
assumed that companies owning nonAcid Rain units affected by CAIR would
opt into the Acid Rain Program because
they would receive title IV allowances
to cover a portion of the unit’s
emissions under CAIR. EPA believes
this assumption is reasonable because
there is very little cost associated with
opting into the Acid Rain Program.5 In
contrast, the analysis of the three
alternative methodologies did not
consider Acid Rain Program opt-in
allowances because these approaches do
not use title IV allowances for CAIR
compliance.
5 The greatest cost associating with opting in to
the title IV program is the cost of monitoring. Since
these sources are already required to monitor using
the same monitoring methodologies that would be
required if they were to opt in, their costs for opting
in are significantly reduced.
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EPA’s analyses, of which a detailed
description is available in the docket,
encompassed 112 (control case) to 114
(base case) parent/holding companies
with sources covered by the CAIR.
These 112 to 114 companies represent
about two-thirds of the total number of
CAIR plants, over 95 percent of total
annual allocations for all methodologies
during 2015, and about 97 percent of the
total projected emissions in the CAIR
region in 2015.6
While allocations vary from company
to company under the four
methodologies, overall, the distributions
of allowances that companies received
relative to their projected emissions for
both the base case and control case are
very similar. In other words, no
methodology stands out as providing a
more reasonable method of allocation
across all companies when examining
allowance needs under either the base
case or control case. Figures 1 and 2,
below, show the distribution of values
for each methodology under the two
cases, and support this conclusion. EPA
repeated these analyses for 2010, which
show similar results. Separate analyses
of owner/operating company allowances
compared to emissions in 2010 and
2015, show similar results, as well. See
TSD Memo, ‘‘Technical Support
Document for Clean Air Interstate Rule
Response to Petition for
Reconsideration.’’
BILLING CODE 6560–50–P
6 According to EPA inventory data, there are a
total of 921 CAIR affected plants. EPA did not have
complete owner, parent company information for
all of these plants.
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EPA also notes that, while the
Petitioner states that the CAIR final
allocation methodology is ‘‘inequitable’’
because lower emitting units would buy
allowances from higher emitting units
that install emission controls, it is
unclear why such a result would
actually be inequitable. On the contrary,
the owner of each of the units involved
would be choosing to adopt the most
economic compliance strategy in light of
the unit’s emission control costs and the
market value of allowances. The ability
of the owners to make such choices
reflects the flexibility provided by a cap
and trade program.
The EPA requests comment on its
analyses of the four allocation
methodologies and on the above
discussion of the Petitioner’s concerns.
B. Fuel Adjustment Factors Used To Set
State NOX Budgets
Several petitioners argue the Agency
did not provide adequate notice
regarding the use of specific fuel
adjustment factors to establish NOX
budgets for States in the CAIR region.
As explained below, EPA believes that
it provided adequate notice both that
the fuel adjustment factors might be
used and of the calculation procedures
that it would use to determine the
specific factors. Nevertheless, given the
significant public interest in this issue,
EPA has decided to grant
reconsideration of, and to take comment
on, EPA’s use of fuel adjustment factors
(i.e., 1.0 for coal, 0.4 for gas, and 0.6 for
fuel oil) in setting State NOX budgets.
Today’s action also presents additional
analysis that EPA conducted to further
explain the impact of these factors on
State annual NOX budgets. This analysis
demonstrates that the factors selected
are reasonable and decrease the
disparity between most States’ actual
electric generation unit (EGU) emissions
and their State NOX budgets. For that
reason, EPA is not proposing any
changes to the final CAIR at this time.
The CAIR establishes regional
emission budgets for annual NOX, and
seasonal NOX emissions. These regional
budgets are then further divided into
State budgets, with a share of each total
regional budget allocated to each State
in the corresponding CAIR region.
States choosing to participate in the
trading programs will be able to
allocate, to sources in their State, the
number of allowances in their budgets.
Petitioners challenge the methodology
EPA used to establish these State
budgets for annual and seasonal NOX.
Background
For States choosing to participate in
the trading program, these budgets
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determine the number of allowances
that could be allocated to sources in that
State. In a cap and trade system,
however, the methodology used to
allocate allowances in any given year
would not affect where control
technologies are installed.7 Rather, the
determinant would be the cost of adding
controls compared to the cost of buying,
or the profit from selling, allowances.
Controls are expected to be installed
where it is relatively less expensive,
without regard to which units received
the initial allocation of allowances.
Further, the total cost to industry of
controlling emissions and the total
amount of reductions achieved would
not be affected by the allocation
methodology in a given year (for a
permanent system). The allocation
method, however, could have financial
impacts on individual units and
companies. A unit that receives more
allocations than it has emissions would
get a benefit at the expense of a unit that
does not receive enough allocations to
cover its emissions. While States
choosing to participate in the cap and
trade program can determine how to
allocate allowances among their units,
companies in States whose budgets
exceed projected EGU emissions would
likely receive a financial benefit while
companies in States whose budgets are
lower than their EGU emissions would
likely incur additional costs. In the
absence of other considerations, EPA
believes that it is in the public interest
to reduce the disparity between the
number of allowances in a State budget
and total projected State EGU emissions.
Notice of Fuel Factor Use in CAIR
Promulgation
In the CAIR notice of proposed
rulemaking (NPR), EPA proposed to use
the simple heat input method. (69 FR
4566) This approach used the unadjusted heat input to set budgets based
on heat input data from the years 1999
through 2002. EPA proposed to give
each State a pro rata share of the
regional NOX budget based on the ratio
of its average annual heat input to the
regional total average annual heat input.
In the Supplemental Notice of
Proposed Rulemaking (SNPR), EPA
proposed to supplement and update the
data used to calculate the State annual
NOX budgets (69 FR 32684). EPA also
described an alternative method that
7 A permanent allocation approach, such as the
CAIR allocation methodology in the model trading
rules, should not affect where controls are installed.
This is true regardless of the type of approach used
to permanently allocate allowances (e.g., heat input,
adjusted heat input, or output). The use of an
updating allocation system, on the other hand,
could impact future generation behavior.
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could be used to calculate the budgets—
the adjusted heat input (fuel factor)
method. This approach, EPA explained,
would ‘‘* * * reflect the inherently
higher emissions rate of coal-fired
plants, and consequently the greater
burden on coal plants to control
emissions.’’ (See 69 FR 32689.) The
SNPR further explains ‘‘in contrast to
allocations based on historic emissions,
the factors would also not penalize coalfired plants that have already installed
pollution controls’’ (69 FR 32689). In
the SNPR, EPA also described the
method that it would use to derive
specific fuel factors if this adjusted heat
input method was selected. EPA
explained, ‘‘States’ shares would be
determined by the amount of the State
heat input, as adjusted, in proportion to
the total regional heat input. The factors
could be based on average historic
emissions rates (in lbs/mmBtu) by fuel
type (coal, gas, and oil) for the years
1999–2002’’ (69 FR 32689). The SNPR
did not identify the specific numeric
factors that would be used. EPA
received and responded to numerous
comments addressing this alternative
fuel factor approach. (See ‘‘Corrected
Response to Significant Public
Comments on the Proposed Clean Air
Interstate Rule,’’ pp. 520–576.)
EPA established State NOX budgets
for the final CAIR using the adjusted
heat input method. The specific fuel
factors used to adjust heat input data
were 1.0 for coal, 0.4 for gas and 0.6 for
oil. These factors are based on the
average historic NOX emissions rate for
each fuel. They reflect for each fuel, the
1999–2002 average emissions by State
summed for the CAIR region, divided by
average heat input by fuel by State,
summed for the CAIR region (70 FR
25230–25231).
EPA Analyses of Potential Impacts
EPA conducted two analyses to
evaluate the potential impact of using
the adjusted heat input method versus
the simple heat input method on State
annual NOX budgets: one on a
regionwide scale and the second on a
State-by-State level.
The regionwide analysis of the
potential impacts compared regionwide
budgets using both approaches (i.e.
simple heat input and fuel factor) to the
regionwide projected emissions of units
fired with that fuel.8 Regional budgets
and emissions, by fuel type, are
summarized in Table 1.
8 It should be noted that simple heat input or
adjusted heat input are used to set State budgets
and do not imply that States would allocate
allowances to units in that manner. In the proposal,
EPA gives States flexibility in the distribution of
allowances.
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TABLE 1.—REGIONWIDE COMPARISON OF CAIR ALLOWANCE DISTRIBUTIONS AND EMISSIONS BY FUEL TYPE
[Thousand tons]
Projected 2009* emissions and
allowances
Coal
Base Case Emissions ..............................................................................
CAIR Emissions .......................................................................................
Simple Heat Input Allowances .................................................................
Fuel Factor Adjusted Allowances ............................................................
2,635
1,404
1,197
1,349
Other
fossil**
97
99
308
156
Projected 2015 emissions and allowances
Total
Coal
2,732
1,503
1,505
1,505
2,650
1,151
998
1,124
Other
fossil
96
89
256
130
Total
2,746
1,254
1,254
1,254
* Numeric value is based on 2010 projections.
** Numeric value includes wood and refuse in three States.
Assuming allowancesare often passed
through to generation units in the same
way that they are apportioned to the
States, Table 1 illustrates that under
either approach natural gas-fired and
other non-coal-fired generation receives
more allowances than their projected
emissions in both 2009 and 2015 and
therefore States with more units of this
type receive a greater share of the
budget. However, using the fuel factor
approach, the disparity between the
number of allowances provided and the
emissions is less than under the simple
heat input method. Table 1 also
demonstrates that the majority of
emission reductions are made by coalfired sources. States with more of these
types of units receive a greater share of
the regional budget under the fuel factor
approach (however, the portion of the
budget derived from the heat input from
these units is still generally smaller than
their projected emissions). Therefore,
the fuel factor approach generally
provides additional allowances to States
with large amounts of coal-fired units
that are making the investments in
emission control measures and
technologies. Conversely the simple
heat input approach provides more
allowances to States with larger
amounts of gas-fired units that are not
making reductions. Note that under
either approach the portion of the State
budgets derived from the heat input
from the gas-fired units generally
exceeds both the historical and the
future projected emissions from these
units. This finding led EPA to believe
that the fuel factor approach better
reduced the disparity between projected
emissions and State budgets.
EPA conducted a second analysis that
examined the potential impacts of the
two approaches for developing
Statewide budgets (i.e., simple heat
input and fuel factor) on a State-by-State
basis. This analysis, summarized in
Tables 2 and 3 below, shows that States
receiving fewer allowances using a fuel
factor approach, generally still receive
Statewide budgets that are greater than
their projected emissions in 2009 and
2015. This results because a substantial
portion of their generation portfolio
consists of gas-fired sources with
generally low NOX emission levels.
TABLE 2.—COMPARISON OF PROJECTED NOX MISSIONS AND STATE BUDGETS FOR CAIR STATES NOT DOMINATED BY
COAL GENERATION
[Thousand tons]
Projected 2009 * emissions and
budgets
Projected 2015 emissions and
budgets
State
Coal
DC ** ......
LA ..........
NY ..........
TX ..........
MS .........
FL ...........
Base Case Emissions ..........................................................
CAIR Emissions ...................................................................
Simple Heat Input Budget ...................................................
Fuel Factor Adjusted Budget ...............................................
Base Case Emissions ..........................................................
CAIR Emissions ...................................................................
Simple Heat Input Budget ...................................................
Fuel Factor Adjusted Budget ...............................................
Base Case Emissions ..........................................................
CAIR Emissions ...................................................................
Simple Heat Input Budget ...................................................
Fuel Factor Adjusted Budget ...............................................
Base Case Emissions ..........................................................
CAIR Emissions ...................................................................
Simple Heat Input Budget ...................................................
Fuel Factor Adjusted Budget ...............................................
Base Case Emissions ..........................................................
CAIR Emissions ...................................................................
Simple Heat Input Budget ...................................................
Fuel Factor Adjusted Budget ...............................................
Base Case Emissions ..........................................................
CAIR Emissions ...................................................................
Simple Heat Input Budget ...................................................
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0
0
0
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30
19
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141
122
114
128
36
30
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13
132
51
58
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Total
0
<1
<1
<1
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23
14
7
7
42
25
45
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118
53
1
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58
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<1
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61
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186
166
231
181
37
31
21
18
151
69
116
02DEP1
0
0
0
0
45
27
16
18
38
15
16
17
141
122
95
106
36
6
9
10
132
44
48
Other
fossil
<1
<1
<1
<1
5
5
26
12
6
6
35
21
39
35
98
44
2
2
8
4
18
18
48
Total
<1
<1
<1
<1
50
32
42
30
44
21
51
38
179
157
192
151
37
8
18
15
151
61
97
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Federal Register / Vol. 70, No. 231 / Friday, December 2, 2005 / Proposed Rules
TABLE 2.—COMPARISON OF PROJECTED NOX MISSIONS AND STATE BUDGETS FOR CAIR STATES NOT DOMINATED BY
COAL GENERATION—Continued
[Thousand tons]
Projected 2009 * emissions and
budgets
Projected 2015 emissions and
budgets
State
Other
fossil
Coal
Fuel Factor Adjusted Budget ...............................................
65
Total
34
Other
fossil
Coal
99
54
28
Total
83
* Numeric value is based on 2010 projections.
** For DC: Projected Base Case emissions are 35 tons in 2015. CAIR Emissions are projected to be 35 tons in both 2009 and 2015. Simple
Heat Input budgets are 213 and 178 tons in 2009 and 2015, respectively. Fuel Factor budgets are 144 and 120 tons in 2009 and 2015,
respectively.
Table 2 lists those States in the CAIR
region that have significant amounts
(i.e., 40 percent or greater) of generation
sources that combust fossil fuels other
than coal. As illustrated by Table 2, DC,
FL, LA, MS, NY, and TX, while
their gas-fired units, these units would
still have excess allowances.
Furthermore in most cases, these States
still receive a larger budget than they
need to cover their projected emissions.
receiving fewer allowances under a fuel
factor approach, are provided with
reasonable Statewide budgets that are
comparable to their projected emissions
in 2009 and 2015. If the States were to
directly pass through allowances to
TABLE 3.—COMPARISON OF PROJECTED NOX EMISSIONS AND STATE BUDGETS FOR CAIR STATES
[Thousand tons]
Projected 2009 * emissions and budgets
Budget
Emissions
State
Base
case
Projected 2015 emissions and budgets
CAIR
Simple
heat input
Fuel
factor
adjusted
Budget
Emissions
Percent
change
Base
case
Simple
heat input
CAIR
Fuel
factor
adjusted
Percent
change
DC ** .........................
LA .............................
NY ............................
TX .............................
MS ............................
FL .............................
MI .............................
MD ............................
VA .............................
AL .............................
GA ............................
IL ..............................
WI .............................
PA .............................
SC ............................
MO ............................
MN ............................
NC ............................
IN ..............................
OH ............................
TN .............................
KY .............................
IA ..............................
WV ............................
0
49
45
186
37
151
117
57
68
132
143
146
71
198
49
116
72
60
234
264
106
176
76
179
<1
35
36
166
31
69
88
13
43
65
106
66
47
86
38
64
36
59
121
91
37
99
45
62
<1
50
61
231
21
116
64
27
35
64
61
70
37
90
30
54
28
56
98
97
46
74
29
66
<1
36
46
181
18
99
65
28
36
69
66
76
41
99
33
60
31
62
109
109
51
83
33
74
¥32
¥29
¥25
¥22
¥16
¥14
3
4
5
8
9
9
9
10
10
10
11
11
11
12
12
12
12
13
<1
50
44
179
37
151
120
57
60
134
141
159
69
193
50
118
74
61
233
274
106
176
81
176
<1
32
21
157
8
61
90
12
39
49
67
65
34
72
36
66
37
49
79
90
27
74
47
40
<1
42
51
192
18
97
53
22
29
53
51
58
31
75
25
45
24
47
81
81
38
62
24
55
<1
30
38
151
15
83
54
23
30
58
55
64
34
83
27
50
26
52
91
91
42
69
27
62
¥33
¥29
¥25
¥22
¥16
¥14
3
4
5
8
9
9
9
10
10
10
11
11
11
12
12
12
12
13
Total ..................
2732
1503
1505
1505
0
2746
1254
1254
1254
0
* Numeric value is based on 2010 projections.
** For DC: Projected ** Base Case emissions are 35 tons in 2015. CAIR Emissions are projected to be 35 tons in both 2009 and 2015. Simple
Heat Input budgets are 213 and 178 tons in 2009 and 2015, respectively. Fuel Factor budgets are 144 and 120 tons in 2009 and 2015,
respectively.
Table 3 shows that relative to the
simple heat input method the fuel factor
method reduces the disparity between
projected State emissions and State
budgets, because the fuel factor
approach allocates State budgets that are
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generally closer to projected State
emissions. As explained above, the
States that receive smaller budgets
under the fuel factor method are still
generally receiving budgets that exceed
their projected emissions. States that
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receive larger budgets under the fuel
factor method are generally States with
a large amount of coal-fired generation
that are installing post combustion
controls as a result of CAIR.
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Analysis of Potential Delaware and New
Jersey Impacts
The analyses described above were
conducted for the States in the CAIR
PM2.5 region only. EPA has proposed to
add Delaware and New Jersey to the
CAIR region for PM2.5 (‘‘Inclusion of
Delaware and New Jersey in the Clean
Air Interstate Rule’’, EPA, May 10,
2005), but has not yet taken final action
on this proposal. EPA proposed a
separate 2-State ‘‘regional’’ budget for
Delaware and New Jersey of just over
14,000 tons. EPA’s analysis, presented
in Table 4, shows that apportioning this
budget between the two States based on
a fuel factor method instead of a simple
heat input method, is reasonable.
(‘‘Inclusion of Delaware and New Jersey
in the Clean Air Interstate Rule’’, EPA,
May 10, 2005)
TABLE 4.—COMPARISON OF PROJECTED NOX EMISSIONS AND STATE BUDGETS FOR NEW JERSEY AND DELAWARE
[Thousand tons]
Projected 2009 * emissions and allowance allocation
Base
case
emissions
State
NJ .............................
DE ............................
CAIR
emissions
Simple
heat input
budget
Fuel
factor
adjusted
budget
16.8
9.4
12.0
8.5
13.4
3.4
12.7
4.2
Percent
change
¥5.6
22.1
Projected 2015 emissions and allowance allocation
Base
case
emissions
CAIR
emissions
Simple
heat input
budget
Fuel
factor
adjusted
budget
17.9
10.7
12.8
9.5
11.2
2.8
10.6
3.5
Percent
change
¥5.6
22.2
* Numeric value is based on 2010 projections.
Other Considerations
EPA notes that the analyses above
were conducted for State annual NOX
budgets established in the CAIR. CAIR
also establishes seasonal NOX budgets
using the fuel factor approach. EPA did
not conduct a similar analysis of the
seasonal NOX budgets. EPA modeling
indicates that the ozone season program
is likely to function as a backstop to the
annual NOX program, and that the
annual NOX program is likely to impose
the binding constraint on NOX
emissions.
Finally, to ensure that our estimates
appropriately reflect the distribution of
emissions in the case of higher
electricity demand and increased gas
and oil prices, EPA conducted a
sensitivity run using EIA’s forecast of
higher electricity demand and gas and
oil prices. This run produced very
similar emissions results to the original
NOX analysis, showing that EPA’s
original analysis is robust enough to
support the fuel adjusted heat input
approach finalized in CAIR. (See the
‘‘CAIR Statewide NOX Budget
Calculations Technical Support
Document, EPA 2005, for additional
discussion of the analysis.)
C. PM2.5 Modeling for Minnesota
One petitioner asserts that EPA’s
modeling to determine whether
emissions from Minnesota significantly
contribute to downwind nonattainment
of the PM2.5 NAAQS failed to take into
account certain emissions reductions
required by State programs. The
petitioner asserts that if these reductions
had been properly included in the
modeling done for CAIR, the modeling
might show that the State of Minnesota
does not significantly contribute to
downwind nonattainment of the PM2.5
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NAAQS. The petitioner also asked EPA
to stay implementation of the CAIR in
Minnesota. The Agency is not taking
action on the request for a stay at this
time.
The Agency agrees that EPA’s
modeling of the contribution of
emissions from Minnesota to downwind
PM2.5 nonattainment for the final CAIR
did not fully account for the effects on
future year emissions of certain State
control programs. In order to ensure that
all parties have ample opportunity to
comment on all aspects of this issue,
EPA is reconsidering the air quality
modeling inputs for Minnesota.
Using the corrected inputs described
below, EPA recently remodeled the
PM2.5 contributions from emissions in
Minnesota. In this analysis, EPA used
the same PM2.5 modeling platform that
was used for the final CAIR modeling.
This modeling platform is described in
the CAIR Air Quality Modeling
Technical Support Document
(‘‘Technical Support Document for the
Final Clean Air Interstate Rule, Air
Quality Modeling,’’ March 2005, OAR–
2003–0053–2123). The EPA is not taking
comment on the modeling platform
itself, only on the corrected 2010
emissions inputs for Minnesota, as
described below.
The result of the revised 2010
Minnesota PM2.5 contribution modeling
is that Minnesota contributes a
maximum of 0.20 µg/m3 to PM2.5
nonattainment in Chicago, IL. This
result confirms the findings from the
CAIR PM2.5 contribution modeling that
emissions in Minnesota make a
significant contribution to PM2.5
nonattainment in Chicago, IL. The 2010
emissions inputs used in the revised
Minnesota modeling and the revised
contributions to each downwind
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nonattainment receptor county can be
found in the CAIR docket.
The following discussion provides
background on the corrected emissions
inputs for Minnesota and on air quality
analyses that the Agency conducted
prior to finalizing CAIR.
The emissions for the electric power
sector used in EPA’s contribution
modeling for the final CAIR were
derived from the Integrated Planning
Model (IPM). The IPM is designed to
forecast the projected impact of
environmental polices on the electric
power sector. The Agency updated its
IPM modeling for the final CAIR. As
part of a routine model update to the
IPM and in response to comments from
various parties, EPA updated the
inventory of EGUs, made revisions to
several model assumptions, and added
various State rules, regulations, and
New Source Review settlements to best
reflect available data and information.
In that IPM update for the final CAIR,
the Agency included emission reduction
actions that are required by Minnesota
for certain units, based on the data
available. However, as discussed in the
RTC for the final CAIR (‘‘Corrected
Response to Significant Public
Comments on the Proposed Clean Air
Interstate Rule,’’ March 2005, corrected
April 2005, OAR–2003–0053–2172) as
well as in a memorandum to the CAIR
docket entitled ‘‘Emissions in
Minnesota: Additional Analysis’’ (OAR–
2003–0053–2091) (’’Minnesota
memorandum’’), the Agency discovered
that there may be some discrepancies
between how the Agency represented
the Minnesota emissions reductions in
the final CAIR IPM update and how the
reductions would be implemented. The
Agency revised its IPM model to better
reflect the emissions reductions from
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those Minnesota units and conducted
revised emissions modeling using the
IPM (in the memorandum mentioned
above, the revised emissions modeling
is described as a sensitivity analysis.)
The revised emissions modeling
(sensitivity analysis) resulted in
somewhat lower NOX and SO2 emission
projections for Minnesota in the base
case, compared to the emissions
modeling done for the final CAIR. The
revised emissions modeling was
discussed in the RTC for the final CAIR
and in the Minnesota memorandum.
Specifically, that revised IPM
modeling projects statewide utility NOX
emissions roughly 16,500 tons lower
and SO2 emissions about 5,800 tons
lower than the emissions modeling used
in the final CAIR. These revised NOX
and SO2 emission projections result in
lower total NOX and SO2 emissions of
4.6 percent and 4.3 percent,
respectively, than the emission
projections used in the final CAIR
modeling. In order to account for these
revised emission projections, the
Agency performed two analyses to
estimate whether air quality modeling
based on the lower emission projections
would show that Minnesota’s
downwind contribution was below the
PM2.5 significance threshold of 0.2
µg/m3. The EPA’s modeling of
Minnesota for the final CAIR showed
that Minnesota’s maximum downwind
contribution is 0.21 µ/m3 to Cook
County, Illinois. The Agency’s analyses
of the effects of the lower emission
projections on Minnesota’s maximum
contribution, which were presented in
the RTC for the final CAIR and the
Minnesota Memorandum, are
summarized below:
• Analysis 1: We reduced the
maximum PM2.5 contribution by the
larger of the percent reduction in NOX
and SO2 emissions (i.e., the 4.6 percent
reduction in NOX). The maximum PM2.5
contribution after making this
adjustment is 0.2 µg/m3.
• Analysis 2: We reduced the sulfate
and nitrate portions of the maximum
PM2.5 contribution by the corresponding
reductions in SO2 and NOX emissions.
Specifically, the sulfate portion
(including sulfate, ammonium, and
particle-bound water) was reduced by
the 4.3 percent reduction in SO2
emissions and the nitrate portion was
reduced by the 4.6 percent reduction in
NOX emissions. We then recalculated
the maximum contribution using these
lower components. The result is that the
adjusted maximum PM2.5 contribution
is 0.2 µg/m3.
Thus, the analyses presented in the
RTC and the Minnesota memorandum
indicate that Minnesota makes a
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significant contribution to PM2.5
nonattainment, even after considering
the lower emissions levels in the revised
emissions modeling.9
Although the Agency’s analyses of
downwind impacts from Minnesota
which were based on the revised
emissions modeling (and presented in
the RTC and the Minnesota
memorandum) indicate that the State
makes a significant contribution to
downwind PM2.5 nonattainment, the
Agency acknowledges that it did not at
that time conduct air quality modeling
based on the revised emissions
modeling. However, as discussed above,
the Agency has now remodeled the
PM2.5 contribution from emissions in
Minnesota and the results of that
revised modeling confirm that
emissions in Minnesota make a
significant contribution to PM2.5
nonattainment in Chicago, IL. This
revised PM2.5 contribution modeling
used the same modeling platform as
EPA used for the final CAIR modeling
coupled with the revised emissions
inputs for Minnesota discussed above.
The EPA is taking comment only on the
revised inputs for Minnesota discussed
above.
D. Inclusion of Florida in the CAIR
Region for Ozone
Florida petitioners (the Florida
Association of Electric Utilities and FPL
Group) maintain that neither the
proposed rule nor the supplemental
proposal or notice of additional data
availability gave adequate notice that
Florida might be included within the
CAIR region as a significant contributor
for ozone. They further maintain that
EPA’s ultimate determination to include
Florida within the ozone CAIR region
was based on modeling inputs not
readily available for comment. The
petitioners state that they therefore
lacked adequate opportunity to
comment on this issue.
The EPA does not fully accept the
Florida petitioners’ characterization.
Clearly, for example, EPA gave notice
that it would utilize a different
modeling platform for the final rule,
9 Although the petition acknowledges that the
Agency revised its IPM emissions analysis to reflect
emission reductions at certain Minnesota units, it
states incorrectly that ‘‘EPA subsequently learned
that emission levels in the IPM sensitivity analysis
were overstated by an additional 16,500 tons of
annual NOX emissions and 5,800 tons of annual
SO2 emissions’’ (petition, p. 7). As discussed above,
the emission projections in EPA’s revised IPM
modeling (the sensitivity analysis) were in fact
lower by 16,500 tons of annual NOX emissions and
5,800 tons of SO2 emissions than the emission
projections in EPA’s modeling for the final CAIR.
For the same reason, the petition is incorrect in
stating (p. 7) that EAP failed to consider these
emission reductions in its analysis.
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with the necessary implication that this
could change the makeup of the CAIR
ozone (and PM2.5) regions (69 FR 47828;
August 6, 2004). The EPA also provided
access to the data inputs for the
modeling runs, including emissions
data and the information necessary to
process that emissions data into modelready files. Nonetheless, considering all
the factors here (notably the absence of
Florida from the CAIR region for ozone
in the NPR and SNPR), EPA has decided
to provide an opportunity for additional
public comment on the inclusion of
Florida within the CAIR region for
ozone.
IV. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), the Agency
must determine whether the regulatory
action is ‘‘significant’’ and, therefore,
subject to Office of Management and
Budget (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 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, OMB has determined that
this is not a significant regulatory
action. This notice takes comment on
several aspects of the CAIR, but does not
propose any modifications.
B. Paperwork Reduction Act
This action does not propose
information collection request
requirements under the provisions of
the Paperwork Reduction Act, 44 U.S.C.
3501 et seq. Therefore, an information
collection request document is not
required.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
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or provide information to or for a
Federal agency. This includes the time
needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purposes of
collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR part 9.
C. Regulatory Flexibility Act
The Regulatory Flexibility Act
generally requires an Agency to prepare
a regulatory flexibility analysis of any
rule subject to notice and comment
rulemaking requirements under the
Administrative Procedures Act or any
other statute unless the Agency certifies
the rule will not have a significant
economic impact on a substantial
number of small entities. Small entities
include small businesses, small
organizations, and small governmental
jurisdictions.
For purposes of assessing the impacts
of today’s proposed rule on small
entities, small entity is defined as: (1) A
small business that is a small industrial
entity as defined in the U.S. Small
Business Administration (SBA) size
standards. (See 13 CFR part 121.); (2) a
governmental jurisdiction that is a
government of a city, county, town,
school district or special district with a
population of less than 50,000; and (3)
a small organization that is any not-forprofit enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of today’s proposed rule on
small entities, I certify that this action
will not have a significant economic
impact on a substantial number of small
entities. This notice does not impose
any requirements on small entities. We
are only announcing our decision to
reconsider and request comment on
specific issues in the CAIR. We continue
to be interested in the potential impacts
of the rule on small entities and
welcome comments on issues related to
such impacts.
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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. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures by State, local,
and Tribal governments, in the
aggregate, or by the private sector, of
$100 million or more in any 1 year.
Before promulgating an EPA rule for
which a written statement is needed,
UMRA section 205 generally requires
EPA to identify and consider a
reasonable number of regulatory
alternatives and adopt the least costly,
most cost-effective, or least-burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the leastcostly, most cost-effective, or leastburdensome alternative if the
Administrator publishes with the final
rule an explanation why that alternative
was not adopted. Before EPA establishes
any regulatory requirements that may
significantly or uniquely affect small
governments, including tribal
governments, it must have developed,
under section 203 of the UMRA, a small
government agency plan. The plan must
provide for notifying potentially
affected small governments, enabling
officials of affected small governments
to have meaningful and timely input in
the development of EPA’s regulatory
proposals with significant Federal
intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
The EPA has determined that today’s
notice of reconsideration does not
contain a Federal mandate that may
result in expenditures of $100 million or
more for State, local, and Tribal
governments, in the aggregate, or the
private sector in any 1 year. Today’s
notice of reconsideration of the CAIR
does not add new requirements that
would increase the cost of the CAIR.
Thus, today’s notice of reconsideration
is not subject to the requirements of
sections 202 and 205 of the UMRA. In
addition, EPA has determined that
today’s notice of reconsideration does
not significantly or uniquely affect small
governments because it contains no
requirements that apply to such
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72281
governments or impose obligations
upon them. Therefore, today’s notice of
reconsideration is not subject to section
203 of the UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires 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 action does not have federalism
implications. It would 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. The CAA
establishes the relationship between the
Federal Government and the States, and
this action would not impact that
relationship. Thus, Executive Order
13132 does not apply to this action.
F. 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 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.’’
For the same reasons stated in the
final CAIR, today’s notice does not have
Tribal implications as defined by
Executive Order 13175. It does not have
a substantial direct effect on one or
more Indian Tribes, since no Tribe has
implemented a federally-enforceable air
quality management program under the
CAA at this time. Furthermore, this
action does not affect the relationship or
distribution of power and
responsibilities between the Federal
government and Indian Tribes. The
CAA and the Tribal Air Rule establish
the relationship of the Federal
government and Tribes in developing
plans to attain the NAAQS, and today’s
notice does nothing to modify that
relationship. Because this notice does
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not have Tribal implications, Executive
Order 13175 does not apply.
If one assumes a Tribe is
implementing a Tribal implementation
plan, the CAIR could have implications
for that Tribe, but it would not impose
substantial direct costs upon the Tribe,
nor would it preempt Tribal Law.
Although Executive Order 13175 does
not apply to the CAIR or this notice of
reconsideration of the CAIR, EPA
consulted with Tribal officials in
developing the CAIR.
G. Executive Order 13045: Protection of
Children From Environmental Health
and Safety Risks
Executive Order 13045: ‘‘Protection of
Children From Environmental Health
and Safety Risks’’ (62 FR 19885, April
23, 1997) applies to any rule that (1) is
determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
the Agency must evaluate the
environmental health or safety effects of
the planned rule on children, and
explain why the planned regulation is
preferable to other potentially effective
and reasonably feasible alternatives
considered by the Agency.
This notice is not subject to Executive
Order 13045 because it does not involve
decisions on environmental health risks
or safety risks that may
disproportionately affect children. The
EPA believes that the emissions
reductions from the CAIR will further
improve air quality and children’s
health.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
Executive Order 13211 (66 FR 28355,
May 22, 2001) provides that agencies
shall prepare and submit to the
Administrator of the Office of
Regulatory Affairs, OMB, a Statement of
Energy Effects for certain actions
identified as ‘‘significant energy
actions.’’ Section 4(b) of Executive
Order 13211 defines ‘‘significant energy
actions’’ as ‘‘any action by an agency
(normally published in the Federal
Register) that promulgates or is
VerDate Aug<31>2005
14:49 Dec 01, 2005
Jkt 208001
expected to lead to the promulgation of
a final rule or regulation, including
notices of inquiry, advance notices of
final rulemaking, and notices of final
rulemaking (1)(i) a significant regulatory
action under Executive Order 12866 or
any successor order, and (ii) likely to
have a significant adverse effect on the
supply, distribution, or use of energy; or
(2) designated by the Administrator of
the Office of Information and Regulatory
Affairs as a ‘‘significant energy action.’’
The final CAIR is a significant
regulatory action under Executive Order
12866, and EPA concluded that the final
CAIR rule may have a significant
adverse effect on the supply,
distribution, or use of energy. The
impacts are detailed in the final CAIR
(70 FR 25315). Today’s notice of
reconsideration of the CAIR is not a
significant action under Executive Order
12866 and does not change EPA’s
previous conclusions.
I. National Technology Transfer
Advancement Act
Section 12(d) of the National
Technology Transfer Advancement Act
of 1995, Public Law 104–113, section
12(d) (15 U.S.C. 272 note) directs EPA
to use voluntary consensus standards in
its regulatory activities unless to do so
would be inconsistent with applicable
law or otherwise impractical. Voluntary
consensus standards are technical
standards (e.g., materials specifications,
test methods, sampling procedures, and
business practices) that are developed or
adopted by voluntary consensus
standards bodies. The National
Technology Transfer Advancement Act
of 1995 directs EPA to provide
Congress, through OMB, explanations
when the Agency decides not to use
available and applicable voluntary
consensus standards.
Today’s notice does not involve
technical standards. Therefore, the
National Technology Transfer and
Advancement Act of 1995 does not
apply.
J. Executive Order 12898: Federal
Actions To Address Environmental
Justice in Minority Populations and
Low-Income Populations
Executive Order 12898, ‘‘Federal
Actions to Address Environmental
PO 00000
Frm 00026
Fmt 4702
Sfmt 4702
Justice in Minority Populations and
Low-Income Populations,’’ requires
Federal agencies to consider the impact
of programs, policies, and activities on
minority populations and low-income
populations. According to EPA
guidance,10 agencies are to assess
whether minority or low-income
populations face risks or a rate of
exposure to hazards that are significant
and that ‘‘appreciably exceed or is likely
to appreciably exceed the risk or rate to
the general population or to the
appropriate comparison group.’’ (EPA,
1998).
In accordance with Executive Order
12898, the Agency has considered
whether the CAIR may have
disproportionate negative impacts on
minority or low-income populations.
The EPA expects the CAIR to lead to
reductions in air pollution and
exposures generally. Therefore, EPA
concluded that negative impacts to
these sub-populations that appreciably
exceed similar impacts to the general
population are not expected. For the
same reasons, EPA is drawing the same
conclusion for today’s notice to
reconsider certain aspects of the CAIR.
List of Subjects
40 CFR Part 51
Environmental protection,
Administrative practice and procedure,
Air pollution control, Intergovernmental
relations, Nitrogen dioxide, Ozone,
Particulate matter, Reporting and
recordkeeping requirements, Sulfur
oxides.
40 CFR Part 96
Environmental protection,
Administrative practice and procedure,
Air pollution control, Nitrogen oxides,
Reporting and recordkeeping
requirements.
Dated: November 22, 2005.
Stephen L. Johnson,
Administrator.
[FR Doc. 05–23501 Filed 12–1–05; 8:45 am]
BILLING CODE 6560–50–P
10 U.S. Environmental Protection Agency, 1998.
Guidance for Incorporating Environmental Justice
Concerns in EPA’s NEPA Compliance Analyses.
Office of Federal Activities, Washington, DC, April,
1998.
E:\FR\FM\02DEP1.SGM
02DEP1
Agencies
[Federal Register Volume 70, Number 231 (Friday, December 2, 2005)]
[Proposed Rules]
[Pages 72268-72282]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-23501]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 51 and 96
[OAR 2003-0053; FRL-8003-7]
Rule To Reduce Interstate Transport of Fine Particulate Matter
and Ozone (Clean Air Interstate Rule): Reconsideration
AGENCY: Environmental Protection Agency (EPA).
ACTION: Notice of reconsideration; request for comment; notice of
public hearing.
-----------------------------------------------------------------------
SUMMARY: On May 12, 2005, EPA published in the Federal Register the
final ``Rule to Reduce Interstate Transport of Fine Particulate Matter
and Ozone'' (Clean Air Interstate Rule or CAIR). The CAIR requires
certain upwind States to reduce emissions of nitrogen oxides
(NOX) and/or sulfur dioxide (SO2) that
significantly contribute to nonattainment of, or interfere with
maintenance by,
[[Page 72269]]
downwind States with respect to the fine particle and/or 8-hour ozone
national ambient air quality standards (NAAQS). Subsequently, EPA
received 11 petitions for reconsideration of the final rule. In this
notice, EPA is announcing its decision to reconsider four specific
issues in the CAIR and is requesting comment on those issues.
The EPA is seeking comment only on the aspects of the CAIR
specifically identified in this notice. We will not respond to comments
addressing other provisions of the CAIR or any related rulemakings.
DATES: Comments must be received on or before January 13, 2006. A
public hearing will be held on December 14, 2005 in Washington, DC. For
additional information on the public hearing, see the SUPPLEMENTARY
INFORMATION section of this preamble.
ADDRESSES: Submit your comments, identified by Docket ID No. OAR-2003-
0053, by one of the following methods:
Federal Rulemaking Portal: https://www.regulations.gov.
Follow the on-line instructions for submitting comments. Attention E-
Docket No. OAR-2003-0053.
Agency Web site: https://www.epa.gov/edocket. EDOCKET,
EPA's electronic public docket and comment system, is EPA's preferred
method for receiving comments. Follow the on-line instructions for
submitting comments. Attention E-Docket No. OAR-2003-0053.
E-mail: A-and-R-Docket@epa.gov. Attention E-Docket No.
OAR-2003-0053.
Fax: The fax number of the Air Docket is (202) 566-1741.
Attention E-Docket No. OAR-2003-0053.
Mail: EPA Docket Center, EPA West (Air Docket), Attention
E-Docket No. OAR-2003-0053, Environmental Protection Agency, Mail Code:
6102T, 1200 Pennsylvania Ave., NW., Washington, DC 20460.
Hand Delivery: EPA Docket Center (Air Docket), Attention
E-Docket No. OAR-2003-0053, Environmental Protection Agency, 1301
Constitution Avenue, NW., Room B102, Washington, DC. Such deliveries
are only accepted during the Docket's normal hours of operation, and
special arrangements should be made for deliveries of boxed
information.
Instructions: Direct your comments to Docket ID No. OAR-2003-0053.
The EPA's policy is that all comments received will be included in the
public docket without change and may be made available on-line at
https://www.epa.gov/edocket, 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 EDOCKET,
regulations.gov, or e-mail. (For instructions on submitting CBI, see
below under SUPPLEMENTARY INFORMATION.)
The EPA EDOCKET and the Federal regulations.gov Web sites are
``anonymous access'' systems, which means EPA will not know your
identity or contact information unless you provide it in the body of
your comment. If you send an e-mail comment directly to EPA without
going through EDOCKET or regulations.gov, your e-mail 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, 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 EPA cannot read your comment due to
technical difficulties and cannot contact you for clarification, EPA
may not be able to consider your comment. Electronic files should avoid
the use of special characters, any form of encryption, and be free of
any defects or viruses. For additional information about EPA's public
docket visit EDOCKET on-line or see the Federal Register of May 31,
2002 (67 FR 38102). For additional information on submitting comments,
go to the SUPPLEMENTARY INFORMATION section of this document.
Docket: All documents in the docket are listed in the EDOCKET index
at https://www.epa.gov/edocket. Although listed in the index, some
information is not publicly available, i.e., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically in EDOCKET or in hard
copy at the EPA Docket Center (Air Docket), EPA/DC, EPA West, Room
B102, 1301 Constitution Ave., NW., Washington, DC. The 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) 566-1742 and the fax number is (202) 566-1741.
FOR FURTHER INFORMATION CONTACT: For general questions concerning
today's action, please contact Carla Oldham, U.S. EPA, Office of Air
Quality Planning and Standards, Air Quality Strategies and Standards
Division, Mail Code C539-02, Research Triangle Park, NC 27711, phone
number (919) 541-3347, e-mail addressoldham.carla@epa.gov. For
questions concerning the analyses described in section III of this
notice, please contact Chitra Kumar, U.S. EPA, Office of Atmospheric
Programs, Clean Air Markets Division, Mail Code 6204J, 1200
Pennsylvania Avenue, NW., Washington, DC 20460, telephone (202) 343-
9128, e-mail address kumar.chitra@epa.gov. For legal questions, please
contact Sonja Rodman, U.S. EPA, Office of General Counsel, Mail Code
2344A, 1200 Pennsylvania Avenue, NW., Washington, DC 20460, telephone
202-564-4079, e-mail address rodman.sonja@epa.gov.
For information concerning the public hearing, please contact Jo
Ann Allman, U.S. EPA, Office of Air Quality Planning and Standards, Air
Quality Strategies and Standards Division, Mail Code C539-02, Research
Triangle Park, NC 27711, phone number (919) 541-1815, e-mail address
allman.joann@epa.gov.
SUPPLEMENTARY INFORMATION:
Does This Action Apply to Me?
The CAIR does not directly regulate emissions sources. Instead, it
requires States to develop, adopt, and submit SIP revisions that would
achieve the necessary SO2 and NOX emissions
reductions, and leaves to the States the task of determining how to
obtain those reductions, including which entities to regulate.
Public Hearing. On December 14, 2005, EPA will hold a public
hearing on today's notice at EPA Headquarters, 1310 L Street (closest
cross street is 13th Street), 1st floor conference rooms 152 and 154,
Washington, DC. The closest Metro stop is McPherson Square (Orange and
Blue lines)--take 14th Street/Franklin Square Exit. Because the hearing
will be held at a U.S. government facility, everyone planning to attend
should be prepared to show valid picture identification to the security
staff in order to gain access to the meeting room.
The hearing will begin at 9 a.m. and end at 12 noon. Persons
wishing to speak at the public hearing should contact Jo Ann Allman by
December 9 at telephone number (919) 541-1815 or by e-mail at
allman.joann@epa.gov. The hearing will be limited to the subject matter
of this document. Oral testimony will be limited to 5 minutes. The EPA
encourages commenters to provide
[[Page 72270]]
written versions of their oral testimonies either electronically (on
computer disk or CD-ROM) or in paper copy. The public hearing schedule,
including the list of speakers, will be posted on EPA's Web site at:
www.epa.gov/cair. Verbatim transcripts and written statements will be
included in the rulemaking docket.
The public hearings will provide interested parties the opportunity
to present data, views, or arguments concerning the proposed rules. The
EPA may ask clarifying questions during the oral presentations, but
will not respond to the presentations or comments at that time. Written
statements and supporting information submitted during the comment
period will be considered with the same weight as any oral comments and
supporting information presented at a public hearing.
Because of the need to resolve the issues in this document in a
timely manner, EPA will not grant requests for extensions of the public
comment period.
What Should I Consider as I Prepare My Comments for EPA?
Note that general instructions for submitting comments are provided
above under the ADDRESSES section.
Submitting CBI. Do not submit comments that include CBI to EPA
through EDOCKET, regulations.gov or e-mail. Clearly mark the part or
all of the information that you claim to be CBI. For CBI information in
a disk or CD ROM that you mail to 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 so marked will not be disclosed except in accordance with
procedures set forth in 40 CFR part 2. Send or deliver information
identified as CBI only to the following address: Roberto Morales, U.S.
EPA, Office of Air Quality Planning and Standards, Mail Code C404-02,
Research Triangle Park, NC 27711, telephone (919) 541-0880, e-mail at
morales.roberto@epa.gov, Attention Docket ID No. OAR-2003-0053.
Tips for Preparing Your Comments. When submitting comments,
remember to:
i. Identify the rulemaking by docket number and other identifying
information (subject heading, Federal Register date and page number).
ii. Follow directions--The agency may ask you to respond to
specific questions or organize comments by referencing a Code of
Federal Regulations (CFR) part or section number.
iii. Explain why you agree or disagree; suggest alternatives and
substitute language for your requested changes.
iv. Describe any assumptions and provide any technical information
and/or data that you used.
v. If you estimate potential costs or burdens, explain how you
arrived at your estimate in sufficient detail to allow for it to be
reproduced.
vi. Provide specific examples to illustrate your concerns, and
suggest alternatives.
vii. Explain your views as clearly as possible, avoiding the use of
profanity or personal threats.
viii. Make sure to submit your comments by the comment period
deadline identified.
Availability of Related Information
Documents related to the CAIR are available for inspection in
docket OAR-2003-0053 at the address and times given above. The EPA has
established a Web site for the CAIR at https://www.epa.gov/
cleanairinterstaterule or more simply https://www.epa.gov/cair/.
Outline
I. Background
II. Today's Action
A. Grant of Reconsideration
B. Schedule for Reconsideration
III. Discussion of Issues
A. SO2 Allocation Methodology in the CAIR Model
Trading Rules
B. Fuel Adjustment Factors Used To Set State NOX
Budgets
C. PM2.5 Modeling for Minnesota
D. Inclusion of Florida in the CAIR Region for Ozone
IV. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination With
Indian Tribal Governments
G. Executive Order 13045: Protection of Children From
Environmental Health and Safety Risks
H. Executive Order 13211: Actions That Significantly Affect
Energy Supply, Distribution or Use
I. National Technology Transfer Advancement Act
J. Executive Order 12898: Federal Actions To Address
Environmental Justice in Minority Populations and Low Income
Populations
I. Background
On May 12, 2005, the EPA (Agency or we) promulgated the final
``Rule to Reduce Interstate Transport of Fine Particulate Matter and
Ozone'' (Clean Air Interstate Rule or CAIR) (70 FR 25162). In this
action, EPA found that 28 States and the District of Columbia
contribute significantly to nonattainment of, or interfere with
maintenance by, downwind States with respect to the NAAQS for fine
particles (PM2.5) and/or 8-hour ozone. The CAIR requires
these upwind States to revise their State implementation plans (SIPs)
to include control measures to reduce emissions of SO2 and/
or NOX. Sulfur dioxide is a precursor to PM2.5
formation and NOX is a precursor to PM2.5 and
ozone formation. By reducing upwind emissions of SO2 and
NOX, CAIR will assist downwind PM2.5 and 8-hour
ozone nonattainment areas in achieving the NAAQS.
The EPA promulgated the CAIR based on the ``good neighbor''
provision of the Clean Air Act (CAA), section 110(a)(2)(D), which
establishes State obligations to address interstate transport of
pollution. The EPA conducted extensive air modeling to determine the
extent to which emissions from certain upwind States were impacting
downwind nonattainment areas. All States found to contribute
significantly to downwind PM2.5 nonattainment or maintenance
problems are included in the CAIR region for PM2.5 and are
required to reduce annual emissions of SO2 and
NOX. All States found to contribute significantly to
downwind 8-hour ozone nonattainment are included in the CAIR region for
ozone and required to reduce NOX emissions during the 5-
month ozone season (May-September). The CAIR establishes regional
emission reduction requirements for annual SO2 and
NOX emissions and seasonal NOX emissions. The
reduction requirements are based on control technologies known to be
highly cost effective for electric generating units (EGUs). The first
phase of NOX reductions starts in 2009 (covering 2009-2014)
and the first phase of SO2 reductions starts in 2010
(covering 2010-2014). The second phase of both SO2 and
NOX reductions starts in 2015 (covering 2015 and
thereafter).
Each State covered by CAIR may independently determine which
emission sources to control, and which control measures to adopt.
States that choose to base their programs on emissions reductions from
EGUs may allow their EGUs to participate in an EPA-administered cap and
trade program. The CAIR includes model
[[Page 72271]]
rules for multi-State cap and trade programs for annual SO2
and NOX emissions, and seasonal NOX emissions.
States may choose to adopt these rules to meet the required emissions
reductions in a flexible and highly cost-effective manner. To learn
more about the CAIR and its impacts, the reader is encouraged to read
the preamble to the CAIR (70 FR 25162; May 10, 2005).
The CAIR was promulgated through a process that involved
significant public participation. The EPA published a notice of
proposed rulemaking on January 30, 2004 (69 FR 4566) and a notice of
supplemental rulemaking on June 10, 2004 (69 FR 32684). The EPA also
published a notice of data availability on August 6, 2004 (69 FR
47828). The Agency held public hearings on the January 2004 proposed
rule on February 25 and 26, 2004, and an additional hearing on the
supplemental proposal on June 3, 2004. In addition, the EPA received
thousands of comments on the proposals. We responded to all significant
public comments in the preamble to the final rule and the final
response to comments document available in the CAIR docket (Docket No.
OAR-2003-0053-2172).
Following publication of the final rule on May 12, 2005, the
Administrator received eleven petitions requesting reconsideration of
certain aspects of the final CAIR. These petitions were filed pursuant
to section 307(d)(7)(B) of the CAA. Under this provision, the
Administrator is to initiate reconsideration proceedings if the
petitioner can show that an objection is of central relevance to the
rule and that it was impracticable to raise the objection to the rule
within the public comment period or that the grounds for the objection
arose after the public comment period but before the time for judicial
review had run. The petitions for reconsideration of the CAIR ask EPA
to reconsider several specific aspects of the final rule, and many of
the petitions make similar requests. This notice addresses four of the
issues raised in those petitions. The EPA expects to issue decisions on
all remaining issues raised in the petitions for reconsideration by
March 15, 2006. The complete petitions are available in the docket for
the CAIR.\1\
---------------------------------------------------------------------------
\1\ Petitions for reconsideration were filed by: State of North
Carolina (OAR-2003-0053-2192); FPL Group OAR-2003-0053-2201);
Florida Association of Electric Utilities (OAR-2003-0053-2200);
Entergy Corporation (OAR-2003-0053-2195 and 2198 (attachment 1));
Massachusetts Department of Environmental Protection (OAR-2003-0053-
2199); Integrated Waste Services Association (OAR-2003-0053-2193);
Texas Commision on Environmental Quality (OAR-2003-0053-2212);
Northern Indiana Public Service Corporation (OAR-2003-0053-2194 and
2213 (supplemental petition)); City of Amarillo, Texas, El Paso
Electric Company, Occidental Permian Ltd, and Southwestern Public
Service Company d/b/a/ Xcel Energy (OAR-2003-0053-2196 and 2197
(attachment 1) and 2205-2207 (attachments 2-4)); Connecticut
Business and Industry Ass'n (OAR-2003-0053-2203); and Minnesota
Power, a division of ALLETE. Inc. (OAR-2003-0053-2212).
---------------------------------------------------------------------------
In addition, fourteen petitions for judicial review of the final
rule were filed with the U.S. Court of Appeals for the District of
Columbia.\2\ The fourteen cases have been consolidated into a single
case, State of North Carolina v. EPA (No. 05-1244) (D.C. Cir). Many of
the parties who petitioned EPA for reconsideration of the CAIR also
petitioned for judicial review of the rule.
---------------------------------------------------------------------------
\2\ State of North Carolina v. EPA (No. 05-1244); Minnesota
Power v. EPA (No. 05-1246); ARIPPA v. EPA (No. 05-1249); South
Carolina Public Service Authority et al. v. EPA (No. 05-1250);
Entergy Corp. v. EPA (No. 05-1251); Florida Ass'n of Electric
Utilities (No. 05-1252); FPL Group v. EPA (No. 05-1253); Northern
Indiana Public Service Co. v. EPA (No. 05-1254); South Carolina
Electric & Gas Co. v. EPA (No. 05-1256); Integrated Waste Services
Ass'n v. EPA (No. 05-1257); AES Corp v. EPA (No. 05-1259); City of
Amarillo, Texas et al. v. EPA (No. 05-1260); Appalachian Mountain
Club et al. v. EPA (No. 05-1246); Duke Energy v. EPA (No. 05-1246).
---------------------------------------------------------------------------
By letters dated August 1, 2005, EPA granted reconsideration of the
definition of ``electric generating unit'' or ``EGU'' as it relates to
solid waste incinerators (and particularly municipal waste
incinerators).\3\ The EPA explained that the issue would be addressed
in the proposed rule signed the same day. That proposed rule, entitled
``Rulemaking on Section 126 Petition from North Carolina to Reduce
Interstate Transport of Fine Particulate Matter and Ozone; Federal
Implementation Plans to Reduce Interstate Transport of Fine Particulate
Matter and Ozone; Revisions to the Clean Air Interstate Rule; Revisions
to the Acid Rain Program; Proposed Rule,'' was published on August 24,
2005 (70 FR 49708). In that proposed rule, EPA reconsidered the
definition of ``EGU'' in the final CAIR as it relates to solid waste
incinerators (70 FR 49738). We proposed revisions to the definition of
``EGU'' and requested comment on this issue. In that action, we did not
address any other issues raised in the petitions for reconsideration of
the CAIR. Today's action does not reopen for comment any aspect of the
August 24, 2005, proposed rule.
---------------------------------------------------------------------------
\3\ These letters are available in the CAIR Docket. (OAR-2003-
0053-2209 and 2210).
---------------------------------------------------------------------------
The EPA also received two requests to stay the implementation of
the CAIR in limited geographic areas pending resolution of this
reconsideration process. One petitioner requested a stay of
implementation of the CAIR in the State of Florida, and one petitioner
requested a stay of implementation of the CAIR in the State of
Minnesota. By letter dated August 1, 2005, EPA declined to stay
implementation of the CAIR in Florida.\4\ The EPA has not yet acted on
the request to stay implementation of the CAIR in Minnesota.
---------------------------------------------------------------------------
\4\ This letter is also available in the CAIR Docket (OAR-2003-
0053-2208).
---------------------------------------------------------------------------
By letters dated November 21, 2005, we informed several petitioners
of our intent to grant reconsideration on one or more issues addressed
in their petitions for reconsideration. We indicated in those letters
that we would initiate the reconsideration process by publishing this
notice.
II. Today's Action
A. Grant of Reconsideration
In this notice, EPA is announcing its decision to grant
reconsideration on four issues raised in the petitions for
reconsideration. This notice initiates that reconsideration process and
requests comment on the issues to be addressed. Given the intense
public interest in this rule, EPA has decided to provide this
additional opportunity for public comment. At this time, however, EPA
does not believe that any of the information submitted to date
demonstrates that EPA's final decisions were erroneous or
inappropriate. Therefore, we are not proposing any modifications to the
final CAIR.
The first issue on which EPA is requesting comment relates to
analysis done by EPA to address petitioner's claims regarding alleged
inequities resulting from the application of the SO2
allowance allocation methodology that States choosing to participate in
the trading program would use to allocate SO2 allowances to
sources. The second issue relates to EPA's use of specific fuel
adjustment factors to establish NOX budgets for each State.
The third issue relates to modeling inputs used by EPA to determine
whether emissions from Minnesota should be included in the CAIR region
for PM2.5. And the fourth issue relates to EPA's
determination that the State of Florida should be included in the CAIR
region for ozone. Each issue is described in greater detail in Section
III of this notice.
The EPA is requesting comment only on the issues specifically
described in Section III. We are not taking comment on any other
provisions in the CAIR or otherwise reopening any other issues decided
in the CAIR for reconsideration or comment.
[[Page 72272]]
B. Schedule for Reconsideration
For the four issues addressed in this notice, EPA expects to take
final action on reconsideration by March 15, 2006. By that date, EPA
will finalize the process of reconsideration by issuing a final rule or
proposing a new approach. EPA also expects, by March 15, 2006, to issue
decisions on all remaining issues raised in the petitions for
reconsideration.
III. Discussion of Issues
A. SO2 Allocation Methodology in the CAIR Model Trading
Rules
One petitioner argues that the SO2 allowance allocation
methodology in the CAIR model trading rules is unreasonable and
inequitable, and asks EPA to establish a different approach. According
to the petitioner, the methodology is inequitable because it results in
owners of units that have lower emission rates, historically, buying
allowances from historically higher emitting units that install new
emission controls. EPA does not accept the petitioner's
characterization of this issue. EPA continues to believe that the
methodology selected is reasonable for the reasons explained in the
final rule and further outlined below. Furthermore, numerous
opportunities for public comment on this issue were provided, and a
full discussion of the allowance allocation options occurred during the
rule development process. Nonetheless, given the intense public
interest in this issue, EPA has decided to grant the Petition for
Reconsideration insofar as it raises issues regarding alleged
inequities resulting from the application of the SO2
allowance allocation.
As explained below, EPA has conducted additional analyses
concerning the impact of the SO2 allowance allocation
approach adopted in the model rules, comparing this approach to various
other alternatives considered during the rulemaking process. These
analyses further illustrate that the approach selected produces a
reasonable result, not the inequities alleged in the Petition for
Reconsideration. Therefore EPA is not proposing any changes to the CAIR
SO2 allocation approach as part of this reconsideration
notice. We are taking comment on the analyses conducted and our
discussion of the petitioner's concerns.
Title IV and CAIR
The CAIR model SO2 trading program relies on the use of
title IV SO2 allowances for compliance with the allowance-
holding requirements of CAIR. Title IV SO2 allowances have
already been allocated on a unit-by-unit basis in perpetuity, based on
formulas set forth in section 405 and 406 of title IV, which were
implemented through final regulations issued in 1998 (Sec 42 U.S.C.
7651d and 7651e; and 18 CFR 73.10(b)). The statutory formula for
SO2 allocations was generally based on unit data for 1985-
1987 and, for some units, data for years up to 1995. For the title IV
SO2 trading program, each allowance authorizes one ton of
SO2 emissions.
For the CAIR SO2 trading program, SO2
reductions would be achieved by generally requiring CAIR sources to
retire more than one title IV allowance for each ton of their
SO2 emissions for 2010 and thereafter. Specifically, each
title IV SO2 allowance issued for 2009 or earlier would be
used for compliance by CAIR sources at a ratio of one allowance per ton
of SO2 emissions and would authorize one ton of
SO2 emissions. Each title IV allowance of vintage 2010
through 2014 would be used for compliance under CAIR at a two-to-one
ratio and authorize 0.5 tons of SO2 emissions. Each title IV
allowance of vintage 2015 and later would be used at a 2.86-to-1 ratio
and authorize 0.35 tons of SO2 emissions. See discussion in
the preamble to the final CAIR in section VII (70 FR 25255-25273) and
section IX (70 FR 25290-25291).
SO2 Allocation Options in CAIR
A variety of SO2 allowance allocation methodologies were
raised and analyzed during the rulemaking process, including the one
EPA selected. Alternative methodologies analyzed included allocating on
the basis of historic tonnage emissions, heat input (with alternatives
based on heat input from all fossil generation, and heat input from
coal- and oil-fired generation only) and output (with alternatives
based on all generation and all fossil-fired generation). While every
allocation methodology suggested by commenters during the rulemaking
process has its advantages and disadvantages for different companies
and States, EPA explained in the final rule that its chosen methodology
is reasonable on several grounds. First, EPA believes that ``achieving
SO2 reductions for EGUs using the title IV allowances is
necessary in order to ensure the preservation of a viable title IV
program'' (Response to Comments (RTC) at page 511, section X.A.26,
2005). See also discussion in preamble to the final CAIR in section IX
(70 FR 25290-25291). Second, in using the title IV allowances, EPA
relied on the selection by Congress of the permanent allocation
methodology established in title IV for purposes of reducing
SO2 emissions. As stated in the RTC (page 512), ``Congress
clearly did not choose a policy to regularly revisit and revise these
allocations, believing that its allocations methodology for title IV
allowances would be appropriate for future time periods.''
Third, title IV allowance allocations provide a logical and well
understood starting point from which additional EGU SO2
emission reductions can be achieved for Acid Rain units, which account
for over 90% of the SO2 emissions from CAIR EGUs. Finally,
EPA's State-by-State analysis of several methods for SO2
allocations shows that the use of title IV allowances to develop state
budgets creates a reasonable result (See RTC, section X.A.26). The
policy decision to base the CAIR SO2 budgets on the existing
title IV allowance system, and EPA's demonstration that the result of
using the system is reasonable fully support the use of an allocation
system based on title IV allowances.
Analysis of SO2 Allocation Options
As a part of this reconsideration, EPA performed additional
analyses, explained below, to evaluate the SO2 allocation
methodology in the final CAIR rule in light of the petitioner's
concerns. In these analyses, EPA compared three alternative
SO2 allowance allocation methodologies to the methodology in
the final CAIR to see how companies fared in terms of the amount of
allowances allocated relative to their projected SO2
emissions. The allocation allowance methodologies evaluated by EPA were
the ones referred to by the petitioner in the Petition for
Reconsideration. EPA believes that, for purposes of evaluating the
various allocation methodologies, computing allocations on a company-
by-company basis is more appropriate than comparing allocations on a
unit-by-unit basis. This is because, while one unit could be allocated
fewer allowances under one methodology, another unit owned by the same
company could be allocated more allowances, which may offset the
smaller allocation of the first unit.
The three alternative allowance allocation methodologies EPA
analyzed were suggested by various commenters during the rulemaking
process. Also note that methodologies 2 and 3 were suggested by the
petitioner. These methodologies are:
1. Allocating allowances based on more recent heat input data;
[[Page 72273]]
2. Allocating allowances based on more recent heat input data
adjusted for fuel type (e.g., coal, oil and gas);
3. Allocating allowances based on more recent heat input data
adjusted both for fuel type (e.g., coal, oil and gas) and for coal type
(e.g., bituminous, sub-bituminous and lignite).
In comparing the CAIR final SO2 allocation methodology
and the three alternative methodologies, EPA took into account certain
factors that are applicable to the CAIR final allocation methodology
but not to the three alternative methodologies. For all four
methodologies, EPA analyzed the resulting total allowance allocations,
and the total projected emissions, for companies' sources located in
the States subject to CAIR. In addition, for all the methodologies, EPA
analyzed the relationship between allowances and emissions in two ways.
In the first, EPA calculated the ratio of allowances to total projected
emissions before CAIR controls (base case). This measures how much each
company falls short of allowance needs. Then, in the second approach,
EPA calculated the ratio of allowances to total projected emissions
with CAIR controls installed (control case). This way measures how many
allowances a company would need to purchase after controls are
installed.
For the CAIR final methodology, EPA also considered both the
allowance allocations and emissions for companies' sources both in the
CAIR region and outside the CAIR region. EPA believes that this is
appropriate because, under the CAIR final methodology, if a company's
sources outside the CAIR region have more title IV allowances than
needed to cover their emissions under the Acid Rain Program, the
company could transfer, at little or no net cost, excess allowances to
the company's sources in the CAIR region for use to cover emissions
under the CAIR trading program. Under the three alternative
methodologies, which would require creating new CAIR SO2
allowances independent of the existing title IV allocations, CAIR
sources could not use title IV for compliance with the CAIR
SO2 allowance holding requirements.
Further, in the analysis of the CAIR final methodology, EPA
considered the allocation of title IV allowances to CAIR region units
that are not currently in the Acid Rain Program but that could opt into
the Acid Rain Program and receive title IV allowances (see 42 U.S.C.
7651i and 18 CFR part 74). This analysis assumed that companies owning
non-Acid Rain units affected by CAIR would opt into the Acid Rain
Program because they would receive title IV allowances to cover a
portion of the unit's emissions under CAIR. EPA believes this
assumption is reasonable because there is very little cost associated
with opting into the Acid Rain Program.\5\ In contrast, the analysis of
the three alternative methodologies did not consider Acid Rain Program
opt-in allowances because these approaches do not use title IV
allowances for CAIR compliance.
---------------------------------------------------------------------------
\5\ The greatest cost associating with opting in to the title IV
program is the cost of monitoring. Since these sources are already
required to monitor using the same monitoring methodologies that
would be required if they were to opt in, their costs for opting in
are significantly reduced.
---------------------------------------------------------------------------
EPA's analyses, of which a detailed description is available in the
docket, encompassed 112 (control case) to 114 (base case) parent/
holding companies with sources covered by the CAIR. These 112 to 114
companies represent about two-thirds of the total number of CAIR
plants, over 95 percent of total annual allocations for all
methodologies during 2015, and about 97 percent of the total projected
emissions in the CAIR region in 2015.\6\
---------------------------------------------------------------------------
\6\ According to EPA inventory data, there are a total of 921
CAIR affected plants. EPA did not have complete owner, parent
company information for all of these plants.
---------------------------------------------------------------------------
While allocations vary from company to company under the four
methodologies, overall, the distributions of allowances that companies
received relative to their projected emissions for both the base case
and control case are very similar. In other words, no methodology
stands out as providing a more reasonable method of allocation across
all companies when examining allowance needs under either the base case
or control case. Figures 1 and 2, below, show the distribution of
values for each methodology under the two cases, and support this
conclusion. EPA repeated these analyses for 2010, which show similar
results. Separate analyses of owner/operating company allowances
compared to emissions in 2010 and 2015, show similar results, as well.
See TSD Memo, ``Technical Support Document for Clean Air Interstate
Rule Response to Petition for Reconsideration.''
BILLING CODE 6560-50-P
[[Page 72274]]
[GRAPHIC] [TIFF OMITTED] TP02DE05.037
[[Page 72275]]
[GRAPHIC] [TIFF OMITTED] TP02DE05.038
BILLING CODE 6560-50-C
[[Page 72276]]
EPA also notes that, while the Petitioner states that the CAIR
final allocation methodology is ``inequitable'' because lower emitting
units would buy allowances from higher emitting units that install
emission controls, it is unclear why such a result would actually be
inequitable. On the contrary, the owner of each of the units involved
would be choosing to adopt the most economic compliance strategy in
light of the unit's emission control costs and the market value of
allowances. The ability of the owners to make such choices reflects the
flexibility provided by a cap and trade program.
The EPA requests comment on its analyses of the four allocation
methodologies and on the above discussion of the Petitioner's concerns.
B. Fuel Adjustment Factors Used To Set State NOX Budgets
Several petitioners argue the Agency did not provide adequate
notice regarding the use of specific fuel adjustment factors to
establish NOX budgets for States in the CAIR region. As
explained below, EPA believes that it provided adequate notice both
that the fuel adjustment factors might be used and of the calculation
procedures that it would use to determine the specific factors.
Nevertheless, given the significant public interest in this issue, EPA
has decided to grant reconsideration of, and to take comment on, EPA's
use of fuel adjustment factors (i.e., 1.0 for coal, 0.4 for gas, and
0.6 for fuel oil) in setting State NOX budgets. Today's
action also presents additional analysis that EPA conducted to further
explain the impact of these factors on State annual NOX
budgets. This analysis demonstrates that the factors selected are
reasonable and decrease the disparity between most States' actual
electric generation unit (EGU) emissions and their State NOX
budgets. For that reason, EPA is not proposing any changes to the final
CAIR at this time.
The CAIR establishes regional emission budgets for annual
NOX, and seasonal NOX emissions. These regional
budgets are then further divided into State budgets, with a share of
each total regional budget allocated to each State in the corresponding
CAIR region. States choosing to participate in the trading programs
will be able to allocate, to sources in their State, the number of
allowances in their budgets. Petitioners challenge the methodology EPA
used to establish these State budgets for annual and seasonal
NOX.
Background
For States choosing to participate in the trading program, these
budgets determine the number of allowances that could be allocated to
sources in that State. In a cap and trade system, however, the
methodology used to allocate allowances in any given year would not
affect where control technologies are installed.\7\ Rather, the
determinant would be the cost of adding controls compared to the cost
of buying, or the profit from selling, allowances. Controls are
expected to be installed where it is relatively less expensive, without
regard to which units received the initial allocation of allowances.
Further, the total cost to industry of controlling emissions and the
total amount of reductions achieved would not be affected by the
allocation methodology in a given year (for a permanent system). The
allocation method, however, could have financial impacts on individual
units and companies. A unit that receives more allocations than it has
emissions would get a benefit at the expense of a unit that does not
receive enough allocations to cover its emissions. While States
choosing to participate in the cap and trade program can determine how
to allocate allowances among their units, companies in States whose
budgets exceed projected EGU emissions would likely receive a financial
benefit while companies in States whose budgets are lower than their
EGU emissions would likely incur additional costs. In the absence of
other considerations, EPA believes that it is in the public interest to
reduce the disparity between the number of allowances in a State budget
and total projected State EGU emissions.
---------------------------------------------------------------------------
\7\ A permanent allocation approach, such as the CAIR allocation
methodology in the model trading rules, should not affect where
controls are installed. This is true regardless of the type of
approach used to permanently allocate allowances (e.g., heat input,
adjusted heat input, or output). The use of an updating allocation
system, on the other hand, could impact future generation behavior.
---------------------------------------------------------------------------
Notice of Fuel Factor Use in CAIR Promulgation
In the CAIR notice of proposed rulemaking (NPR), EPA proposed to
use the simple heat input method. (69 FR 4566) This approach used the
un-adjusted heat input to set budgets based on heat input data from the
years 1999 through 2002. EPA proposed to give each State a pro rata
share of the regional NOX budget based on the ratio of its
average annual heat input to the regional total average annual heat
input.
In the Supplemental Notice of Proposed Rulemaking (SNPR), EPA
proposed to supplement and update the data used to calculate the State
annual NOX budgets (69 FR 32684). EPA also described an
alternative method that could be used to calculate the budgets--the
adjusted heat input (fuel factor) method. This approach, EPA explained,
would ``* * * reflect the inherently higher emissions rate of coal-
fired plants, and consequently the greater burden on coal plants to
control emissions.'' (See 69 FR 32689.) The SNPR further explains ``in
contrast to allocations based on historic emissions, the factors would
also not penalize coal-fired plants that have already installed
pollution controls'' (69 FR 32689). In the SNPR, EPA also described the
method that it would use to derive specific fuel factors if this
adjusted heat input method was selected. EPA explained, ``States'
shares would be determined by the amount of the State heat input, as
adjusted, in proportion to the total regional heat input. The factors
could be based on average historic emissions rates (in lbs/mmBtu) by
fuel type (coal, gas, and oil) for the years 1999-2002'' (69 FR 32689).
The SNPR did not identify the specific numeric factors that would be
used. EPA received and responded to numerous comments addressing this
alternative fuel factor approach. (See ``Corrected Response to
Significant Public Comments on the Proposed Clean Air Interstate
Rule,'' pp. 520-576.)
EPA established State NOX budgets for the final CAIR
using the adjusted heat input method. The specific fuel factors used to
adjust heat input data were 1.0 for coal, 0.4 for gas and 0.6 for oil.
These factors are based on the average historic NOX
emissions rate for each fuel. They reflect for each fuel, the 1999-2002
average emissions by State summed for the CAIR region, divided by
average heat input by fuel by State, summed for the CAIR region (70 FR
25230-25231).
EPA Analyses of Potential Impacts
EPA conducted two analyses to evaluate the potential impact of
using the adjusted heat input method versus the simple heat input
method on State annual NOX budgets: one on a regionwide
scale and the second on a State-by-State level.
The regionwide analysis of the potential impacts compared
regionwide budgets using both approaches (i.e. simple heat input and
fuel factor) to the regionwide projected emissions of units fired with
that fuel.\8\ Regional budgets and emissions, by fuel type, are
summarized in Table 1.
---------------------------------------------------------------------------
\8\ It should be noted that simple heat input or adjusted heat
input are used to set State budgets and do not imply that States
would allocate allowances to units in that manner. In the proposal,
EPA gives States flexibility in the distribution of allowances.
[[Page 72277]]
Table 1.--Regionwide Comparison of CAIR Allowance Distributions and Emissions by Fuel Type
[Thousand tons]
----------------------------------------------------------------------------------------------------------------
Projected 2009* emissions and Projected 2015 emissions and
allowances allowances
-----------------------------------------------------------------
Other Other
Coal fossil** Total Coal fossil Total
----------------------------------------------------------------------------------------------------------------
Base Case Emissions........................... 2,635 97 2,732 2,650 96 2,746
CAIR Emissions................................ 1,404 99 1,503 1,151 89 1,254
Simple Heat Input Allowances.................. 1,197 308 1,505 998 256 1,254
Fuel Factor Adjusted Allowances............... 1,349 156 1,505 1,124 130 1,254
----------------------------------------------------------------------------------------------------------------
* Numeric value is based on 2010 projections.
** Numeric value includes wood and refuse in three States.
Assuming allowancesare often passed through to generation units in
the same way that they are apportioned to the States, Table 1
illustrates that under either approach natural gas-fired and other non-
coal-fired generation receives more allowances than their projected
emissions in both 2009 and 2015 and therefore States with more units of
this type receive a greater share of the budget. However, using the
fuel factor approach, the disparity between the number of allowances
provided and the emissions is less than under the simple heat input
method. Table 1 also demonstrates that the majority of emission
reductions are made by coal-fired sources. States with more of these
types of units receive a greater share of the regional budget under the
fuel factor approach (however, the portion of the budget derived from
the heat input from these units is still generally smaller than their
projected emissions). Therefore, the fuel factor approach generally
provides additional allowances to States with large amounts of coal-
fired units that are making the investments in emission control
measures and technologies. Conversely the simple heat input approach
provides more allowances to States with larger amounts of gas-fired
units that are not making reductions. Note that under either approach
the portion of the State budgets derived from the heat input from the
gas-fired units generally exceeds both the historical and the future
projected emissions from these units. This finding led EPA to believe
that the fuel factor approach better reduced the disparity between
projected emissions and State budgets.
EPA conducted a second analysis that examined the potential impacts
of the two approaches for developing Statewide budgets (i.e., simple
heat input and fuel factor) on a State-by-State basis. This analysis,
summarized in Tables 2 and 3 below, shows that States receiving fewer
allowances using a fuel factor approach, generally still receive
Statewide budgets that are greater than their projected emissions in
2009 and 2015. This results because a substantial portion of their
generation portfolio consists of gas-fired sources with generally low
NOX emission levels.
Table 2.--Comparison of Projected NOX Missions and State Budgets for CAIR States Not Dominated by Coal
Generation
[Thousand tons]
----------------------------------------------------------------------------------------------------------------
Projected 2009 * emissions and Projected 2015 emissions and
budgets budgets
State -----------------------------------------------------------------
Other Other
Coal fossil Total Coal fossil Total
----------------------------------------------------------------------------------------------------------------
DC **................ Base Case Emissions.... 0 0 0 0 <1 <1
CAIR Emissions......... 0 <1 <1 0 <1 <1
Simple Heat Input 0 <1 <1 0 <1 <1
Budget.
Fuel Factor Adjusted 0 <1 <1 0 <1 <1
Budget.
LA................... Base Case Emissions.... 45 5 49 45 5 50
CAIR Emissions......... 30 4 35 27 5 32
Simple Heat Input 19 23 42 16 26 42
Budget.
Fuel Factor Adjusted 21 14 36 18 12 30
Budget.
NY................... Base Case Emissions.... 38 7 45 38 6 44
CAIR Emissions......... 29 7 36 15 6 21
Simple Heat Input 19 42 61 16 35 51
Budget.
Fuel Factor Adjusted 21 25 46 17 21 38
Budget.
TX................... Base Case Emissions.... 141 45 186 141 39 179
CAIR Emissions......... 122 44 166 122 35 157
Simple Heat Input 114 118 231 95 98 192
Budget.
Fuel Factor Adjusted 128 53 181 106 44 151
Budget.
MS................... Base Case Emissions.... 36 1 37 36 2 37
CAIR Emissions......... 30 1 31 6 2 8
Simple Heat Input 11 10 21 9 8 18
Budget.
Fuel Factor Adjusted 13 5 18 10 4 15
Budget.
FL................... Base Case Emissions.... 132 19 151 132 18 151
CAIR Emissions......... 51 17 69 44 18 61
Simple Heat Input 58 58 116 48 48 97
Budget.
[[Page 72278]]
Fuel Factor Adjusted 65 34 99 54 28 83
Budget.
----------------------------------------------------------------------------------------------------------------
* Numeric value is based on 2010 projections.
** For DC: Projected Base Case emissions are 35 tons in 2015. CAIR Emissions are projected to be 35 tons in both
2009 and 2015. Simple Heat Input budgets are 213 and 178 tons in 2009 and 2015, respectively. Fuel Factor
budgets are 144 and 120 tons in 2009 and 2015, respectively.
Table 2 lists those States in the CAIR region that have significant
amounts (i.e., 40 percent or greater) of generation sources that
combust fossil fuels other than coal. As illustrated by Table 2, DC,
FL, LA, MS, NY, and TX, while receiving fewer allowances under a fuel
factor approach, are provided with reasonable Statewide budgets that
are comparable to their projected emissions in 2009 and 2015. If the
States were to directly pass through allowances to their gas-fired
units, these units would still have excess allowances. Furthermore in
most cases, these States still receive a larger budget than they need
to cover their projected emissions.
Table 3.--Comparison of Projected NOX Emissions and State Budgets for CAIR States
[Thousand tons]
--------------------------------------------------------------------------------------------------------------------------------------------------------
Projected 2009 * emissions and budgets Projected 2015 emissions and budgets
-------------------------------------------------------------------------------------------------------------
Emissions Budget Emissions Budget
State -------------------------------------------------------------------------------------------------------------
Simple Fuel Simple Fuel
Base case CAIR heat factor Percent Base case CAIR heat factor Percent
input adjusted change input adjusted change
--------------------------------------------------------------------------------------------------------------------------------------------------------
DC **..................................... 0 <1 <1 <1 -32 <1 <1 <1 <1 -33
LA........................................ 49 35 50 36 -29 50 32 42 30 -29
NY........................................ 45 36 61 46 -25 44 21 51 38 -25
TX........................................ 186 166 231 181 -22 179 157 192 151 -22
MS........................................ 37 31 21 18 -16 37 8 18 15 -16
FL........................................ 151 69 116 99 -14 151 61 97 83 -14
MI........................................ 117 88 64 65 3 120 90 53 54 3
MD........................................ 57 13 27 28 4 57 12 22 23 4
VA........................................ 68 43 35 36 5 60 39 29 30 5
AL........................................ 132 65 64 69 8 134 49 53 58 8
GA........................................ 143 106 61 66 9 141 67 51 55 9
IL........................................ 146 66 70 76 9 159 65 58 64 9
WI........................................ 71 47 37 41 9 69 34 31 34 9
PA........................................ 198 86 90 99 10 193 72 75 83 10
SC........................................ 49 38 30 33 10 50 36 25 27 10
MO........................................ 116 64 54 60 10 118 66 45 50 10
MN........................................ 72 36 28 31 11 74 37 24 26 11
NC........................................ 60 59 56 62 11 61 49 47 52 11
IN........................................ 234 121 98 109 11 233 79 81 91 11
OH........................................ 264 91 97 109 12 274 90 81 91 12
TN........................................ 106 37 46 51 12 106 27 38 42 12
KY........................................ 176 99 74 83 12 176 74 62 69 12
IA........................................ 76 45 29 33 12 81 47 24 27 12
WV........................................ 179 62 66 74 13 176 40 55 62 13
------------
Total................................. 2732 1503 1505 1505 0 2746 1254 1254 1254 0
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Numeric value is based on 2010 projections.
** For DC: Projected ** Base Case emissions are 35 tons in 2015. CAIR Emissions are projected to be 35 tons in both 2009 and 2015. Simple Heat Input
budgets are 213 and 178 tons in 2009 and 2015, respectively. Fuel Factor budgets are 144 and 120 tons in 2009 and 2015, respectively.
Table 3 shows that relative to the simple heat input method the
fuel factor method reduces the disparity between projected State
emissions and State budgets, because the fuel factor approach allocates
State budgets that are generally closer to projected State emissions.
As explained above, the States that receive smaller budgets under the
fuel factor method are still generally receiving budgets that exceed
their projected emissions. States that receive larger budgets under the
fuel factor method are generally States with a large amount of coal-
fired generation that are installing post combustion controls as a
result of CAIR.
[[Page 72279]]
Analysis of Potential Delaware and New Jersey Impacts
The analyses described above were conducted for the States in the
CAIR PM2.5 region only. EPA has proposed to add Delaware and
New Jersey to the CAIR region for PM2.5 (``Inclusion of
Delaware and New Jersey in the Clean Air Interstate Rule'', EPA, May
10, 2005), but has not yet taken final action on this proposal. EPA
proposed a separate 2-State ``regional'' budget for Delaware and New
Jersey of just over 14,000 tons. EPA's analysis, presented in Table 4,
shows that apportioning this budget between the two States based on a
fuel factor method instead of a simple heat input method, is
reasonable. (``Inclusion of Delaware and New Jersey in the Clean Air
Interstate Rule'', EPA, May 10, 2005)
Table 4.--Comparison of Projected NOX Emissions and State Budgets for New Jersey and Delaware
[Thousand tons]
--------------------------------------------------------------------------------------------------------------------------------------------------------
Projected 2009 * emissions and allowance allocation Projected 2015 emissions and allowance allocation
-------------------------------------------------------------------------------------------------------------
Simple Fuel Simple Fuel
State Base case CAIR heat factor Percent Base case CAIR heat factor Percent
emissions input adjusted change emissions input adjusted change
emissions budget budget emissions budget budget
--------------------------------------------------------------------------------------------------------------------------------------------------------
NJ........................................ 16.8 12.0 13.4 12.7 -5.6 17.9 12.8 11.2 10.6 -5.6
DE........................................ 9.4 8.5 3.4 4.2 22.1 10.7 9.5 2.8 3.5 22.2
--------------------------------------------------------------------------------------------------------------------------------------------------------
* Numeric value is based on 2010 projections.
Other Considerations
EPA notes that the analyses above were conducted for State annual
NOX budgets established in the CAIR. CAIR also establishes
seasonal NOX budgets using the fuel factor approach. EPA did
not conduct a similar analysis of the seasonal NOX budgets.
EPA modeling indicates that the ozone season program is likely to
function as a backstop to the annual NOX program, and that
the annual NOX program is likely to impose the binding
constraint on NOX emissions.
Finally, to ensure that our estimates appropriately reflect the
distribution of emissions in the case of higher electricity demand and
increased gas and oil prices, EPA conducted a sensitivity run using
EIA's forecast of higher electricit