Approval and Promulgation of Implementation Plans and Designation of Areas for Air Quality Planning Purposes; Wisconsin; Redesignation of the Manitowoc County and Door County Areas to Attainment for Ozone, 22047-22063 [2010-9753]
Download as PDF
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
Issued in Fort Worth, TX on April 19,
2010.
Anthony D. Roetzel,
Manager, Operations Support Group, ATO
Central Service Center.
[FR Doc. 2010–9749 Filed 4–26–10; 8:45 am]
BILLING CODE 4910–13–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
15 CFR Part 922
Intent To Initiate Consultation and
Coordinate the National Oceanic and
Atmospheric Administration’s
Responsibilities Under Section 106 of
the National Historic Preservation Act
(NHPA) With the Ongoing National
Environmental Policy Act (NEPA)
Process Supporting the Review of the
Olympic Coast National Marine
Sanctuary Management Plan
AGENCY: Office of National Marine
Sanctuaries (ONMS), National Ocean
Service (NOS), National Oceanic and
Atmospheric Administration (NOAA),
Department of Commerce (DOC).
ACTION: Consultation under Section 106
of the NHPA in conjunction with
Review of Management Plan/
Regulations and associated NEPA public
process.
In accordance with section
304(e) of the National Marine
Sanctuaries Act, as amended, (NMSA)
(16 U.S.C. 1431 et seq.), the Office of
National Marine Sanctuaries (ONMS) of
the National Oceanic and Atmospheric
Administration (NOAA) has initiated a
review of the Olympic Coast National
Marine Sanctuary (OCNMS or
sanctuary) management plan, to
evaluate substantive progress toward
implementing the goals for the
Sanctuary, and to make revisions to the
plan and regulations as necessary to
fulfill the purposes and policies of the
NMSA (73 FR 53161). The management
plan review process occurs concurrently
with a public process under the
National Environmental Policy Act
(NEPA; 42 U.S.C. 4321 et seq.). This
notice confirms that NOAA will
coordinate its responsibilities under
NEPA with those under section 106 of
the National Historic Preservation Act
(NHPA, 16 U.S.C. 470).
DATES: Comments may be submitted at
any time.
ADDRESSES: Written comments may be
sent to the Olympic Coast National
Marine Sanctuary (Management Plan
Review), 115 Railroad Ave. East, Suite
mstockstill on DSKH9S0YB1PROD with PROPOSALS
SUMMARY:
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
301, Port Angeles, WA 98362, or faxed
to (360) 457–8496. Electronic comments
may be sent to
ocnmsmanagementplan@noaa.gov.
FOR FURTHER INFORMATION CONTACT:
George Galasso, 360.457.6622 Ext. 12,
ocnmsmanagementplan@noaa.gov.
SUPPLEMENTARY INFORMATION: OCNMS
was designated in May 1994. It spans
3,310 square miles of marine waters off
the rugged Olympic Peninsula coast,
covering much of the continental shelf
and the heads of several major
submarine canyons. The present
management plan was written as part of
the sanctuary designation process and
published in the Final Environmental
Impact Statement in 1993.
In September 2008, NOAA published
a Notice of Intent to prepare an
Environmental Impact Statement under
the authority of NEPA (73 FR 53161).
The management plan review process is
composed of four major stages: (1)
Information collection and
characterization; (2) preparation and
release of a draft management plan/
environmental impact analysis
document; (3) public review and
comment; (4) preparation and release of
a final management plan/environmental
impact analysis document, and any final
amendments to the regulations. NOAA
anticipates completion of the revised
management plan and concomitant
documents will require approximately
thirty-six months from the date of
publication of the original notice of
intent (37 FR 53161; September 15,
2008). The proposed revised
management plan will likely involve
changes to existing policies of the
Sanctuary in order to address
contemporary issues and challenges,
and to better protect and manage the
Sanctuary’s natural resources and
qualities and historic properties.
This notice confirms that NOAA will
coordinate its responsibilities under
section 106 of the National Historic
Preservation Act (NHPA, 16 U.S.C. 470)
with its ongoing NEPA process,
pursuant to 36 CFR 800.8(a)—
coordination with NEPA—including the
use of NEPA documents and public and
stakeholder meetings to also meet the
section 106 requirements. The NHPA
specifically applies to any agency
undertaking that has an adverse effect
on historic properties. Pursuant to 36
CFR 800.16(1)(1), historic properties
includes: ‘‘any prehistoric or historic
district, site, building, structure or
object included in, or eligible for
inclusion in, the National Register of
Historic Places maintained by the
Secretary of the Interior. The term
includes artifacts, records, and remains
PO 00000
Frm 00022
Fmt 4702
Sfmt 4702
22047
that are related to and located within
such properties. The term includes
properties of traditional religious and
cultural importance to an Indian tribe
* * * and that meet the National
Register criteria.’’
In coordinating its responsibilities
under the NHPA and NEPA, NOAA
intends to identify consulting parties;
identify historic properties and assess
the effects of the undertaking on such
properties; initiate formal consultation
with the Washington State Historic
Preservation Officer, appropriate Tribal
Historic Preservation Officers, the
Advisory Council of Historic
Preservation, and other consulting
parties; involve the public in
accordance with NOAA’s NEPA
procedures, and develop in consultation
with identified consulting parties
alternatives and proposed measures that
might avoid, minimize or mitigate any
adverse effects on historic properties
and describe them in any
Environmental Assessment or Draft
Environmental Impact Statement.
Authority: 16 U.S.C. 1431 et seq.; 16
U.S.C. 470.
(Federal Domestic Assistance Catalog
Number 11.429 Marine Sanctuary Program)
Dated: April 15, 2010.
Daniel J. Basta,
Director for the Office of National Marine
Sanctuaries.
[FR Doc. 2010–9203 Filed 4–26–10; 8:45 am]
BILLING CODE 3510–NK–M
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR PARTS 52 AND 81
[EPA–R05–OAR–2009–0730; FRL–9142–2]
Approval and Promulgation of
Implementation Plans and Designation
of Areas for Air Quality Planning
Purposes; Wisconsin; Redesignation
of the Manitowoc County and Door
County Areas to Attainment for Ozone
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
SUMMARY: EPA is proposing to approve
Wisconsin’s requests to redesignate the
Manitowoc County and Door County,
Wisconsin nonattainment areas, to
attainment for the 1997 8-hour ozone
standard, because the requests meet the
statutory requirements for redesignation
under the Clean Air Act (CAA). The
Wisconsin Department of Natural
Resources (WDNR) submitted these
requests on September 11, 2009.
E:\FR\FM\27APP1.SGM
27APP1
mstockstill on DSKH9S0YB1PROD with PROPOSALS
22048
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
These proposed approvals involve
several related actions. EPA is
proposing to determine that the
Manitowoc County and Door County
areas have attained the 8-hour ozone
National Ambient Air Quality Standard
(NAAQS). These determinations are
based on three years of complete,
quality-assured and certified ambient air
quality monitoring data for the 2006–
2008 ozone seasons that demonstrate
that the 8-hour ozone NAAQS has been
attained in the areas. Complete, qualityassured air quality data for the 2009
ozone season have been recorded in the
EPA’s Air Quality System (AQS) and
show that the areas continue to attain
the 8-hour ozone standard. EPA is also
proposing to approve, as revisions to the
Wisconsin State Implementation Plan
(SIP), the State’s plans for maintaining
the 8-hour ozone NAAQS through 2020
in the areas.
EPA is proposing to approve the 2005
base year emissions inventories for the
Manitowoc County and Door County
areas as meeting the base year emissions
inventory requirement of the CAA.
WDNR submitted these base year
emissions inventories on June 12, 2007.
Finally, EPA finds adequate and is
proposing to approve the State’s 2012
and 2020 Motor Vehicle Emission
Budgets (MVEBs) for the Manitowoc
County and Door County areas.
DATES: Comments must be received on
or before May 27, 2010.
ADDRESSES: Submit your comments,
identified by Docket ID No. EPA–R05–
OAR–2009–0730, by one of the
following methods:
1. https://www.regulations.gov: Follow
the on-line instructions for submitting
comments.
2. E-mail: bortzer.jay@epa.gov.
3. Fax: (312) 692–2054.
4. Mail: Jay Bortzer, Chief, Air
Programs Branch (AR–18J), U.S.
Environmental Protection Agency, 77
West Jackson Boulevard, Chicago,
Illinois 60604.
5. Hand delivery: Jay Bortzer, Chief,
Air Programs Branch (AR–18J), U.S.
Environmental Protection Agency, 77
West Jackson Boulevard, 18th Floor,
Chicago, Illinois 60604. Such deliveries
are only accepted during the Regional
Office normal hours of operation, and
special arrangements should be made
for deliveries of boxed information. The
Regional Office official hours of
business are Monday through Friday,
8:30 a.m. to 4:30 p.m., excluding
Federal holidays.
Instructions: Direct your comments to
Docket ID No. EPA–R05–OAR–2009–
0730. EPA’s policy is that all comments
received will be included in the public
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
docket without change and may be
made available online at https://
www.regulations.gov, including any
personal information provided, unless
the comment includes information
claimed to be Confidential Business
Information (CBI) or other information
whose disclosure is restricted by statute.
Do not submit information that you
consider to be CBI or otherwise
protected through https://
www.regulations.gov or e-mail. The
https://www.regulations.gov Web site is
an ‘‘anonymous access’’ system, 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 https://
www.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 instructions on
submitting comments, go to section I of
this document, ‘‘What Should I Consider
as I Prepare My Comments for EPA?’’
Docket: All documents in the docket
are listed in the https://
www.regulations.gov index. Although
listed in the index, some information is
not publicly available, e.g., CBI or other
information whose disclosure is
restricted by statute. Certain other
material, such as copyrighted material,
will be publicly available only in hard
copy. Publicly available docket
materials are available either
electronically in https://
www.regulations.gov or in hard copy at
the Environmental Protection Agency,
Region 5, Air and Radiation Division, 77
West Jackson Boulevard, Chicago,
Illinois 60604. This facility is open from
8:30 a.m. to 4:30 p.m., Monday through
Friday, excluding Federal holidays. We
recommend that you telephone
Kathleen D’Agostino, Environmental
Engineer, at (312) 886–1767 before
visiting the Region 5 office.
FOR FURTHER INFORMATION CONTACT:
Kathleen D’Agostino, Environmental
Engineer, Criteria Pollutant Section, Air
Programs Branch (AR–18J), U.S.
Environmental Protection Agency,
PO 00000
Frm 00023
Fmt 4702
Sfmt 4702
Region 5, 77 West Jackson Boulevard,
Chicago, Illinois 60604, (312) 886–1767,
dagostino.kathleen@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document whenever
‘‘we,’’ ‘‘us,’’ or ‘‘our’’ is used, we mean
EPA. This supplementary information
section is arranged as follows:
Table of Contents
I. What should I consider as I prepare my
comments for EPA?
II. What actions is EPA proposing to take?
III. What is the background for these actions?
A. What is the general background
information?
B. What are the impacts of the December
22, 2006, and June 8, 2007, United States
Court of Appeals decisions regarding
EPA’s Phase 1 implementation rule?
IV. What are the criteria for redesignation?
V. What is the effect of these actions?
VI. What is EPA’s analysis of the requests?
A. Attainment Determinations and
Redesignations
B. Adequacy of Wisconsin’s MVEBs
C. 2005 Base Year Emissions Inventories
VII. What actions is EPA taking?
VIII. Statutory and Executive Order Reviews
I. What should I consider as I prepare
my comments for EPA?
When submitting comments,
remember to:
1. Identify the rulemaking by docket
number and other identifying
information (subject heading, Federal
Register date and page number).
2. Follow directions—EPA may ask
you to respond to specific questions or
organize comments by referencing a
Code of Federal Regulations (CFR) part
or section number.
3. Explain why you agree or disagree;
suggest alternatives and substitute
language for your requested changes.
4. Describe any assumptions and
provide any technical information and/
or data that you used.
5. If you estimate potential costs or
burdens, explain how you arrived at
your estimate in sufficient detail to
allow for it to be reproduced.
6. Provide specific examples to
illustrate your concerns, and suggest
alternatives.
7. Explain your views as clearly as
possible, avoiding the use of profanity
or personal threats.
8. Make sure to submit your
comments by the comment period
deadline identified.
II. What actions is EPA proposing to
take?
EPA is proposing to take several
related actions. EPA is proposing to
determine that the Manitowoc County
and Door County nonattainment areas
have attained the 1997 8-hour ozone
E:\FR\FM\27APP1.SGM
27APP1
mstockstill on DSKH9S0YB1PROD with PROPOSALS
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
standard and that the areas have met the
requirements for redesignation under
section 107(d)(3)(E) of the CAA. EPA is
thus proposing to approve the requests
from WDNR to change the legal
designation of the Manitowoc County
and Door County areas from
nonattainment to attainment for the 8hour ozone NAAQS. EPA is also
proposing to approve, as revisions to the
Wisconsin SIP, the State’s maintenance
plans (such approval being one of the
CAA criteria for redesignation to
attainment status). The maintenance
plans are designed to keep the
Manitowoc County and Door County
areas in attainment of the ozone NAAQS
through 2020. EPA is proposing to
approve the 2005 base year emissions
inventories for the Manitowoc County
and Door County areas as meeting the
requirements of section 172(c)(3) of the
CAA. If EPA’s determination of
attainment is finalized, under the
provisions of 40 CFR 51.918, the
requirement to submit certain planning
SIPs related to attainment (the
Reasonably Available Control Measure
(RACM) requirement of section 172(c)(1)
of the CAA, the Reasonable Further
Progress (RFP) and attainment
demonstration requirements of sections
172(c)(2) and (6) of the CAA, and the
requirement for contingency measures
of section 172(c)(9) of the CAA) are not
applicable to the area as long as it
continues to attain the NAAQS and
would cease to be applicable upon
redesignation. In addition, as set forth in
more detail below, in the context of
redesignations, EPA has interpreted
requirements related to attainment as
not applicable for purposes of
redesignation. Finally, EPA finds
adequate and is proposing to approve
the newly-established 2012 and 2020
MVEBs for the Manitowoc County and
Door County areas. The adequacy
comment period for the MVEBs began
on February 24, 2010, with EPA’s
posting of the availability of the
submittal on EPA’s Adequacy Web site
(at https://www.epa.gov/otaq/
stateresources/transconf/
adequacy.htm). The adequacy comment
period for these MVEBs ended on March
26, 2010. EPA did not receive any
requests for this submittal, or adverse
comments on this submittal during the
adequacy comment period. In a letter
dated April 7, 2010, EPA informed
WDNR that we had found the 2012 and
2020 MVEBs to be adequate for use in
transportation conformity analyses.
Please see section VI.B. of this
rulemaking, ‘‘Adequacy of Wisconsin’s
MVEBs,’’ for further explanation of this
process. Therefore, we find adequate,
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
and are proposing to approve, the
State’s 2012 and 2020 MVEBs for
transportation conformity purposes.
III. What is the background for these
actions?
A. What is the general background
information?
Ground-level ozone is not emitted
directly by sources. Rather, emissions of
nitrogen oxides (NOX) and volatile
organic compounds (VOCs) react in the
presence of sunlight to form groundlevel ozone. NOX and VOCs are referred
to as precursors of ozone.
The CAA establishes a process for air
quality management through the
NAAQS. Before promulgation of the 8hour standard, the ozone NAAQS was
based on a 1-hour standard. On
November 6, 1991 (56 FR 56693 and
56852), the Manitowoc County and Door
County areas were designated as
moderate and rural transport
nonattainment areas, respectively,
under the 1-hour ozone NAAQS. The
Manitowoc County and Door County
areas were subsequently redesignated to
attainment of the 1-hour standard on
April 17, 2003 (68 FR 18883). At the
time EPA revoked the 1-hour ozone
NAAQS, on June 15, 2005, the
Manitowoc County and Door County
areas were designated as attainment
under the 1-hour ozone NAAQS.
On July 18, 1997 (62 FR 38856), EPA
promulgated an 8-hour ozone standard
of 0.08 parts per million parts (ppm). On
April 30, 2004 (69 FR 23857), EPA
published a final rule designating and
classifying areas under the 8-hour ozone
NAAQS. These designations and
classifications became effective June 15,
2004. EPA designated as nonattainment
any area that was violating the 8-hour
ozone NAAQS based on the three most
recent years of air quality data, 2001–
2003.
The CAA contains two sets of
provisions, subpart 1 and subpart 2, that
address planning and control
requirements for nonattainment areas.
(Both are found in Title I, part D, of the
CAA; 42 U.S.C. 7501–7509a and 7511–
7511f, respectively.) Subpart 1 contains
general requirements for nonattainment
areas for any pollutant, including ozone,
governed by a NAAQS. Subpart 2
provides additional and more specific
requirements for ozone nonattainment
areas.
Under EPA’s implementation rule for
the 1997 8-hour ozone standard, (69 FR
23951 (April 30, 2004)), an area was
classified under subpart 2 based on its
8-hour ozone design value (i.e. the
three-year average annual fourth-highest
daily maximum 8-hour average ozone
PO 00000
Frm 00024
Fmt 4702
Sfmt 4702
22049
concentration), if it had a 1-hour design
value at the time of designation at or
above 0.121 ppm (the lowest 1-hour
design value in Table 1 of subpart 2) (69
FR 23954). All other areas were covered
under subpart 1, based upon their 8hour design values (69 FR 23958). The
Manitowoc County and Door County
areas were designated as a subpart 1, 8hour ozone nonattainment area by EPA
on April 30, 2004 (69 FR 23857, 23947),
based on air quality monitoring data
from 2001–2003 (69 FR 23860).
40 CFR 50.10 and 40 CFR part 50,
Appendix I, provide that the 8-hour
ozone standard is attained when the
three-year average of the annual fourthhighest daily maximum 8-hour average
ozone concentration is less than or
equal to 0.08 ppm, when rounded. The
data completeness requirement is met
when the average percent of days with
valid ambient monitoring data is greater
than 90%, and no single year has less
than 75% data completeness. See 40
CFR part 50, Appendix I, 2.3(d).
The WDNR submitted requests to
redesignate the Manitowoc County and
Door County areas to attainment for the
8-hour ozone standard on September 11,
2009. The redesignation requests
included three years of complete,
quality-assured data for the period of
2006 through 2008, indicating the 8hour NAAQS for ozone, as promulgated
in 1997, had been attained for the
Manitowoc County and Door County
areas. Complete, quality-assured
monitoring data in AQS but not yet
certified for the 2009 ozone season show
that the areas continue to attain the 8hour ozone standard. Under the CAA,
nonattainment areas may be
redesignated to attainment if sufficient
complete, quality-assured data are
available for the Administrator to
determine that the area has attained the
standard, and the area meets the other
CAA redesignation requirements in
section 107(d)(3)(E).
On March 27, 2008 (73 FR 16436),
EPA promulgated a revised 8-hour
ozone standard of 0.075 ppm. In May
2008, States, environmental groups and
industry groups filed petitions with the
DC Circuit Court of Appeals for review
of the 2008 ozone standards. In March
2009, the court granted EPA’s request to
stay the litigation so EPA could review
the standards and determine whether
they should be reconsidered. On
September 16, 2009, we announced that
we are reconsidering our 2008 decision
setting national standards for groundlevel ozone. The designation process for
that standard has been stayed. On
January 19, 2010, EPA proposed to set
the level of the primary 8-hour ozone
standard within the range of 0.060 to
E:\FR\FM\27APP1.SGM
27APP1
22050
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
0.070 ppm, rather than at 0.075 ppm (75
FR 2938). We expect by August 2010 to
have completed our reconsideration of
the standard and also expect that
thereafter we will proceed with
designations. The actions addressed in
today’s proposed rulemaking relate only
to the 1997 8-hour ozone standard.
mstockstill on DSKH9S0YB1PROD with PROPOSALS
B. What are the impacts of the
December 22, 2006, and June 8, 2007,
United States Court of Appeals
decisions regarding EPA’s Phase 1
implementation rule?
1. Summary of Court Decision
On December 22, 2006, in South
Coast Air Quality Management Dist. v.
EPA (South Coast), the U.S. Court of
Appeals for the District of Columbia
Circuit vacated EPA’s Phase 1
Implementation Rule for the 8-hour
Ozone Standard (69 FR 23951, April 30,
2004). 472 F.3d 882 (DC Cir. 2006). On
June 8, 2007, in response to several
petitions for rehearing, the DC Circuit
Court clarified that the Phase 1 Rule was
vacated only with regard to those parts
of the rule that had been successfully
challenged. Id., Docket No. 04 1201.
Therefore, several provisions of the
Phase 1 Rule remain effective:
provisions related to classifications for
areas currently classified under subpart
2 of Title I, part D, of the CAA as 8-hour
nonattainment areas; the 8-hour
attainment dates; and the timing for
emissions reductions needed for
attainment of the 8-hour ozone NAAQS.
The June 8, 2007, decision also left
intact the court’s rejection of EPA’s
reasons for implementing the 8-hour
standard in certain nonattainment areas
under subpart 1 in lieu of subpart 2. By
limiting the vacatur, the court let stand
EPA’s revocation of the 1-hour standard
and those anti-backsliding provisions of
the Phase 1 Rule that had not been
successfully challenged. The June 8,
2007, decision reaffirmed the December
22, 2006, decision that EPA had
improperly failed to retain four
measures required for 1-hour
nonattainment areas under the antibacksliding provisions of the
regulations: (1) Nonattainment area New
Source Review (NSR) requirements
based on an area’s 1-hour nonattainment
classification; (2) section 185 penalty
fees for 1-hour severe or extreme
nonattainment areas; (3) measures to be
implemented pursuant to section
172(c)(9) or 182(c)(9) of the CAA, on the
contingency of an area not making
reasonable further progress toward
attainment of the 1-hour NAAQS, or for
failure to attain that NAAQS; and (4)
certain transportation conformity
requirements for certain types of Federal
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
actions. The June 8, 2007, decision
clarified that the court’s reference to
conformity requirements was limited to
requiring the continued use of 1-hour
motor vehicle emissions budgets until 8hour budgets were available for 8-hour
conformity determinations.
This section sets forth EPA’s views on
the potential effect of the court’s rulings
on these proposed redesignation
actions. For the reasons set forth below,
EPA does not believe that the court’s
rulings alter any requirements relevant
to these redesignation actions so as to
preclude redesignation or prevent EPA
from proposing or ultimately finalizing
these redesignations. EPA believes that
the court’s December 22, 2006, and June
8, 2007, decisions impose no
impediment to moving forward with
redesignation of these areas to
attainment, because even in light of the
court’s decisions, redesignation is
appropriate under the relevant
redesignation provisions of the CAA
and longstanding policies regarding
redesignation requests.
2. Requirements Under the 8-Hour
Standard
With respect to the 8-hour standard,
the court’s ruling rejected EPA’s reasons
for classifying areas under subpart 1 for
the 8-hour standard, and remanded that
matter to the Agency. In its January 16,
2009, proposed rulemaking in response
to the South Coast decision, EPA has
proposed to classify Door County and
Manitowoc County under subpart 2 as
moderate and marginal areas,
respectively (74 FR 2936, 2944). If EPA
finalizes this rulemaking, the
requirements under subpart 2 will
become applicable when they are due,
a deadline that EPA has proposed to be
one year after the effective date of a final
rulemaking classifying areas as
moderate or marginal (74 FR 2940–
2941). Although a future final decision
by EPA to classify these areas under
subpart 2 would trigger additional
future requirements for the areas, EPA
believes that this does not mean that
redesignations cannot now go forward.
This belief is based upon: (1) EPA’s
longstanding policy of evaluating
requirements in accordance with the
requirements due at the time the request
is submitted; and, (2) consideration of
the inequity of applying retroactively
any requirements that might be applied
in the future.
First, at the time the redesignation
requests were submitted, the Manitowoc
County and Door County areas were not
classified under subpart 2, nor were
there any subpart 2 requirements yet
due for these areas. Under EPA’s
longstanding interpretation of section
PO 00000
Frm 00025
Fmt 4702
Sfmt 4702
107(d)(3)(E) of the CAA, to qualify for
redesignation, States requesting
redesignation to attainment must meet
only the relevant SIP requirements that
came due prior to the submittal of a
complete redesignation request. See
September 4, 1992, Calcagni
memorandum (‘‘Procedures for
Processing Requests to Redesignate
Areas to Attainment,’’ Memorandum
from John Calcagni, Director, Air
Quality Management Division). See also
Michael Shapiro Memorandum,
September 17, 1993, and 60 FR 12459,
12465–12466 (March 7, 1995)
(Redesignation of Detroit-Ann Arbor).
See Sierra Club v. EPA, 375 F.3d 537
(7th Cir. 2004), which upheld EPA’s
redesignation rulemaking applying this
interpretation. See, e.g. also 68 FR
25418, 25424, 25427 (May 12, 2003)
(Redesignation of St. Louis).
Moreover, it would be inequitable to
retroactively apply any new SIP
requirements that were not applicable at
the time the request was submitted. The
DC Circuit has recognized the inequity
in such retroactive rulemaking. In Sierra
Club v. Whitman, 285 F.3d 63 (DC Cir.
2002), the DC Circuit upheld a district
court’s ruling refusing to make
retroactive an EPA determination of
nonattainment that was past the
statutory due date. Such a
determination would have resulted in
the imposition of additional
requirements on the area. The court
stated: ‘‘Although EPA failed to make
the nonattainment determination within
the statutory time frame, Sierra Club’s
proposed solution only makes the
situation worse. Retroactive relief would
likely impose large costs on the States,
which would face fines and suits for not
implementing air pollution prevention
plans in 1997, even though they were
not on notice at the time.’’ Id. at 68.
Similarly here it would be unfair to
penalize the areas by applying to them,
for purposes of redesignation, additional
SIP requirements under subpart 2 that
were not in effect or yet due at the time
WDNR submitted its redesignation
requests.
3. Requirements Under the 1-Hour
Standard
With respect to the 1-hour standard
requirements, the Manitowoc County
and Door County areas were attainment
areas subject to CAA section 175A
maintenance plans under the 1-hour
standard at the time that the 1-hour
standard was revoked. Therefore, the DC
Circuit’s decisions with respect to 1hour nonattainment anti-backsliding
requirements do not impact
redesignation requests for these types of
areas, except to the extent that the court
E:\FR\FM\27APP1.SGM
27APP1
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
in its June 8, 2007, decision clarified
that for those areas with 1-hour motor
vehicle emissions budgets in their
maintenance plans, anti-backsliding
requires that those 1-hour budgets must
be used for 8-hour conformity
determinations until replaced by 8-hour
budgets. To meet this requirement,
conformity determinations in such areas
must comply with the applicable
requirements of EPA’s conformity
regulations at 40 CFR part 93.
With respect to the three other antibacksliding provisions for the 1-hour
standard that the court found were not
properly retained, the Manitowoc
County and Door County areas are
attainment areas subject to maintenance
plans for the 1-hour standard, and the
NSR, contingency measures (pursuant to
section 172(c)(9) or 182(c)(9)), and fee
provision requirements no longer apply
to areas that have been redesignated to
attainment of the 1-hour standard.
Thus, the South Coast decision in
South Coast Air Quality Management
Dist. does not preclude EPA from
finalizing the redesignation of these
areas.
mstockstill on DSKH9S0YB1PROD with PROPOSALS
IV. What are the criteria for
redesignation?
The CAA provides the requirements
for redesignating a nonattainment area
to attainment. Specifically, section
107(d)(3)(E) allows for redesignation
provided that: (1) The Administrator
determines that the area has attained the
applicable NAAQS; (2) the
Administrator has fully approved the
applicable implementation plan for the
area under section 110(k); (3) the
Administrator determines that the
improvement in air quality is due to
permanent and enforceable reductions
in emissions resulting from
implementation of the applicable SIP
and applicable Federal air pollutant
control regulations and other permanent
and enforceable reductions; (4) the
Administrator has fully approved a
maintenance plan for the area as
meeting the requirements of section
175A; and, (5) the State containing such
area has met all requirements applicable
to the area under section 110 and part
D.
EPA provided guidance on
redesignation in the General Preamble
for the Implementation of Title I of the
CAA Amendments of 1990 on April 16,
1992 (57 FR 13498), and supplemented
this guidance on April 28, 1992 (57 FR
18070). EPA has provided further
guidance on processing redesignation
requests in the following documents:
‘‘Ozone and Carbon Monoxide Design
Value Calculations,’’ Memorandum from
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
William G. Laxton, Director Technical
Support Division, June 18, 1990;
‘‘Maintenance Plans for Redesignation
of Ozone and Carbon Monoxide
Nonattainment Areas,’’ Memorandum
from G. T. Helms, Chief, Ozone/Carbon
Monoxide Programs Branch, April 30,
1992;
‘‘Contingency Measures for Ozone and
Carbon Monoxide (CO) Redesignations,’’
Memorandum from G. T. Helms, Chief,
Ozone/Carbon Monoxide Programs
Branch, June 1, 1992;
‘‘Procedures for Processing Requests
to Redesignate Areas to Attainment,’’
Memorandum from John Calcagni,
Director, Air Quality Management
Division, September 4, 1992;
‘‘State Implementation Plan (SIP)
Actions Submitted in Response to Clean
Air Act (ACT) Deadlines,’’
Memorandum from John Calcagni,
Director, Air Quality Management
Division, October 28, 1992;
‘‘Technical Support Documents
(TSDs) for Redesignation Ozone and
Carbon Monoxide (CO) Nonattainment
Areas,’’ Memorandum from G. T. Helms,
Chief, Ozone/Carbon Monoxide
Programs Branch, August 17, 1993;
‘‘State Implementation Plan (SIP)
Requirements for Areas Submitting
Requests for Redesignation to
Attainment of the Ozone and Carbon
Monoxide (CO) National Ambient Air
Quality Standards (NAAQS) On or After
November 15, 1992,’’ Memorandum
from Michael H. Shapiro, Acting
Assistant Administrator for Air and
Radiation, September 17, 1993;
‘‘Use of Actual Emissions in
Maintenance Demonstrations for Ozone
and CO Nonattainment Areas,’’
Memorandum from D. Kent Berry,
Acting Director, Air Quality
Management Division, to Air Division
Directors, Regions 1–10, November 30,
1993.
‘‘Part D New Source Review (part D
NSR) Requirements for Areas
Requesting Redesignation to
Attainment,’’ Memorandum from Mary
D. Nichols, Assistant Administrator for
Air and Radiation, October 14, 1994;
and
‘‘Reasonable Further Progress,
Attainment Demonstration, and Related
Requirements for Ozone Nonattainment
Areas Meeting the Ozone National
Ambient Air Quality Standard,’’
Memorandum from John S. Seitz,
Director, Office of Air Quality Planning
and Standards, May 10, 1995.
V. What is the effect of these actions?
Approval of the redesignation
requests would change the official
designations of the Manitowoc County
and Door County areas for the 1997 8-
PO 00000
Frm 00026
Fmt 4702
Sfmt 4702
22051
hour ozone NAAQS found at 40 CFR
part 81. It would also incorporate into
the Wisconsin SIP plans for maintaining
the 8-hour ozone NAAQS through 2020.
The maintenance plans include
contingency measures as required under
CAA section 175A to remedy future
violations of the 8-hour NAAQS. They
also establish MVEBs for the Manitowoc
County area of 1.76 and 1.25 tons per
day (tpd) for VOC and 3.76 and 1.86 tpd
for NOX for the years 2012 and 2020,
respectively, and MVEBs for the Door
County area of 0.78 and 0.53 tpd for
VOC and 1.55 and 0.74 tpd for NOX for
the years 2012 and 2020, respectively.
VI. What is EPA’s analysis of the
request?
A. Attainment Determinations and
Redesignations
EPA is proposing to determine that
the Manitowoc County and Door County
areas have attained the 1997 8-hour
ozone standard and that the areas have
met all other applicable redesignation
criteria under CAA section 107(d)(3)(E).
The basis for EPA’s proposed approvals
of the redesignation requests is as
follows:
1. The Areas Have Attained the 8-Hour
Ozone NAAQS (Section 107(d)(3)(E)(i))
EPA is proposing to make
determinations that the Manitowoc
County and Door County areas have
attained the 1997 8-hour ozone NAAQS.
An area may be considered to be
attaining the 8-hour ozone NAAQS if
there are no violations, as determined in
accordance with 40 CFR 50.10 and part
50, Appendix I, based on three
complete, consecutive calendar years of
quality-assured air quality monitoring
data. To attain this standard, the threeyear average of the fourth-highest daily
maximum 8-hour average ozone
concentrations measured at each
monitor within an area over each year
must not exceed 0.08 ppm. Based on the
rounding convention described in 40
CFR part 50, Appendix I, the standard
is attained if the design value is 0.084
ppm or below. The data must be
collected and quality-assured in
accordance with 40 CFR part 58, and
recorded in AQS. The monitors
generally should have remained at the
same location for the duration of the
monitoring period required for
demonstrating attainment.
Wisconsin included in its
redesignation requests ozone monitoring
data for the 2006 to 2008 ozone seasons
and has subsequently provided
monitoring data for 2009. Monitoring
data for 2006 through 2008 have been
certified by the State; 2009 data have
E:\FR\FM\27APP1.SGM
27APP1
22052
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
not yet been certified. However,
Wisconsin has quality-assured all of the
ambient monitoring data in accordance
with 40 CFR 58.10, and has recorded it
in the AQS database. The data meet the
completeness criteria in 40 CFR 50,
Appendix I, which require a minimum
completeness of 75 percent annually
and 90 percent over each three-year
period. Monitoring data are presented in
Table 1 below.
TABLE 1—ANNUAL 4TH HIGH DAILY MAXIMUM 8-HOUR OZONE CONCENTRATION AND THREE YEAR AVERAGES OF 4TH
HIGH DAILY MAXIMUM 8-HOUR OZONE CONCENTRATIONS
2006
4th high
(ppm)
Monitor
Door 55–029–0004 ..........................................................
Manitowoc 55–071–0007 .................................................
In addition, as discussed below with
respect to the maintenance plans,
WDNR has committed to continue to
operate an EPA-approved monitoring
network in the areas. WDNR will
continue to quality assure monitoring
data in accordance with 40 CFR part 58
and enter all data into AQS in
accordance with Federal guidelines. In
summary, EPA believes that the data
show that the Manitowoc County and
Door County areas have attained the 8hour ozone NAAQS.
mstockstill on DSKH9S0YB1PROD with PROPOSALS
2. The Areas Have Met All Applicable
Requirements Under Section 110 and
Part D; and the Areas Have Fully
Approved SIPs Under Section 110(k)
(Sections 107(d)(3)(E)(v) and
107(d)(3)(E)(ii))
We have determined that Wisconsin
has met all currently applicable SIP
requirements for purposes of
redesignation for the Manitowoc County
and Door County areas under section
110 of the CAA (general SIP
requirements). We are also proposing to
determine that the Wisconsin SIP meets
all SIP requirements for these areas
currently applicable for purposes of
redesignation under part D of Title I of
the CAA (requirements specific to
subpart 1 nonattainment areas), in
accordance with section 107(d)(3)(E)(v).
In addition, with the exception of the
base year emissions inventories, we
have approved all applicable
requirements of the Wisconsin SIP for
purposes of redesignation, in
accordance with section 107(d)(3)(E)(ii).
As discussed below, in this action EPA
is proposing to approve Wisconsin’s
2005 base year emissions inventories as
meeting the section 172(c)(3) emissions
inventory requirement for the areas.
In proposing these determinations, we
have ascertained which SIP
requirements are applicable to the areas
for purposes of redesignation, and have
determined that there are SIP measures
meeting those requirements and that
they are, or upon final approval of the
emissions inventories, will be fully
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
0.079
0.078
2007
4th high
(ppm)
2008
4th high
(ppm)
0.092
0.085
0.069
0.064
approved under section 110(k) of the
CAA. As discussed more fully below,
for purposes of evaluating a
redesignation request, SIPs must be
fully approved only with respect to
requirements that became due prior to
the submission of the redesignation
request.
The September 4, 1992, Calcagni
memorandum (see ‘‘Procedures for
Processing Requests to Redesignate
Areas to Attainment,’’ Memorandum
from John Calcagni, Director, Air
Quality Management Division,
September 4, 1992) describes EPA’s
interpretation of section 107(d)(3)(E) of
the CAA. Under this interpretation, a
State and the area it wishes to
redesignate must meet the relevant CAA
requirements that are due prior to the
State’s submittal of a complete
redesignation request for the area. See
also the September 17, 1993, Michael
Shapiro memorandum and 60 FR 12459,
12465–12466 (March 7, 1995)
(Redesignation of Detroit-Ann Arbor,
Michigan to attainment of the 1-hour
ozone NAAQS). Applicable
requirements of the CAA that come due
subsequent to the State’s submittal of a
complete request remain applicable
until a redesignation to attainment is
approved, but are not required as a
prerequisite to redesignation. See
section 175A(c) of the CAA. Sierra Club
v. EPA, 375 F.3d 537 (7th Cir. 2004). See
also 68 FR 25424, 25427 (May 12, 2003)
(Redesignation of the St. Louis/East St.
Louis area to attainment of the 1-hour
ozone NAAQS).
Since EPA is proposing here to
determine that the areas have attained
the 1997 8-hour ozone standard, under
40 CFR 51.918, if these determinations
are finalized, the requirements to submit
certain planning SIPs related to
attainment, including attainment
demonstration requirements (the RACM
requirement of section 172(c)(1) of the
CAA, the RFP and attainment
demonstration requirements of sections
172(c)(2) and (c)(6) of the CAA, and the
requirement for contingency measures
PO 00000
Frm 00027
Fmt 4702
Sfmt 4702
2009
4th high
(ppm)
0.075
0.078
2006–2008
average
(ppm)
2007–2009
average
(ppm)
0.080
0.075
0.078
0.075
of section 172(c)(9) of the CAA), would
not be applicable to the areas as long as
they continue to attain the NAAQS and
would cease to apply upon
redesignation. In addition, in the
context of redesignations, EPA has
interpreted requirements related to
attainment as not applicable for
purposes of redesignation. For example,
in the General Preamble EPA stated that:
[t]he section 172(c)(9) requirements are
directed at ensuring RFP and attainment by
the applicable date. These requirements no
longer apply when an area has attained the
standard and is eligible for redesignation.
Furthermore, section 175A for maintenance
plans * * * provides specific requirements
for contingency measures that effectively
supersede the requirements of section
172(c)(9) for these areas. ‘‘General Preamble
for the Interpretation of Title I of the Clean
Air Act Amendments of 1990,’’ (General
Preamble) 57 FR 13498, 13564 (April 16,
1992).
See also Calcagni memorandum at 6
(‘‘The requirements for reasonable
further progress and other measures
needed for attainment will not apply for
redesignations because they only have
meaning for areas not attaining the
standard.’’).
a. The Manitowoc County and Door
County Areas Have Met All Applicable
Requirements for Purposes of
Redesignation Under Section 110 and
Part D of the CAA
i. Section 110 General SIP requirements
Section 110(a) of Title I of the CAA
contains the general requirements for a
SIP. Section 110(a)(2) provides that the
implementation plan submitted by a
State must have been adopted by the
State after reasonable public notice and
hearing, and, among other things, must:
Include enforceable emission
limitations and other control measures,
means or techniques necessary to meet
the requirements of the CAA; provide
for establishment and operation of
appropriate devices, methods, systems
and procedures necessary to monitor
ambient air quality; provide for
implementation of a source permit
E:\FR\FM\27APP1.SGM
27APP1
mstockstill on DSKH9S0YB1PROD with PROPOSALS
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
program to regulate the modification
and construction of any stationary
source within the areas covered by the
plan; include provisions for the
implementation of part C, Prevention of
Significant Deterioration (PSD) and part
D, NSR permit programs; include
criteria for stationary source emission
control measures, monitoring, and
reporting; include provisions for air
quality modeling; and provide for
public and local agency participation in
planning and emission control rule
development.
Section 110(a)(2)(D) of the CAA
requires that SIPs contain measures to
prevent sources in a State from
significantly contributing to air quality
problems in another State. To
implement this provision, EPA has
required certain States to establish
programs to address transport of air
pollutants (NOX SIP Call 1 and Clean Air
Interstate Rule (CAIR) (70 FR 25162,
May 12, 2005)). However, the section
110(a)(2)(D) requirements for a State are
not linked with a particular
nonattainment area’s designation and
classification. EPA believes that the
requirements linked with a particular
nonattainment area’s designation and
classification are the relevant measures
to evaluate in reviewing a redesignation
request. The transport SIP submittal
requirements, where applicable,
continue to apply to a State regardless
of the designation of any one particular
area in the State. Thus, we believe that
these requirements should not be
construed to be applicable requirements
for purposes of redesignation.
Further, we believe that the other
section 110 elements described above
that are not connected with
nonattainment plan submissions and
not linked with an area’s attainment
status are also not applicable
requirements for purposes of
redesignation. A State remains subject
to these requirements after an area is
redesignated to attainment. We
conclude that only the section 110 and
part D requirements that are linked with
a particular area’s designation and
classification are the relevant measures
that we may consider in evaluating a
redesignation request. This approach is
consistent with EPA’s existing policy on
applicability of conformity and
oxygenated fuels requirements for
redesignation purposes, as well as with
section 184 ozone transport
requirements. See Reading,
1 On October 27, 1998 (63 FR 57356), EPA issued
a NOX SIP Call requiring the District of Columbia
and 22 States to reduce emissions of NOX in order
to reduce the transport of ozone and ozone
precursors. Wisconsin was not included in EPA’s
NOX SIP Call.
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
Pennsylvania, proposed and final
rulemakings (61 FR 53174–53176,
October 10, 1996), (62 FR 24826, May 7,
1997); Cleveland-Akron-Lorain, Ohio,
final rulemaking (61 FR 20458, May 7,
1996); and Tampa, Florida, final
rulemaking (60 FR 62748, December 7,
1995). See also the discussion on this
issue in the Cincinnati, Ohio 1-hour
ozone redesignation (65 FR 37890, June
19, 2000), and in the Pittsburgh,
Pennsylvania 1-hour ozone
redesignation (66 FR 50399, October 19,
2001).
We have reviewed Wisconsin’s SIP
and have concluded that it meets the
general SIP requirements under section
110 of the CAA to the extent they are
applicable for purposes of
redesignation. EPA has previously
approved provisions of the Wisconsin
SIP addressing section 110 elements
under the 1-hour ozone standard (40
CFR 52.2570). Further, in a submittal
dated December 12, 2007, Wisconsin
confirmed that the State continues to
meet the section 110 requirements for
the 8-hour ozone standard. EPA has not
yet taken rulemaking action on this
submittal; however, such approval is
not necessary for redesignation.
ii. Part D Requirements
EPA has determined that, if EPA
finalizes the approval of the base year
emissions inventories discussed in
section VI.C. of this rulemaking, the
Wisconsin SIP will meet the applicable
SIP requirements for the Manitowoc
County and Door County areas
applicable for purposes of redesignation
under part D of the CAA. Subpart 1 of
part D, found in sections 172–176 of the
CAA, sets forth the basic nonattainment
requirements applicable to all
nonattainment areas. Subpart 2 of part
D, which includes section 182 of the
CAA, establishes additional specific
requirements depending on the area’s
nonattainment classification.
Since the Manitowoc County and
Door County areas were not classified
under subpart 2, of Part D at the time
the redesignation requests were
submitted, the subpart 2 requirements
do not apply for purposes of evaluating
the State’s redesignation requests. The
applicable subpart 1 requirements are
contained in sections 172(c)(1)–(9) and
in section 176.
Subpart 1 Section 172 Requirements
For purposes of evaluating these
redesignation requests, the applicable
section 172 SIP requirements for the
Manitowoc County and Door County
areas are contained in sections
172(c)(1)–(9). A thorough discussion of
the requirements contained in section
PO 00000
Frm 00028
Fmt 4702
Sfmt 4702
22053
172 can be found in the General
Preamble for Implementation of Title I
(57 FR 13498, April 16, 1992).
Section 172(c)(1) requires the plans
for all nonattainment areas to provide
for the implementation of all RACM as
expeditiously as practicable and to
provide for attainment of the primary
NAAQS. EPA interprets this
requirement to impose a duty on all
nonattainment areas to consider all
available control measures and to adopt
and implement such measures as are
reasonably available for implementation
in each area as components of the area’s
attainment demonstration. Because
attainment has been reached, no
additional measures are needed to
provide for attainment, and section
172(c)(1) requirements are no longer
considered to be applicable as long as
the area continues to attain the standard
until redesignation. (40 CFR 51.918).
The RFP requirement under section
172(c)(2) is defined as progress that
must be made toward attainment. This
requirement is not relevant for purposes
of redesignation because the Manitowoc
County and Door County areas have
monitored attainment of the ozone
NAAQS. (General Preamble, 57 FR
13564). See also 40 CFR 51.918. In
addition, because the Manitowoc
County and Door County areas have
attained the ozone NAAQS and are no
longer subject to an RFP requirement,
the requirement to submit the section
172(c)(9) contingency measures is not
applicable for purposes of
redesignation. Id.
Section 172(c)(3) requires submission
and approval of a comprehensive,
accurate and current inventory of actual
emissions. Wisconsin submitted 2005
base year emissions inventories on June
12, 2007. As discussed below in section
VI.C., EPA is proposing to approve the
2005 base year inventories as meeting
the section 172(c)(3) emissions
inventory requirement for the
Manitowoc County and Door County
areas.
Section 172(c)(4) requires the
identification and quantification of
allowable emissions for major new and
modified stationary sources in an area,
and section 172(c)(5) requires source
permits for the construction and
operation of new and modified major
stationary sources anywhere in the
nonattainment area. EPA approved
Wisconsin’s current NSR program on
December 17, 2008 (73 FR 76558 and
76560). Nonetheless, EPA has
determined that, since PSD
requirements will apply after
redesignation, areas being redesignated
need not comply with the requirement
that a nonattainment NSR program be
E:\FR\FM\27APP1.SGM
27APP1
22054
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
mstockstill on DSKH9S0YB1PROD with PROPOSALS
approved prior to redesignation,
provided that the area demonstrates
maintenance of the NAAQS without
part D NSR. A more detailed rationale
for this view is described in a
memorandum from Mary Nichols,
Assistant Administrator for Air and
Radiation, dated October 14, 1994,
entitled, ‘‘Part D New Source Review
Requirements for Areas Requesting
Redesignation to Attainment.’’
Wisconsin has demonstrated that the
Manitowoc County and Door County
areas will be able to maintain the
standard without part D NSR in effect;
therefore, the State need not have a fully
approved part D NSR program prior to
approval of the redesignation request.
The State’s PSD program will become
effective in the Manitowoc County and
Door County areas upon redesignation
to attainment. See rulemakings for
Detroit, Michigan (60 FR 12467–12468,
March 7, 1995); Cleveland-AkronLorain, Ohio (61 FR 20458, 20469–
20470, May 7, 1996); Louisville,
Kentucky (66 FR 53665, October 23,
2001); and Grand Rapids, Michigan (61
FR 31834–31837, June 21, 1996).
Section 172(c)(6) requires the SIP to
contain control measures necessary to
provide for attainment of the standard.
Because attainment has been reached,
no additional measures are needed to
provide for attainment.
Section 172(c)(7) requires the SIP to
meet the applicable provisions of
section 110(a)(2). As noted above, we
believe the Wisconsin SIP meets the
requirements of section 110(a)(2)
applicable for purposes of
redesignation.
Subpart 1 Section 176 Conformity
Requirements
Section 176(c) of the CAA requires
States to establish criteria and
procedures to ensure that Federallysupported or funded activities,
including highway projects, conform to
the air quality planning goals in the
applicable SIPs. The requirement to
determine conformity applies to
transportation plans, programs and
projects developed, funded or approved
under Title 23 of the U.S. Code and the
Federal Transit Act (transportation
conformity) as well as to all other
Federally-supported or funded projects
(general conformity). State conformity
revisions must be consistent with
Federal conformity regulations relating
to consultation, enforcement, and
enforceability, which EPA promulgated
pursuant to CAA requirements.
EPA believes that it is reasonable to
interpret the conformity SIP
requirements as not applying for
purposes of evaluating the redesignation
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
request under section 107(d) for two
reasons. First, the requirement to submit
SIP revisions to comply with the
conformity provisions of the CAA
continues to apply to areas after
redesignation to attainment since such
areas would be subject to a section 175A
maintenance plan. Second, EPA’s
Federal conformity rules require the
performance of conformity analyses in
the absence of Federally-approved State
rules. Therefore, because areas are
subject to the conformity requirements
regardless of whether they are
redesignated to attainment and, because
they must implement conformity under
Federal rules if State rules are not yet
approved, EPA believes it is reasonable
to view these requirements as not
applying for purposes of evaluating a
redesignation request. See Wall v. EPA,
265 F.3d 426 (6th Cir. 2001), upholding
this interpretation. See also 60 FR
62748, 62749–62750 (Dec. 7, 1995)
(Tampa, Florida).
EPA approved Wisconsin’s general
and transportation conformity SIPs on
July 29, 1996 (61 FR 39329), and August
27, 1996 (61 FR 43970), respectively.
Section 176(c) of the CAA was amended
by provisions contained in the Safe,
Accountable, Flexible, Efficient
Transportation Equity Act: A Legacy for
Users (SAFETEALU), which was signed
into law on August 10, 2005 (Pub. L.
109–59). Among the changes Congress
made to this section of the CAA were
streamlined requirements for State
conformity SIPs. Wisconsin is in the
process of updating its transportation
conformity SIP to meet these new
requirements. Wisconsin has submitted
onroad MVEBs for the Manitowoc
County area of 1.76 and 1.25 tpd VOC
and 3.76 and 1.86 tpd NOX for the years
2012 and 2020, respectively and MVEBs
for the Door County area of 0.78 and
0.53 tpd VOC and 1.55 and 0.74 tpd
NOX for the years 2012 and 2020,
respectively. The areas must use the
MVEBs from the maintenance plans in
any conformity determination that is
effective on or after the effective date of
the adequacy finding and/or the
maintenance plans’ approval.
b. The Manitowoc County and Door
County Areas Have Fully Approved
Applicable SIPs under Section 110(k) of
the CAA
If EPA issues a final approval of the
base year emissions inventories, EPA
will have fully approved the Wisconsin
SIP for the Manitowoc County and Door
County areas under section 110(k) of the
CAA for all requirements applicable for
purposes of redesignation. EPA may rely
on prior SIP approvals in approving a
redesignation request (See page 3 of the
PO 00000
Frm 00029
Fmt 4702
Sfmt 4702
September 4, 1992, John Calcagni
memorandum; Southwestern
Pennsylvania Growth Alliance v.
Browner, 144 F.3d 984, 989–990 (6th
Cir. 1998); Wall v. EPA, 265 F.3d 426
(6th Cir. 2001)) plus any additional
measures it may approve in conjunction
with a redesignation action. See 68 FR
25413, 25426 (May 12, 2003). Since the
passage of the CAA of 1970, Wisconsin
has adopted and submitted, and EPA
has fully approved, provisions
addressing various required SIP
elements under the 1-hour ozone
standard. In this action, EPA is
proposing to approve Wisconsin’s 2005
base year emissions inventories for the
Manitowoc County and Door County
areas as meeting the requirement of
section 172(c)(3) of the CAA. No
Manitowoc County or Door County area
SIP provisions are currently
disapproved, conditionally approved, or
partially approved.
3. The Improvement in Air Quality Is
Due to Permanent and Enforceable
Reductions in Emissions Resulting From
Implementation of the SIP and
Applicable Federal Air Pollution
Control Regulations and Other
Permanent and Enforceable Reductions
(Section 107(d)(3)(E)(iii))
EPA finds that Wisconsin has
demonstrated that the observed air
quality improvement in the Manitowoc
County and Door County areas is due to
permanent and enforceable reductions
in emissions resulting from
implementation of the SIPs, Federal
measures, and other State-adopted
measures.
In making this demonstration, WDNR
has calculated the change in emissions
between 2002 and 2007. Wisconsin
developed an emissions inventory for
2002, one of the years used to designate
the areas as nonattainment. The State
developed an attainment inventory for
2007, one of the years the Manitowoc
County and Door County areas
monitored attainment. The reduction in
emissions and the corresponding
improvement in air quality over this
time period can be attributed to a
number of regulatory control measures
that Manitowoc and Door Counties and
upwind areas have implemented in
recent years.
a. Permanent and Enforceable Controls
Implemented
The following is a discussion of
permanent and enforceable measures
that have been implemented in the
areas:
E:\FR\FM\27APP1.SGM
27APP1
mstockstill on DSKH9S0YB1PROD with PROPOSALS
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
i. Federal Emission Control Measures
Reductions in VOC and NOX
emissions have occurred statewide and
in upwind areas as a result of Federal
emission control measures, with
additional emission reductions expected
to occur in the future. Federal emission
control measures include the following.
Tier 2 Emission Standards for
Vehicles and Gasoline Sulfur Standards.
These emission control requirements
result in lower VOC and NOX emissions
from new cars and light duty trucks,
including sport utility vehicles. The
Federal rules were phased in between
2004 and 2009. The EPA has estimated
that, by the end of the phase-in period,
the following vehicle NOX emission
reductions will occur nationwide:
Passenger cars (light duty vehicles) (77
percent); light duty trucks, minivans,
and sports utility vehicles (86 percent);
and, larger sports utility vehicles, vans,
and heavier trucks (69 to 95 percent).
VOC emission reductions are expected
to range from 12 to 18 percent,
depending on vehicle class, over the
same period. Some of these emission
reductions occurred by the 2007–2009
period used to demonstrate attainment,
and additional emission reductions will
occur during the maintenance period.
Heavy-Duty Diesel Engine Rule. EPA
issued this rule in July 2000. This rule
includes standards limiting the sulfur
content of diesel fuel, which went into
effect in 2004. A second phase took
effect in 2007 which further reduced the
highway diesel fuel sulfur content to 15
ppm, leading to additional reductions in
combustion NOX and VOC emissions.
This rule is expected to achieve a 95
percent reduction in NOX emissions
from diesel trucks and busses.
Non-Road Diesel Rule. EPA issued
this rule in 2004. This rule applies to
diesel engines used in industries, such
as construction, agriculture, and mining.
It is estimated that compliance with this
rule will cut NOX emissions from nonroad diesel engines by up to 90 percent.
This rule is currently achieving
emission reductions, but will not be
fully implemented until 2010.
Maximum Achievable Control
Technology (MACT) Rules. EPA has
promulgated numerous MACT
standards, many of which limit VOC
emissions. Compliance began for many
of the MACT rules from late 2005
through 2007.
ii. Control Measures in Upwind Areas
NOX Reasonably Available Control
Technology (RACT). Wisconsin adopted
NOX RACT regulations for the upwind
Milwaukee-Racine area. The emission
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
requirements apply to stationary
combustion units at major sources, with
compliance required by May 1, 2009.
The RACT rule is estimated to achieve
reductions of over 29,000 tpy of NOX
emissions from 2002 levels.
NOX SIP Call. On October 27, 1998
(63 FR 57356), EPA issued a NOX SIP
Call requiring the District of Columbia
and 22 States to reduce emissions of
NOX. Affected States were required to
comply with Phase I of the SIP Call
beginning in 2004, and Phase II
beginning in 2007. The reduction in
NOX emissions has resulted in lower
concentrations of transported ozone
entering the Manitowoc County and
Door County areas. Emission reductions
resulting from regulations developed in
response to the NOX SIP Call are
permanent and enforceable.
b. Emission Reductions
States are required to develop
periodic emissions inventories every
three years. (40 CFR part 51, subpart A).
Wisconsin is using the periodic
emissions inventory from 2002 as the
nonattainment inventory. Point source
sector emissions inventories were
developed using reported point source
emissions, EPA’s Clean Air Markets
database and approved EPA techniques
for emissions calculations. Emissions
were estimated by collecting processlevel information from each facility that
qualifies for inclusion into WDNR’s
point source database. Process, boiler,
fugitive and tank emissions were
typically calculated using throughput
information multiplied by an emission
factor for the process. Emission factor
sources included mass balance, stack
testing, continuous emissions monitors,
engineering judgment and EPA’s Factor
Information Retrieval database.
Area source emissions were generated
by backcasting from the 2005 periodic
emissions inventory to minimize
differences between the nonattainment
and attainment inventories due to
changes in methodology. The
backcasting factors were based on 2002–
2008 growth factors including the
Census Bureau’s County Business
Pattern employment data, growth factors
developed for the Lake Michigan Air
Directors Consortium (LADCO) by E.H.
Pechan & Associates, Inc. (Pechan); and
the Economic Growth Analysis System
(EGAS6.0). Area source emissions
estimates for the 2005 periodic
inventory were calculated using
population, gasoline consumption,
employment, crop acreages, and other
activity surrogates. The results of an
EPA Solvent Mass Balance study were
PO 00000
Frm 00030
Fmt 4702
Sfmt 4702
22055
used to estimate emissions for some
categories. Emission factors were
derived from local data, local or
national surveys and EPA guidance for
the development of emissions
inventories. Point source emissions
were subtracted from total category
specific area source emissions to
prevent double counting.
Nonroad mobile source emissions
were calculated using EPA’s National
Mobile Inventory Model (NMIM) and
emissions estimates developed for
commercial marine vessels, aircraft, and
railroads (MAR), three nonroad
categories not included in NMIM.
Before NMIM was run, the following
modifications and additions were made
to the NMIM input data: (1) Revised
activity data for construction equipment
using updates provided by Pechan; (2)
revised allocation data for recreational
marine equipment using updates
provided by ENVIRON International
Corporation (ENVIRON); (3) added
emission factors for diesel tampers/
rammers provided by Pechan; (4)
revised population data for construction
and recreational marine equipment
using updates provided by Pechan and
ENVIRON, respectively; (5) revised
growth rates using updates provided by
Pechan; and (6) revised gasoline
parameters, including Reid Vapor
Pressure, oxygenate content and sulfur
content, using updates provided by the
States and Pechan. Onroad mobile
source emissions were calculated using
the MOBILE6.2 emissions model.
Wisconsin developed a 2007
attainment year inventory using the
methodologies described above to
estimate point, nonroad mobile and
onroad mobile sector emissions. Area
source emissions were generated by
applying growth factors and applicable
emission controls to the 2005 area
source sector inventory. Growth factors
include the Census Bureau’s County
Business Pattern employment data,
growth factors developed for LADCO by
Pechan; and EGAS6.0.
Using the inventories described
above, Wisconsin’s submittal
documents changes in VOC and NOX
emissions from 2002 to 2007 for the
Manitowoc County and Door County
areas. Because Manitowoc and Door
Counties are impacted by transport,
WDNR also documented emissions
reductions for the upwind Wisconsin
areas of Sheboygan and MilwaukeeRacine. Emissions data are shown in
Tables 2 through 6 below.
BILLING CODE 6560–50–P
E:\FR\FM\27APP1.SGM
27APP1
22056
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
PO 00000
Frm 00031
Fmt 4702
Sfmt 4702
E:\FR\FM\27APP1.SGM
27APP1
EP27AP10.002
mstockstill on DSKH9S0YB1PROD with PROPOSALS
BILLING CODE 6560–50–C
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
mstockstill on DSKH9S0YB1PROD with PROPOSALS
4. The Area Has a Fully Approved
Maintenance Plan Pursuant to Section
175A of the CAA (Section
107(d)(3)(E)(iv))
In conjunction with its requests to
redesignate the Manitowoc County and
Door County nonattainment areas to
attainment status, Wisconsin submitted
SIP revisions to provide for the
maintenance of the 8-hour ozone
NAAQS in the areas through 2020.
a. What is required in a maintenance
plan?
Section 175A of the CAA sets forth
the required elements of a maintenance
plan for areas seeking redesignation
from nonattainment to attainment.
Under section 175A, the plan must
demonstrate continued attainment of
the applicable NAAQS for at least ten
years after the Administrator approves a
redesignation to attainment. Eight years
after the redesignation, the State must
submit a revised maintenance plan
which demonstrates that attainment will
continue to be maintained for ten years
following the initial ten-year
maintenance period. To address the
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
possibility of future NAAQS violations,
the maintenance plan must contain
contingency measures with a schedule
for implementation as EPA deems
necessary to assure prompt correction of
any future 8-hour ozone violations.
The September 4, 1992, John Calcagni
memorandum provides additional
guidance on the content of a
maintenance plan. The memorandum
clarifies that an ozone maintenance plan
should address the following items: the
attainment VOC and NOX emissions
inventories, a maintenance
demonstration showing maintenance for
the ten years of the maintenance period,
a commitment to maintain the existing
monitoring network, factors and
procedures to be used for verification of
continued attainment of the NAAQS,
and a contingency plan to prevent or
correct future violations of the NAAQS.
b. Attainment Inventory
The WDNR developed emissions
inventories for 2007, one of the years
used to demonstrate monitored
attainment of the 8-hour NAAQS, as
described above. The attainment level of
emissions is summarized in Table 3,
above.
c. Demonstration of Maintenance
Along with the redesignation
requests, WDNR submitted revisions to
the Wisconsin 8-hour ozone SIP to
include maintenance plans for the
Manitowoc County and Door County
areas, as required by section 175A of the
CAA. These demonstrations show
maintenance of the 8-hour ozone
standard through 2020 by showing that
current and future emissions of VOC
and NOX for the areas remain at or
below attainment year emission levels.
A maintenance demonstration need not
be based on modeling. See Wall v. EPA,
265 F.3d 426 (6th Cir. 2001), Sierra Club
PO 00000
Frm 00032
Fmt 4702
Sfmt 4702
v. EPA, 375 F. 3d 537 (7th Cir. 2004).
See also 66 FR 53094, 53099–53100
(October 19, 2001), 68 FR 25413, 25430–
25432 (May 12, 2003).
Wisconsin is using emissions
inventory projections for the years 2012
and 2020 to demonstrate maintenance.
Emissions estimates were generated for
point sources, area sources, and the
MAR portion of the nonroad mobile
sector by applying growth factors and
applicable emission controls to the 2005
emissions inventory. The 2005
emissions inventory was developed
following the same methodologies
described for the 2002 inventory, in
section VI.A.3.b., above. Growth factors
include the Census Bureau’s County
Business Pattern employment data,
growth factors developed for LADCO by
Pechan; and EGAS6.0. Growth factors
were only available for emission
projections to 2018. Emissions for 2020
were estimated using linear
interpolation from 2018. For Electric
Generating Unit (EGU) point sources,
projections were performed on a facility
by facility basis. The growth in
generation emissions considers
corporate utility growth in electricity
demand and the potential dispatch by
the regional Midwest Independent
Transmission System Operator to meet
broader demand. The growth in
electricity consumption by load type is
based on growth rate projections by the
Wisconsin Public Service Commission
and historic growth rates. Nonroad
mobile emissions, excluding MAR, were
calculated using NMIM with the
modifications and additions to the input
data described in section VI.A.3.b.,
above. Onroad mobile source emissions
were calculated using the MOBILE6.2
emissions model. Emissions data are
shown in Tables 7 through 11, below.
BILLING CODE 6560–50–P
E:\FR\FM\27APP1.SGM
27APP1
EP27AP10.003
Table 4 shows that the Manitowoc
County area reduced VOC emissions by
1.85 tpd and NOX emissions by 2.32 tpd
between 2002 and 2007. Table 5 shows
that the Door County area reduced VOC
emissions by 1.23 tpd and NOX
emissions by 2.17 tpd between 2002 and
2007. In addition, as shown in Table 6,
the upwind areas of Sheboygan and
Milwaukee-Racine reduced VOC
emissions by 39.90 tpd and NOX
emissions by 125.08 tpd between 2002
and 2007. Based on the information
summarized above, Wisconsin has
adequately demonstrated that the
improvement in air quality is due to
permanent and enforceable emissions
reductions.
22057
22058
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
PO 00000
Frm 00033
Fmt 4702
Sfmt 4702
E:\FR\FM\27APP1.SGM
27APP1
EP27AP10.004
mstockstill on DSKH9S0YB1PROD with PROPOSALS
BILLING CODE 6560–50–C
22059
The emission projections show that
Wisconsin does not expect emissions in
the Manitowoc County and Door County
areas to exceed the level of the 2007
attainment year inventory during the
maintenance period, even without
implementation of CAIR. (See also
discussion below.) As shown in Table 9,
VOC and NOX emissions in the
Manitowoc County area are projected to
decrease by 0.99 tpd and 3.88 tpd,
respectively, between 2007 and 2020.
As shown in Table 10, VOC and NOX
emissions in the Door County area are
projected to decrease by 2.96 tpd and
1.27 tpd, respectively, between 2007
and 2020. In addition, as shown in
Table 11, VOC and NOX emissions in
the upwind areas of Sheboygan and
Milwaukee-Racine are projected to
decrease by 16.20 tpd and 66.63 tpd,
respectively, between 2007 and 2020.
In addition, LADCO performed a
regional modeling analysis to address
the effect of the recent court decision
vacating CAIR. This analysis is
documented in LADCO’s ‘‘Regional Air
Quality Analyses for Ozone, PM2.5, and
Regional Haze: Final Technical Support
Document (Supplement), September 12,
2008.’’ LADCO produced a base year
inventory for 2005 and future year
inventories for 2009, 2012, and 2018. To
estimate future EGU NOX emissions
without implementation of CAIR,
LADCO projected 2007 EGU NOX
emissions for all States in the modeling
domain based on Energy Information
Administration growth rates by State
(North American Electric Reliability
Corporation (NERC) region) and fuel
type for the years 2009, 2012 and 2018.
The assumed 2007–2018 growth rates
were 8.8% for Illinois, Iowa, Missouri
and Wisconsin; 13.5% for Indiana,
Kentucky, Michigan and Ohio; and
15.1% for Minnesota. Emissions were
adjusted by applying legally enforceable
controls, e.g., consent decree or rule.
EGU NOX emissions projections for the
States of Illinois, Indiana, Michigan,
Ohio, and Wisconsin are shown below
in Table 12. The emission projections
used for the modeling analysis do not
account for certain relevant factors such
as allowance trading and potential
changes in operation of existing control
devices. The NOX projections indicate
that, due to the NOX SIP Call, certain
State rules, consent decrees resulting
from enforcement cases, and ongoing
implementation of a number of mobile
source rules, EGU NOX is not expected
to increase in Wisconsin, or any of the
States in the immediate region, and
overall NOX emissions in Wisconsin,
and the nearby region are expected to
decrease substantially between 2005
and 2020.2 Total NOX emissions
projections are shown in Table 13,
below.
2 There is more uncertainty about the use of SO
2
allowances and future projections for SO2
emissions; thus, further review and discussion will
be needed regarding the appropriateness of using
these emission projections for future PM2.5 SIP
approvals and redesignation requests.
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
PO 00000
Frm 00034
Fmt 4702
Sfmt 4702
E:\FR\FM\27APP1.SGM
27APP1
EP27AP10.005
mstockstill on DSKH9S0YB1PROD with PROPOSALS
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
22060
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
TABLE 12—EGU NOX EMISSIONS FOR THE STATES OF ILLINOIS, INDIANA, MICHIGAN, OHIO AND WISCONSIN (TPD) FOR
2007, 2009, 2012, AND 2018
2007
EGU .................................................................................................................................................
1,582
2009
1,552
2012
1,516
2018
1,524
TABLE 13—TOTAL NOX EMISSIONS FOR THE STATES OF ILLINOIS, INDIANA, MICHIGAN, OHIO AND WISCONSIN (TPD) FOR
THE YEARS 2005, 2009, 2012, AND 2018
2005
mstockstill on DSKH9S0YB1PROD with PROPOSALS
Total NOX ........................................................................................................................................
Given that 2007 is one of the years
Wisconsin used to demonstrate
monitored attainment of the 8-hour
NAAQS, Table 12 shows that EGU NOX
emissions will remain below attainment
levels through 2018. If the rate of
emissions increase between 2012 and
2018 continues through 2020, EGU NOX
emissions would still remain below
attainment levels in 2020. Furthermore,
as shown in Table 13, total NOX
emissions clearly continue to decrease
substantially throughout the
maintenance period.
Ozone modeling performed by
LADCO supports the conclusion that the
Manitowoc County and Door County
areas will maintain the standard
throughout the maintenance period.
Peak modeled ozone levels in the
Manitowoc County area for 2009, 2012
and 2018 are 0.081 ppm, 0.079 ppm,
and 0.073 ppm, respectively. Peak
modeled ozone levels in the Door
County area for 2009, 2012 and 2018 are
0.084 ppm, 0.081 ppm, and 0.076 ppm,
respectively. These projected ozone
levels were modeled applying only
legally enforceable controls; e.g.,
consent decrees, rules, the NOX SIP
Call, Federal motor vehicle control
programs, etc. Because these programs
will remain in place, emission levels,
and therefore ozone levels, would not be
expected to increase significantly
between 2018 and 2020. Given that
projected emissions and modeled ozone
levels continue to decrease substantially
through 2018, it is reasonable to infer
that a 2020 modeling run would also
show levels well below the 1997 8-hour
ozone standard.
EPA has considered the relationship
of the maintenance plans to the
reductions required pursuant to CAIR.
This rule was remanded to EPA, and the
process of developing a replacement
rule is ongoing. However, the remand of
CAIR does not alter the requirements of
the NOX SIP Call, and Wisconsin has
demonstrated maintenance without any
additional CAIR requirements (beyond
those required by the NOX SIP Call).
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
Therefore, EPA believes that
Wisconsin’s demonstration of
maintenance under sections 175A and
107(d)(3)(E) is valid.
The NOX SIP Call requires States to
make significant, specific emissions
reductions. It also provided a
mechanism, the NOX Budget Trading
Program, which States could use to
achieve those reductions. When EPA
promulgated CAIR, it discontinued
(starting in 2009) the NOX Budget
Trading Program, 40 CFR 51.121(r), but
created another mechanism, the CAIR
ozone season trading program, which
States could use to meet their SIP Call
obligations (70 FR 25289–25290). EPA
notes that a number of States, when
submitting SIP revisions to require
sources to participate in the CAIR ozone
season trading program, removed the
SIP provisions that required sources to
participate in the NOX Budget Trading
Program. In addition, because the
provisions of CAIR, including the ozone
season NOX trading program, remain in
place during the remand, EPA is not
currently administering the NOX Budget
Trading Program. Nonetheless, all
States, regardless of the current status of
their regulations that previously
required participation in the NOX
Budget Trading Program, will remain
subject to all of the requirements in the
NOX SIP Call even if the existing CAIR
ozone season trading program is
withdrawn or altered. In addition, the
anti-backsliding provisions of 40 CFR
51.905(f) specifically provide that the
provisions of the NOX SIP Call,
including the statewide NOX emission
budgets, continue to apply after
revocation of the 1-hour standard.
All NOX SIP Call States have SIPs that
currently satisfy their obligations under
the SIP Call, the SIP Call reduction
requirements are being met, and EPA
will continue to enforce the
requirements of the NOX SIP Call even
after any response to the CAIR remand.
For these reasons, EPA believes that
regardless of the status of the CAIR
program, the NOX SIP Call requirements
PO 00000
Frm 00035
Fmt 4702
Sfmt 4702
8,260
2009
6,778
2012
6,076
2018
4,759
can be relied upon in demonstrating
maintenance.
d. Monitoring Network
Wisconsin currently operates one
ozone monitor in Manitowoc County
and one ozone monitor in Door County.
Wisconsin has committed to continue to
operate and maintain an approved
ozone monitoring network in the
Manitowoc County and Door County
areas. WDNR has also committed to
consult with EPA regarding any changes
in siting that may become necessary in
the future. Wisconsin remains obligated
to continue to quality assure monitoring
data in accordance with 40 CFR part 58
and enter all data into the AQS in
accordance with Federal guidelines.
e. Verification of Continued Attainment
Continued attainment of the ozone
NAAQS in the Manitowoc County and
Door County areas depends, in part, on
the State’s efforts toward tracking
indicators of continued attainment
during the maintenance period.
Wisconsin’s plan for verifying
continued attainment of the 8-hour
standard in the Manitowoc County and
Door County areas consists of continued
ambient ozone monitoring in
accordance with the requirements of 40
CFR part 58. WDNR will also continue
to develop and submit periodic
emission inventories as required by the
Federal Consolidated Emissions
Reporting Rule (67 FR 39602, June 10,
2002), and will evaluate future VOC and
NOX emissions inventories for increases
over the 2007 emission inventory levels.
f. Contingency Plan
The contingency plan provisions are
designed to promptly correct or prevent
a violation of the NAAQS that might
occur after redesignation of an area to
attainment. Section 175A of the CAA
requires that a maintenance plan
include such contingency measures as
EPA deems necessary to assure that the
State will promptly correct a violation
of the NAAQS that occurs after
E:\FR\FM\27APP1.SGM
27APP1
mstockstill on DSKH9S0YB1PROD with PROPOSALS
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
redesignation. The maintenance plan
should identify the contingency
measures to be adopted, a schedule and
procedure for adoption and
implementation of the contingency
measures, and a time limit for action by
the State. The State should also identify
specific indicators to be used to
determine when the contingency
measures need to be adopted and
implemented. The maintenance plan
must include a requirement that the
State will implement all measures with
respect to control of the pollutant(s) that
were contained in the SIP before
redesignation of the area to attainment.
See section 175A(d) of the CAA.
As required by section 175A of the
CAA, Wisconsin has adopted
contingency plans for the Manitowoc
County and Door County areas to
address possible future ozone air quality
problems. A contingency plan response
will be triggered whenever a three-year
average fourth-high monitored value of
0.085 ppm or greater is monitored
within the maintenance area. When a
response is triggered, WDNR will
evaluate existing but not fully
implemented, on-the way, and, if
necessary, new control measures to
correct the violation of the standard
within 18 months. The State has
confirmed EPA’s interpretation that this
commitment means that the measure
will be adopted and implemented
within 18 months of the triggering
event. In addition, it is EPA’s
understanding that to acceptably
address a violation of the standard,
existing and on-the way control
measures must be in excess of emissions
reductions included in the projected
maintenance inventories.
WDNR included the following list of
potential contingency measures in its
maintenance plans:
i. Broaden the application of the NOX
RACT program by including a larger
geographic area, and/or including
sources with potential emissions of 50
tons per year, and/or increasing the
cost-effectiveness thresholds utilized as
a basis for Wisconsin’s NOX RACT
Program;
ii. Develop an anti-idling control
program for mobile sources targeting
diesel vehicles;
iii. Adopt a rule reducing VOC
content in architectural, industrial and
maintenance coatings; and
iv. Adopt a rule reducing VOC
content in commercial and consumer
products.
g. Provisions for Future Updates of the
Ozone Maintenance Plan
As required by section 175A(b) of the
CAA, WDNR commits to submit to the
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
EPA updated ozone maintenance plans
eight years after redesignation of the
Manitowoc County and Door County
areas to cover an additional ten-year
period beyond the initial ten-year
maintenance period. As required by
section 175A of the CAA, Wisconsin has
committed to retain the VOC and NOX
control measures contained in the SIP
prior to redesignation.
EPA has concluded that the
maintenance plans adequately address
the five basic components of a
maintenance plan: Attainment
inventory, maintenance demonstration,
monitoring network, verification of
continued attainment, and a
contingency plan. Thus EPA proposes to
find that the maintenance plan SIP
revisions submitted by Wisconsin for
the Manitowoc County and Door County
areas meet the requirements of section
175A of the CAA.
B. Adequacy of Wisconsin’s MVEBs
1. How are MVEBs developed and what
are the MVEBs for the Manitowoc
County and Door County areas?
Under the CAA, States are required to
submit, at various times, control strategy
SIP revisions and ozone maintenance
plans for ozone nonattainment areas and
for areas seeking redesignations to
attainment of the ozone standard. These
emission control strategy SIP revisions
(e.g., RFP and attainment demonstration
SIP revisions) and ozone maintenance
plans create MVEBs based on onroad
mobile source emissions for criteria
pollutants and/or their precursors to
address pollution from onroad
transportation sources. The MVEBs are
the portions of the total allowable
emissions that are allocated to highway
and transit vehicle use that, together
with emissions from other sources in
the area, will provide for attainment or
maintenance.
Under 40 CFR part 93, a MVEB for an
area seeking a redesignation to
attainment is established for the last
year of the maintenance plan. The
MVEB serves as a ceiling on emissions
from an area’s planned transportation
system. The MVEB concept is further
explained in the preamble to the
November 24, 1993, transportation
conformity rule (58 FR 62188).
Under section 176(c) of the CAA, new
transportation projects that receive
Federal funding or support, such as the
construction of new highways, must
‘‘conform’’ to (i.e., be consistent with)
the SIP. Conformity to the SIP means
that transportation activities will not
cause new air quality violations, worsen
existing air quality violations, or delay
timely attainment of the NAAQS. If a
PO 00000
Frm 00036
Fmt 4702
Sfmt 4702
22061
transportation plan does not conform,
most new transportation projects that
would expand the capacity of roadways
cannot go forward. Regulations at 40
CFR part 93 set forth EPA policy,
criteria, and procedures for
demonstrating and assuring conformity
of such transportation activities to a SIP.
When reviewing SIP revisions
containing MVEBs, including
attainment strategies, rate-of-progress
plans, and maintenance plans, EPA
must affirmatively approve or find that
the MVEBs are ‘‘adequate’’ for use in
determining transportation conformity
before the MVEBs can be used. Once
EPA affirmatively approves or finds the
submitted MVEBs to be adequate for
transportation conformity purposes, the
MVEBs must be used by State and
Federal agencies in determining
whether proposed transportation
projects conform to the SIP as required
by section 176(c) of the CAA. EPA’s
substantive criteria for determining the
adequacy of MVEBs are set out in 40
CFR 93.118(e)(4).
EPA’s process for determining
adequacy of a MVEB consists of three
basic steps: (1) Providing public
notification of a SIP submission; (2)
providing the public the opportunity to
comment on the MVEB during a public
comment period; and, (3) EPA taking
action on the MVEB. The process for
determining the adequacy of submitted
SIP MVEBs is codified at 40 CFR 93.118.
The maintenance plans submitted by
Wisconsin for the Manitowoc County
and Door County areas contain new
VOC and NOX MVEBs for the areas for
the years 2012 and 2020. The
availability of the SIP submission with
these 2012 and 2020 MVEBs was
announced for public comment on
EPA’s Adequacy Web site on February
24, 2010, at: https://www.epa.gov/otaq/
stateresources/transconf/currsips.htm.
The EPA public comment period on
adequacy of the 2012 and 2020 MVEBs
for the Manitowoc County and Door
County areas closed on March 26, 2010.
No adverse comments on the submittal
were received during the adequacy
comment period.
EPA, through this rulemaking, has
found adequate and is proposing to
approve the MVEBs for use to determine
transportation conformity in the
Manitowoc County and Door County
areas, because EPA has determined that
the areas can maintain attainment of the
8-hour ozone NAAQS for the relevant
maintenance period with mobile source
emissions at the levels of the MVEBs.
WDNR has determined the 2012 MVEBs
for the Manitowoc County and Door
County areas to be 1.76 tpd for VOC and
3.76 tpd for NOX, and 0.78 tpd for VOC
E:\FR\FM\27APP1.SGM
27APP1
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
and 1.55 tpd for NOX, respectively.
WDNR has determined the 2020 MVEBs
for the Manitowoc County and Door
County areas to be 1.25 tpd for VOC and
1.86 tpd for NOX, and 0.53 tpd for VOC
and 0.74 tpd for NOX, respectively.
These MVEBs are consistent with the
onroad mobile source VOC and NOX
emissions projected by the Wisconsin
Department of Transportation for 2012
and 2020, as summarized in Tables 9
and 10 above. Wisconsin has
demonstrated that the Manitowoc
County area can maintain the 8-hour
ozone NAAQS with mobile source
emissions of 1.76 tpd and 1.25 tpd of
VOC and 3.76 tpd and 1.86 tpd of NOX
in 2012 and 2020, respectively, since
emissions will remain under attainment
year emission levels. Wisconsin has
demonstrated that the Door County area
can maintain the 8-hour ozone NAAQS
with mobile source emissions of 0.78
tpd and 0.53 tpd of VOC and 1.55 tpd
and 0.74 tpd of NOX in 2012 and 2020,
respectively, since emissions will
remain under attainment year emission
levels.
C. 2005 Base Year Emissions Inventories
As discussed above, section 172(c)(3)
of the CAA requires areas to submit a
base year emissions inventory. On June
12, 2007, WDNR submitted a 2005 base
year emissions inventory to meet this
requirement. Emissions contained in the
submittal cover the general source
categories of point sources, area sources,
mstockstill on DSKH9S0YB1PROD with PROPOSALS
VII. What actions is EPA taking?
EPA is proposing to determine that
the Manitowoc County and Door County
areas have attained the 1997 8-hour
ozone NAAQS. EPA is proposing to
approve the redesignations of the
Manitowoc County and Door County
areas from nonattainment to attainment
for the 1997 8-hour ozone NAAQS.
After evaluating the redesignation
requests submitted by Wisconsin, EPA
believes that the requests meet the
redesignation criteria set forth in section
107(d)(3)(E) of the CAA. The final
approval of these redesignation requests
would change the official designations
for the Manitowoc County and Door
County areas from nonattainment to
attainment for the 1997 8-hour ozone
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
on-road mobile sources, and non-road
mobile sources. All emission summaries
were accompanied by descriptions of
emission calculation procedures and
sources of input data.
Point source sector emissions
inventories were developed using
reported point source emissions, EPA’s
Clean Air Markets database and
approved EPA techniques for emissions
calculations. Emissions were estimated
by collecting process-level information
from each facility that qualifies for
inclusion into WDNR’s point source
database. Process, boiler, fugitive and
tank emissions were typically calculated
using throughput information
multiplied by an emission factor for the
process. Emission factor sources
included mass balance, stack testing,
continuous emissions monitors,
engineering judgment and EPA’s Factor
Information Retrieval database.
Area source emissions were
calculated using population, gasoline
consumption, employment, crop
acreages, and other activity surrogates.
The results of an EPA Solvent Mass
Balance study were used to estimate
emissions for some categories. Emission
factors were derived from local data,
local or national surveys and EPA
guidance for the development of
emissions inventories. Point source
emissions were subtracted from total
category specific area source emissions
to prevent double counting.
Nonroad mobile source emissions
were calculated using EPA’s NMIM and
emissions estimates developed for
commercial marine vessels, aircraft, and
railroads (MAR), three nonroad
categories not included in NMIM.
Before NMIM was run, the following
modifications and additions were made
to the NMIM input data: (1) Revised
activity data for construction equipment
using updates provided by Pechan; (2)
revised allocation data for recreational
marine equipment using updates
provided by ENVIRON International
Corporation (ENVIRON); (3) added
emission factors for diesel tampers/
rammers provided by Pechan; (4)
revised population data for construction
and recreational marine equipment
using updates provided by Pechan and
ENVIRON, respectively; (5) revised
growth rates using updates provided by
Pechan; and (6) revised gasoline
parameters, including Reid Vapor
Pressure, oxygenate content and sulfur
content, using updates provided by the
States and Pechan. Onroad mobile
source emissions were calculated using
the MOBILE6.2 emissions model.
The 2005 summer day emissions of
VOC and NOX for the Manitowoc
County and Door County areas are
summarized in Table 14, below. EPA is
proposing to approve these 2005 base
year inventories as meeting the section
172(c)(3) emissions inventory
requirement.
standard. EPA is also proposing to
approve the maintenance plan SIP
revisions for the Manitowoc County and
Door County areas. EPA’s proposed
approvals of the maintenance plans is
based on the State’s demonstration that
the plans meet the requirements of
section 175A of the CAA, as described
more fully above. EPA is proposing to
approve WDNR’s 2005 base year
emissions inventories for the
Manitowoc County and Door County
areas as meeting the requirements of
section 172(c)(3) of the CAA. Finally,
EPA finds adequate and is proposing to
approve Wisconsin’s 2012 and 2020
MVEBs for the Manitowoc County and
Door County areas.
VIII. Statutory and Executive Order
Reviews
PO 00000
Frm 00037
Fmt 4702
Sfmt 4702
Under the CAA, redesignation of an
area to attainment and the
accompanying approval of a
maintenance plan under section
107(d)(3)(E) are actions that affect the
status of a geographical area and do not
impose any additional regulatory
requirements on sources beyond those
imposed by State law. A redesignation
to attainment does not in and of itself
create any new requirements, but rather
results in the applicability of
requirements contained in the CAA for
areas that have been redesignated to
attainment. Moreover, the Administrator
is required to approve a SIP submission
that complies with the provisions of the
E:\FR\FM\27APP1.SGM
27APP1
EP27AP10.006
22062
mstockstill on DSKH9S0YB1PROD with PROPOSALS
Federal Register / Vol. 75, No. 80 / Tuesday, April 27, 2010 / Proposed Rules
Act and applicable Federal regulations.
42 U.S.C. 7410(k); 40 CFR 52.02(a).
Thus, in reviewing SIP submissions,
EPA’s role is to approve State choices,
provided that they meet the criteria of
the Clean Air Act. Accordingly, these
actions merely do not impose additional
requirements beyond those imposed by
State law and the Clean Air Act. For that
reason, these actions:
• Are not ‘‘significant regulatory
actions’’ subject to review by the Office
of Management and Budget under
Executive Order 12866 (58 FR 51735,
October 4, 1993);
• Do not impose an information
collection burden under the provisions
of the Paperwork Reduction Act (44
U.S.C. 3501 et seq.);
• Are certified as not having a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act
(5 U.S.C. 601 et seq.);
• Do not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4);
• Do not have Federalism
implications as specified in Executive
Order 13132 (64 FR 43255, August 10,
1999);
• Are not an economically significant
regulatory action based on health or
safety risks subject to Executive Order
13045 (62 FR 19885, April 23, 1997);
• Is not a significant regulatory action
subject to Executive Order 13211 (66 FR
28355, May 22, 2001);
• Are not subject to requirements of
section 12(d) of the National
Technology Transfer and Advancement
Act of 1995 (15 U.S.C. 272 note) because
application of those requirements would
be inconsistent with the Clean Air Act;
and
• Do not provide EPA with the
discretionary authority to address, as
appropriate, disproportionate human
health or environmental effects, using
practicable and legally permissible
methods, under Executive Order 12898
(59 FR 7629, February 16, 1994).
In addition, this rule does not have
Tribal implications as specified by
Executive Order 13175 (65 FR 67249,
November 9, 2000), because the SIP is
not approved to apply in Indian country
located in the State, and EPA notes that
it will not impose substantial direct
costs on Tribal governments or preempt
Tribal law.
List of Subjects
40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
VerDate Nov<24>2008
16:07 Apr 26, 2010
Jkt 220001
relations, Ozone, Nitrogen dioxides,
Reporting and recordkeeping
requirements, Volatile organic
compounds.
40 CFR Part 81
Environmental protection, Air
pollution control.
Authority: 42 U.S.C. 7401 et seq.
Dated: April 14, 2010.
Walter W. Kovalick Jr.,
Acting Regional Administrator, Region 5.
[FR Doc. 2010–9753 Filed 4–26–10; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF THE INTERIOR
Fish and Wildlife Service
50 CFR Part 17
[FWS-R8-ES-2010-0006]
[MO 92210-0-0008 B2]
Endangered and Threatened Wildlife
and Plants; 90–day Finding on a
Petition to List the Mohave Ground
Squirrel as Endangered with Critical
Habitat
AGENCY: Fish and Wildlife Service,
Interior.
ACTION: Notice of 90–day petition
finding and initiation of status review.
SUMMARY: We, the U.S. Fish and
Wildlife Service (Service), announce a
90–day finding on a petition to list the
Mohave ground squirrel
(Xerospermophilus mohavensis) as an
endangered species under the
Endangered Species Act of 1973, as
amended (Act). Based on our review, we
find that the petition presents
substantial scientific or commercial
information indicating that listing the
Mohave ground squirrel may be
warranted. Therefore, with the
publication of this notice, we are
initiating a status review of the species
to determine if listing the species is
warranted. To ensure that this status
review is comprehensive, we are
requesting scientific and commercial
data and other information regarding
this species. Based on the status review,
we will issue a 12–month finding on the
petition, which will address whether
the petitioned action is warranted, as
provided in section 4(b)(3)(B) of the Act.
We will make a determination on
critical habitat for this species, which
was also requested in the petition, if and
when we initiate a listing action.
DATES: To allow us adequate time to
conduct this review, we request that we
receive information on or before June
28, 2010. After this date, you must
PO 00000
Frm 00038
Fmt 4702
Sfmt 4702
22063
submit information directly to the
Ventura Fish and Wildlife Office (see
FOR FURTHER INFORMATION CONTACT
section below). Please note that we may
not be able to address or incorporate
information that we receive after the
date noted above.
ADDRESSES: You may submit
information by one of the following
methods:
• Federal eRulemaking Portal: https://
www.regulations.gov. Search for docket
FWS-R8-ES-2010-0006 and then follow
the instructions for submitting
comments.
• U.S. mail or hand-delivery: Public
Comments Processing, Attn: FWS-R8ES-2010-0006; Division of Policy and
Directives Management; U.S. Fish and
Wildlife Service; 4401 N. Fairfax Drive,
Suite 222; Arlington, VA 22203.
We will post all information received
on https://www.regulations.gov. This
generally means that we will post any
personal information you provide us
(see the Information Solicited section
below for more information).
FOR FURTHER INFORMATION CONTACT:
Michael McCrary, Listing and Recovery
Coordinator, Ventura Fish and Wildlife
Office, 2593 Portola Road, Suite B,
Ventura, CA 93003; telephone (805)
644-1766; facsimile (805) 644-3958. If
you use a telecommunications device
for the deaf (TDD), call the Federal
Information Relay Service (FIRS) at
(800) 877-8339.
SUPPLEMENTARY INFORMATION:
Information Solicited
When we make a finding that a
petition presents substantial
information indicating that listing a
species may be warranted, we are
required to promptly review the status
of the species (status review). For the
status review to be complete and based
on the best available scientific and
commercial information, we request
information on the Mohave ground
squirrel from government agencies,
Native American Tribes, the scientific
community, industry, and any other
interested parties. We seek information
on:
(1) The species’ biology, range, and
population trends, including:
(a) Habitat requirements for feeding,
breeding, and sheltering;
(b) Genetics and taxonomy;
(c) Historical and current range,
including distribution patterns;
(d) Historical and current population
levels, and current and projected trends;
and
(e) Past and ongoing conservation
measures for the species, its habitat, or
both.
E:\FR\FM\27APP1.SGM
27APP1
Agencies
[Federal Register Volume 75, Number 80 (Tuesday, April 27, 2010)]
[Proposed Rules]
[Pages 22047-22063]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 2010-9753]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR PARTS 52 AND 81
[EPA-R05-OAR-2009-0730; FRL-9142-2]
Approval and Promulgation of Implementation Plans and Designation
of Areas for Air Quality Planning Purposes; Wisconsin; Redesignation of
the Manitowoc County and Door County Areas to Attainment for Ozone
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to approve Wisconsin's requests to
redesignate the Manitowoc County and Door County, Wisconsin
nonattainment areas, to attainment for the 1997 8-hour ozone standard,
because the requests meet the statutory requirements for redesignation
under the Clean Air Act (CAA). The Wisconsin Department of Natural
Resources (WDNR) submitted these requests on September 11, 2009.
[[Page 22048]]
These proposed approvals involve several related actions. EPA is
proposing to determine that the Manitowoc County and Door County areas
have attained the 8-hour ozone National Ambient Air Quality Standard
(NAAQS). These determinations are based on three years of complete,
quality-assured and certified ambient air quality monitoring data for
the 2006-2008 ozone seasons that demonstrate that the 8-hour ozone
NAAQS has been attained in the areas. Complete, quality-assured air
quality data for the 2009 ozone season have been recorded in the EPA's
Air Quality System (AQS) and show that the areas continue to attain the
8-hour ozone standard. EPA is also proposing to approve, as revisions
to the Wisconsin State Implementation Plan (SIP), the State's plans for
maintaining the 8-hour ozone NAAQS through 2020 in the areas.
EPA is proposing to approve the 2005 base year emissions
inventories for the Manitowoc County and Door County areas as meeting
the base year emissions inventory requirement of the CAA. WDNR
submitted these base year emissions inventories on June 12, 2007.
Finally, EPA finds adequate and is proposing to approve the State's
2012 and 2020 Motor Vehicle Emission Budgets (MVEBs) for the Manitowoc
County and Door County areas.
DATES: Comments must be received on or before May 27, 2010.
ADDRESSES: Submit your comments, identified by Docket ID No. EPA-R05-
OAR-2009-0730, by one of the following methods:
1. https://www.regulations.gov: Follow the on-line instructions for
submitting comments.
2. E-mail: bortzer.jay@epa.gov.
3. Fax: (312) 692-2054.
4. Mail: Jay Bortzer, Chief, Air Programs Branch (AR-18J), U.S.
Environmental Protection Agency, 77 West Jackson Boulevard, Chicago,
Illinois 60604.
5. Hand delivery: Jay Bortzer, Chief, Air Programs Branch (AR-18J),
U.S. Environmental Protection Agency, 77 West Jackson Boulevard, 18th
Floor, Chicago, Illinois 60604. Such deliveries are only accepted
during the Regional Office normal hours of operation, and special
arrangements should be made for deliveries of boxed information. The
Regional Office official hours of business are Monday through Friday,
8:30 a.m. to 4:30 p.m., excluding Federal holidays.
Instructions: Direct your comments to Docket ID No. EPA-R05-OAR-
2009-0730. EPA's policy is that all comments received will be included
in the public docket without change and may be made available online at
https://www.regulations.gov, including any personal information
provided, unless the comment includes information claimed to be
Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute. Do not submit information that you
consider to be CBI or otherwise protected through https://www.regulations.gov or e-mail. The https://www.regulations.gov Web site
is an ``anonymous access'' system, 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 https://www.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 instructions on submitting
comments, go to section I of this document, ``What Should I Consider as
I Prepare My Comments for EPA?''
Docket: All documents in the docket are listed in the https://www.regulations.gov index. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, will be publicly available only in hard copy.
Publicly available docket materials are available either electronically
in https://www.regulations.gov or in hard copy at the Environmental
Protection Agency, Region 5, Air and Radiation Division, 77 West
Jackson Boulevard, Chicago, Illinois 60604. This facility is open from
8:30 a.m. to 4:30 p.m., Monday through Friday, excluding Federal
holidays. We recommend that you telephone Kathleen D'Agostino,
Environmental Engineer, at (312) 886-1767 before visiting the Region 5
office.
FOR FURTHER INFORMATION CONTACT: Kathleen D'Agostino, Environmental
Engineer, Criteria Pollutant Section, Air Programs Branch (AR-18J),
U.S. Environmental Protection Agency, Region 5, 77 West Jackson
Boulevard, Chicago, Illinois 60604, (312) 886-1767,
dagostino.kathleen@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document whenever ``we,''
``us,'' or ``our'' is used, we mean EPA. This supplementary information
section is arranged as follows:
Table of Contents
I. What should I consider as I prepare my comments for EPA?
II. What actions is EPA proposing to take?
III. What is the background for these actions?
A. What is the general background information?
B. What are the impacts of the December 22, 2006, and June 8,
2007, United States Court of Appeals decisions regarding EPA's Phase
1 implementation rule?
IV. What are the criteria for redesignation?
V. What is the effect of these actions?
VI. What is EPA's analysis of the requests?
A. Attainment Determinations and Redesignations
B. Adequacy of Wisconsin's MVEBs
C. 2005 Base Year Emissions Inventories
VII. What actions is EPA taking?
VIII. Statutory and Executive Order Reviews
I. What should I consider as I prepare my comments for EPA?
When submitting comments, remember to:
1. Identify the rulemaking by docket number and other identifying
information (subject heading, Federal Register date and page number).
2. Follow directions--EPA may ask you to respond to specific
questions or organize comments by referencing a Code of Federal
Regulations (CFR) part or section number.
3. Explain why you agree or disagree; suggest alternatives and
substitute language for your requested changes.
4. Describe any assumptions and provide any technical information
and/or data that you used.
5. If you estimate potential costs or burdens, explain how you
arrived at your estimate in sufficient detail to allow for it to be
reproduced.
6. Provide specific examples to illustrate your concerns, and
suggest alternatives.
7. Explain your views as clearly as possible, avoiding the use of
profanity or personal threats.
8. Make sure to submit your comments by the comment period deadline
identified.
II. What actions is EPA proposing to take?
EPA is proposing to take several related actions. EPA is proposing
to determine that the Manitowoc County and Door County nonattainment
areas have attained the 1997 8-hour ozone
[[Page 22049]]
standard and that the areas have met the requirements for redesignation
under section 107(d)(3)(E) of the CAA. EPA is thus proposing to approve
the requests from WDNR to change the legal designation of the Manitowoc
County and Door County areas from nonattainment to attainment for the
8-hour ozone NAAQS. EPA is also proposing to approve, as revisions to
the Wisconsin SIP, the State's maintenance plans (such approval being
one of the CAA criteria for redesignation to attainment status). The
maintenance plans are designed to keep the Manitowoc County and Door
County areas in attainment of the ozone NAAQS through 2020. EPA is
proposing to approve the 2005 base year emissions inventories for the
Manitowoc County and Door County areas as meeting the requirements of
section 172(c)(3) of the CAA. If EPA's determination of attainment is
finalized, under the provisions of 40 CFR 51.918, the requirement to
submit certain planning SIPs related to attainment (the Reasonably
Available Control Measure (RACM) requirement of section 172(c)(1) of
the CAA, the Reasonable Further Progress (RFP) and attainment
demonstration requirements of sections 172(c)(2) and (6) of the CAA,
and the requirement for contingency measures of section 172(c)(9) of
the CAA) are not applicable to the area as long as it continues to
attain the NAAQS and would cease to be applicable upon redesignation.
In addition, as set forth in more detail below, in the context of
redesignations, EPA has interpreted requirements related to attainment
as not applicable for purposes of redesignation. Finally, EPA finds
adequate and is proposing to approve the newly-established 2012 and
2020 MVEBs for the Manitowoc County and Door County areas. The adequacy
comment period for the MVEBs began on February 24, 2010, with EPA's
posting of the availability of the submittal on EPA's Adequacy Web site
(at https://www.epa.gov/otaq/stateresources/transconf/adequacy.htm). The
adequacy comment period for these MVEBs ended on March 26, 2010. EPA
did not receive any requests for this submittal, or adverse comments on
this submittal during the adequacy comment period. In a letter dated
April 7, 2010, EPA informed WDNR that we had found the 2012 and 2020
MVEBs to be adequate for use in transportation conformity analyses.
Please see section VI.B. of this rulemaking, ``Adequacy of Wisconsin's
MVEBs,'' for further explanation of this process. Therefore, we find
adequate, and are proposing to approve, the State's 2012 and 2020 MVEBs
for transportation conformity purposes.
III. What is the background for these actions?
A. What is the general background information?
Ground-level ozone is not emitted directly by sources. Rather,
emissions of nitrogen oxides (NOX) and volatile organic
compounds (VOCs) react in the presence of sunlight to form ground-level
ozone. NOX and VOCs are referred to as precursors of ozone.
The CAA establishes a process for air quality management through
the NAAQS. Before promulgation of the 8-hour standard, the ozone NAAQS
was based on a 1-hour standard. On November 6, 1991 (56 FR 56693 and
56852), the Manitowoc County and Door County areas were designated as
moderate and rural transport nonattainment areas, respectively, under
the 1-hour ozone NAAQS. The Manitowoc County and Door County areas were
subsequently redesignated to attainment of the 1-hour standard on April
17, 2003 (68 FR 18883). At the time EPA revoked the 1-hour ozone NAAQS,
on June 15, 2005, the Manitowoc County and Door County areas were
designated as attainment under the 1-hour ozone NAAQS.
On July 18, 1997 (62 FR 38856), EPA promulgated an 8-hour ozone
standard of 0.08 parts per million parts (ppm). On April 30, 2004 (69
FR 23857), EPA published a final rule designating and classifying areas
under the 8-hour ozone NAAQS. These designations and classifications
became effective June 15, 2004. EPA designated as nonattainment any
area that was violating the 8-hour ozone NAAQS based on the three most
recent years of air quality data, 2001-2003.
The CAA contains two sets of provisions, subpart 1 and subpart 2,
that address planning and control requirements for nonattainment areas.
(Both are found in Title I, part D, of the CAA; 42 U.S.C. 7501-7509a
and 7511-7511f, respectively.) Subpart 1 contains general requirements
for nonattainment areas for any pollutant, including ozone, governed by
a NAAQS. Subpart 2 provides additional and more specific requirements
for ozone nonattainment areas.
Under EPA's implementation rule for the 1997 8-hour ozone standard,
(69 FR 23951 (April 30, 2004)), an area was classified under subpart 2
based on its 8-hour ozone design value (i.e. the three-year average
annual fourth-highest daily maximum 8-hour average ozone
concentration), if it had a 1-hour design value at the time of
designation at or above 0.121 ppm (the lowest 1-hour design value in
Table 1 of subpart 2) (69 FR 23954). All other areas were covered under
subpart 1, based upon their 8-hour design values (69 FR 23958). The
Manitowoc County and Door County areas were designated as a subpart 1,
8-hour ozone nonattainment area by EPA on April 30, 2004 (69 FR 23857,
23947), based on air quality monitoring data from 2001-2003 (69 FR
23860).
40 CFR 50.10 and 40 CFR part 50, Appendix I, provide that the 8-
hour ozone standard is attained when the three-year average of the
annual fourth-highest daily maximum 8-hour average ozone concentration
is less than or equal to 0.08 ppm, when rounded. The data completeness
requirement is met when the average percent of days with valid ambient
monitoring data is greater than 90%, and no single year has less than
75% data completeness. See 40 CFR part 50, Appendix I, 2.3(d).
The WDNR submitted requests to redesignate the Manitowoc County and
Door County areas to attainment for the 8-hour ozone standard on
September 11, 2009. The redesignation requests included three years of
complete, quality-assured data for the period of 2006 through 2008,
indicating the 8-hour NAAQS for ozone, as promulgated in 1997, had been
attained for the Manitowoc County and Door County areas. Complete,
quality-assured monitoring data in AQS but not yet certified for the
2009 ozone season show that the areas continue to attain the 8-hour
ozone standard. Under the CAA, nonattainment areas may be redesignated
to attainment if sufficient complete, quality-assured data are
available for the Administrator to determine that the area has attained
the standard, and the area meets the other CAA redesignation
requirements in section 107(d)(3)(E).
On March 27, 2008 (73 FR 16436), EPA promulgated a revised 8-hour
ozone standard of 0.075 ppm. In May 2008, States, environmental groups
and industry groups filed petitions with the DC Circuit Court of
Appeals for review of the 2008 ozone standards. In March 2009, the
court granted EPA's request to stay the litigation so EPA could review
the standards and determine whether they should be reconsidered. On
September 16, 2009, we announced that we are reconsidering our 2008
decision setting national standards for ground-level ozone. The
designation process for that standard has been stayed. On January 19,
2010, EPA proposed to set the level of the primary 8-hour ozone
standard within the range of 0.060 to
[[Page 22050]]
0.070 ppm, rather than at 0.075 ppm (75 FR 2938). We expect by August
2010 to have completed our reconsideration of the standard and also
expect that thereafter we will proceed with designations. The actions
addressed in today's proposed rulemaking relate only to the 1997 8-hour
ozone standard.
B. What are the impacts of the December 22, 2006, and June 8, 2007,
United States Court of Appeals decisions regarding EPA's Phase 1
implementation rule?
1. Summary of Court Decision
On December 22, 2006, in South Coast Air Quality Management Dist.
v. EPA (South Coast), the U.S. Court of Appeals for the District of
Columbia Circuit vacated EPA's Phase 1 Implementation Rule for the 8-
hour Ozone Standard (69 FR 23951, April 30, 2004). 472 F.3d 882 (DC
Cir. 2006). On June 8, 2007, in response to several petitions for
rehearing, the DC Circuit Court clarified that the Phase 1 Rule was
vacated only with regard to those parts of the rule that had been
successfully challenged. Id., Docket No. 04 1201. Therefore, several
provisions of the Phase 1 Rule remain effective: provisions related to
classifications for areas currently classified under subpart 2 of Title
I, part D, of the CAA as 8-hour nonattainment areas; the 8-hour
attainment dates; and the timing for emissions reductions needed for
attainment of the 8-hour ozone NAAQS. The June 8, 2007, decision also
left intact the court's rejection of EPA's reasons for implementing the
8-hour standard in certain nonattainment areas under subpart 1 in lieu
of subpart 2. By limiting the vacatur, the court let stand EPA's
revocation of the 1-hour standard and those anti-backsliding provisions
of the Phase 1 Rule that had not been successfully challenged. The June
8, 2007, decision reaffirmed the December 22, 2006, decision that EPA
had improperly failed to retain four measures required for 1-hour
nonattainment areas under the anti-backsliding provisions of the
regulations: (1) Nonattainment area New Source Review (NSR)
requirements based on an area's 1-hour nonattainment classification;
(2) section 185 penalty fees for 1-hour severe or extreme nonattainment
areas; (3) measures to be implemented pursuant to section 172(c)(9) or
182(c)(9) of the CAA, on the contingency of an area not making
reasonable further progress toward attainment of the 1-hour NAAQS, or
for failure to attain that NAAQS; and (4) certain transportation
conformity requirements for certain types of Federal actions. The June
8, 2007, decision clarified that the court's reference to conformity
requirements was limited to requiring the continued use of 1-hour motor
vehicle emissions budgets until 8-hour budgets were available for 8-
hour conformity determinations.
This section sets forth EPA's views on the potential effect of the
court's rulings on these proposed redesignation actions. For the
reasons set forth below, EPA does not believe that the court's rulings
alter any requirements relevant to these redesignation actions so as to
preclude redesignation or prevent EPA from proposing or ultimately
finalizing these redesignations. EPA believes that the court's December
22, 2006, and June 8, 2007, decisions impose no impediment to moving
forward with redesignation of these areas to attainment, because even
in light of the court's decisions, redesignation is appropriate under
the relevant redesignation provisions of the CAA and longstanding
policies regarding redesignation requests.
2. Requirements Under the 8-Hour Standard
With respect to the 8-hour standard, the court's ruling rejected
EPA's reasons for classifying areas under subpart 1 for the 8-hour
standard, and remanded that matter to the Agency. In its January 16,
2009, proposed rulemaking in response to the South Coast decision, EPA
has proposed to classify Door County and Manitowoc County under subpart
2 as moderate and marginal areas, respectively (74 FR 2936, 2944). If
EPA finalizes this rulemaking, the requirements under subpart 2 will
become applicable when they are due, a deadline that EPA has proposed
to be one year after the effective date of a final rulemaking
classifying areas as moderate or marginal (74 FR 2940-2941). Although a
future final decision by EPA to classify these areas under subpart 2
would trigger additional future requirements for the areas, EPA
believes that this does not mean that redesignations cannot now go
forward. This belief is based upon: (1) EPA's longstanding policy of
evaluating requirements in accordance with the requirements due at the
time the request is submitted; and, (2) consideration of the inequity
of applying retroactively any requirements that might be applied in the
future.
First, at the time the redesignation requests were submitted, the
Manitowoc County and Door County areas were not classified under
subpart 2, nor were there any subpart 2 requirements yet due for these
areas. Under EPA's longstanding interpretation of section 107(d)(3)(E)
of the CAA, to qualify for redesignation, States requesting
redesignation to attainment must meet only the relevant SIP
requirements that came due prior to the submittal of a complete
redesignation request. See September 4, 1992, Calcagni memorandum
(``Procedures for Processing Requests to Redesignate Areas to
Attainment,'' Memorandum from John Calcagni, Director, Air Quality
Management Division). See also Michael Shapiro Memorandum, September
17, 1993, and 60 FR 12459, 12465-12466 (March 7, 1995) (Redesignation
of Detroit-Ann Arbor). See Sierra Club v. EPA, 375 F.3d 537 (7th Cir.
2004), which upheld EPA's redesignation rulemaking applying this
interpretation. See, e.g. also 68 FR 25418, 25424, 25427 (May 12, 2003)
(Redesignation of St. Louis).
Moreover, it would be inequitable to retroactively apply any new
SIP requirements that were not applicable at the time the request was
submitted. The DC Circuit has recognized the inequity in such
retroactive rulemaking. In Sierra Club v. Whitman, 285 F.3d 63 (DC Cir.
2002), the DC Circuit upheld a district court's ruling refusing to make
retroactive an EPA determination of nonattainment that was past the
statutory due date. Such a determination would have resulted in the
imposition of additional requirements on the area. The court stated:
``Although EPA failed to make the nonattainment determination within
the statutory time frame, Sierra Club's proposed solution only makes
the situation worse. Retroactive relief would likely impose large costs
on the States, which would face fines and suits for not implementing
air pollution prevention plans in 1997, even though they were not on
notice at the time.'' Id. at 68. Similarly here it would be unfair to
penalize the areas by applying to them, for purposes of redesignation,
additional SIP requirements under subpart 2 that were not in effect or
yet due at the time WDNR submitted its redesignation requests.
3. Requirements Under the 1-Hour Standard
With respect to the 1-hour standard requirements, the Manitowoc
County and Door County areas were attainment areas subject to CAA
section 175A maintenance plans under the 1-hour standard at the time
that the 1-hour standard was revoked. Therefore, the DC Circuit's
decisions with respect to 1-hour nonattainment anti-backsliding
requirements do not impact redesignation requests for these types of
areas, except to the extent that the court
[[Page 22051]]
in its June 8, 2007, decision clarified that for those areas with 1-
hour motor vehicle emissions budgets in their maintenance plans, anti-
backsliding requires that those 1-hour budgets must be used for 8-hour
conformity determinations until replaced by 8-hour budgets. To meet
this requirement, conformity determinations in such areas must comply
with the applicable requirements of EPA's conformity regulations at 40
CFR part 93.
With respect to the three other anti-backsliding provisions for the
1-hour standard that the court found were not properly retained, the
Manitowoc County and Door County areas are attainment areas subject to
maintenance plans for the 1-hour standard, and the NSR, contingency
measures (pursuant to section 172(c)(9) or 182(c)(9)), and fee
provision requirements no longer apply to areas that have been
redesignated to attainment of the 1-hour standard.
Thus, the South Coast decision in South Coast Air Quality
Management Dist. does not preclude EPA from finalizing the
redesignation of these areas.
IV. What are the criteria for redesignation?
The CAA provides the requirements for redesignating a nonattainment
area to attainment. Specifically, section 107(d)(3)(E) allows for
redesignation provided that: (1) The Administrator determines that the
area has attained the applicable NAAQS; (2) the Administrator has fully
approved the applicable implementation plan for the area under section
110(k); (3) the Administrator determines that the improvement in air
quality is due to permanent and enforceable reductions in emissions
resulting from implementation of the applicable SIP and applicable
Federal air pollutant control regulations and other permanent and
enforceable reductions; (4) the Administrator has fully approved a
maintenance plan for the area as meeting the requirements of section
175A; and, (5) the State containing such area has met all requirements
applicable to the area under section 110 and part D.
EPA provided guidance on redesignation in the General Preamble for
the Implementation of Title I of the CAA Amendments of 1990 on April
16, 1992 (57 FR 13498), and supplemented this guidance on April 28,
1992 (57 FR 18070). EPA has provided further guidance on processing
redesignation requests in the following documents:
``Ozone and Carbon Monoxide Design Value Calculations,'' Memorandum
from William G. Laxton, Director Technical Support Division, June 18,
1990;
``Maintenance Plans for Redesignation of Ozone and Carbon Monoxide
Nonattainment Areas,'' Memorandum from G. T. Helms, Chief, Ozone/Carbon
Monoxide Programs Branch, April 30, 1992;
``Contingency Measures for Ozone and Carbon Monoxide (CO)
Redesignations,'' Memorandum from G. T. Helms, Chief, Ozone/Carbon
Monoxide Programs Branch, June 1, 1992;
``Procedures for Processing Requests to Redesignate Areas to
Attainment,'' Memorandum from John Calcagni, Director, Air Quality
Management Division, September 4, 1992;
``State Implementation Plan (SIP) Actions Submitted in Response to
Clean Air Act (ACT) Deadlines,'' Memorandum from John Calcagni,
Director, Air Quality Management Division, October 28, 1992;
``Technical Support Documents (TSDs) for Redesignation Ozone and
Carbon Monoxide (CO) Nonattainment Areas,'' Memorandum from G. T.
Helms, Chief, Ozone/Carbon Monoxide Programs Branch, August 17, 1993;
``State Implementation Plan (SIP) Requirements for Areas Submitting
Requests for Redesignation to Attainment of the Ozone and Carbon
Monoxide (CO) National Ambient Air Quality Standards (NAAQS) On or
After November 15, 1992,'' Memorandum from Michael H. Shapiro, Acting
Assistant Administrator for Air and Radiation, September 17, 1993;
``Use of Actual Emissions in Maintenance Demonstrations for Ozone
and CO Nonattainment Areas,'' Memorandum from D. Kent Berry, Acting
Director, Air Quality Management Division, to Air Division Directors,
Regions 1-10, November 30, 1993.
``Part D New Source Review (part D NSR) Requirements for Areas
Requesting Redesignation to Attainment,'' Memorandum from Mary D.
Nichols, Assistant Administrator for Air and Radiation, October 14,
1994; and
``Reasonable Further Progress, Attainment Demonstration, and
Related Requirements for Ozone Nonattainment Areas Meeting the Ozone
National Ambient Air Quality Standard,'' Memorandum from John S. Seitz,
Director, Office of Air Quality Planning and Standards, May 10, 1995.
V. What is the effect of these actions?
Approval of the redesignation requests would change the official
designations of the Manitowoc County and Door County areas for the 1997
8-hour ozone NAAQS found at 40 CFR part 81. It would also incorporate
into the Wisconsin SIP plans for maintaining the 8-hour ozone NAAQS
through 2020. The maintenance plans include contingency measures as
required under CAA section 175A to remedy future violations of the 8-
hour NAAQS. They also establish MVEBs for the Manitowoc County area of
1.76 and 1.25 tons per day (tpd) for VOC and 3.76 and 1.86 tpd for
NOX for the years 2012 and 2020, respectively, and MVEBs for
the Door County area of 0.78 and 0.53 tpd for VOC and 1.55 and 0.74 tpd
for NOX for the years 2012 and 2020, respectively.
VI. What is EPA's analysis of the request?
A. Attainment Determinations and Redesignations
EPA is proposing to determine that the Manitowoc County and Door
County areas have attained the 1997 8-hour ozone standard and that the
areas have met all other applicable redesignation criteria under CAA
section 107(d)(3)(E). The basis for EPA's proposed approvals of the
redesignation requests is as follows:
1. The Areas Have Attained the 8-Hour Ozone NAAQS (Section
107(d)(3)(E)(i))
EPA is proposing to make determinations that the Manitowoc County
and Door County areas have attained the 1997 8-hour ozone NAAQS. An
area may be considered to be attaining the 8-hour ozone NAAQS if there
are no violations, as determined in accordance with 40 CFR 50.10 and
part 50, Appendix I, based on three complete, consecutive calendar
years of quality-assured air quality monitoring data. To attain this
standard, the three-year average of the fourth-highest daily maximum 8-
hour average ozone concentrations measured at each monitor within an
area over each year must not exceed 0.08 ppm. Based on the rounding
convention described in 40 CFR part 50, Appendix I, the standard is
attained if the design value is 0.084 ppm or below. The data must be
collected and quality-assured in accordance with 40 CFR part 58, and
recorded in AQS. The monitors generally should have remained at the
same location for the duration of the monitoring period required for
demonstrating attainment.
Wisconsin included in its redesignation requests ozone monitoring
data for the 2006 to 2008 ozone seasons and has subsequently provided
monitoring data for 2009. Monitoring data for 2006 through 2008 have
been certified by the State; 2009 data have
[[Page 22052]]
not yet been certified. However, Wisconsin has quality-assured all of
the ambient monitoring data in accordance with 40 CFR 58.10, and has
recorded it in the AQS database. The data meet the completeness
criteria in 40 CFR 50, Appendix I, which require a minimum completeness
of 75 percent annually and 90 percent over each three-year period.
Monitoring data are presented in Table 1 below.
Table 1--Annual 4th High Daily Maximum 8-Hour Ozone Concentration and Three Year Averages of 4th High Daily
Maximum 8-Hour Ozone Concentrations
----------------------------------------------------------------------------------------------------------------
2006-2008 2007-2009
Monitor 2006 4th 2007 4th 2008 4th 2009 4th average average
high (ppm) high (ppm) high (ppm) high (ppm) (ppm) (ppm)
----------------------------------------------------------------------------------------------------------------
Door 55-029-0004.................. 0.079 0.092 0.069 0.075 0.080 0.078
Manitowoc 55-071-0007............. 0.078 0.085 0.064 0.078 0.075 0.075
----------------------------------------------------------------------------------------------------------------
In addition, as discussed below with respect to the maintenance
plans, WDNR has committed to continue to operate an EPA-approved
monitoring network in the areas. WDNR will continue to quality assure
monitoring data in accordance with 40 CFR part 58 and enter all data
into AQS in accordance with Federal guidelines. In summary, EPA
believes that the data show that the Manitowoc County and Door County
areas have attained the 8-hour ozone NAAQS.
2. The Areas Have Met All Applicable Requirements Under Section 110 and
Part D; and the Areas Have Fully Approved SIPs Under Section 110(k)
(Sections 107(d)(3)(E)(v) and 107(d)(3)(E)(ii))
We have determined that Wisconsin has met all currently applicable
SIP requirements for purposes of redesignation for the Manitowoc County
and Door County areas under section 110 of the CAA (general SIP
requirements). We are also proposing to determine that the Wisconsin
SIP meets all SIP requirements for these areas currently applicable for
purposes of redesignation under part D of Title I of the CAA
(requirements specific to subpart 1 nonattainment areas), in accordance
with section 107(d)(3)(E)(v). In addition, with the exception of the
base year emissions inventories, we have approved all applicable
requirements of the Wisconsin SIP for purposes of redesignation, in
accordance with section 107(d)(3)(E)(ii). As discussed below, in this
action EPA is proposing to approve Wisconsin's 2005 base year emissions
inventories as meeting the section 172(c)(3) emissions inventory
requirement for the areas.
In proposing these determinations, we have ascertained which SIP
requirements are applicable to the areas for purposes of redesignation,
and have determined that there are SIP measures meeting those
requirements and that they are, or upon final approval of the emissions
inventories, will be fully approved under section 110(k) of the CAA. As
discussed more fully below, for purposes of evaluating a redesignation
request, SIPs must be fully approved only with respect to requirements
that became due prior to the submission of the redesignation request.
The September 4, 1992, Calcagni memorandum (see ``Procedures for
Processing Requests to Redesignate Areas to Attainment,'' Memorandum
from John Calcagni, Director, Air Quality Management Division,
September 4, 1992) describes EPA's interpretation of section
107(d)(3)(E) of the CAA. Under this interpretation, a State and the
area it wishes to redesignate must meet the relevant CAA requirements
that are due prior to the State's submittal of a complete redesignation
request for the area. See also the September 17, 1993, Michael Shapiro
memorandum and 60 FR 12459, 12465-12466 (March 7, 1995) (Redesignation
of Detroit-Ann Arbor, Michigan to attainment of the 1-hour ozone
NAAQS). Applicable requirements of the CAA that come due subsequent to
the State's submittal of a complete request remain applicable until a
redesignation to attainment is approved, but are not required as a
prerequisite to redesignation. See section 175A(c) of the CAA. Sierra
Club v. EPA, 375 F.3d 537 (7th Cir. 2004). See also 68 FR 25424, 25427
(May 12, 2003) (Redesignation of the St. Louis/East St. Louis area to
attainment of the 1-hour ozone NAAQS).
Since EPA is proposing here to determine that the areas have
attained the 1997 8-hour ozone standard, under 40 CFR 51.918, if these
determinations are finalized, the requirements to submit certain
planning SIPs related to attainment, including attainment demonstration
requirements (the RACM requirement of section 172(c)(1) of the CAA, the
RFP and attainment demonstration requirements of sections 172(c)(2) and
(c)(6) of the CAA, and the requirement for contingency measures of
section 172(c)(9) of the CAA), would not be applicable to the areas as
long as they continue to attain the NAAQS and would cease to apply upon
redesignation. In addition, in the context of redesignations, EPA has
interpreted requirements related to attainment as not applicable for
purposes of redesignation. For example, in the General Preamble EPA
stated that:
[t]he section 172(c)(9) requirements are directed at ensuring
RFP and attainment by the applicable date. These requirements no
longer apply when an area has attained the standard and is eligible
for redesignation. Furthermore, section 175A for maintenance plans *
* * provides specific requirements for contingency measures that
effectively supersede the requirements of section 172(c)(9) for
these areas. ``General Preamble for the Interpretation of Title I of
the Clean Air Act Amendments of 1990,'' (General Preamble) 57 FR
13498, 13564 (April 16, 1992).
See also Calcagni memorandum at 6 (``The requirements for reasonable
further progress and other measures needed for attainment will not
apply for redesignations because they only have meaning for areas not
attaining the standard.'').
a. The Manitowoc County and Door County Areas Have Met All Applicable
Requirements for Purposes of Redesignation Under Section 110 and Part D
of the CAA
i. Section 110 General SIP requirements
Section 110(a) of Title I of the CAA contains the general
requirements for a SIP. Section 110(a)(2) provides that the
implementation plan submitted by a State must have been adopted by the
State after reasonable public notice and hearing, and, among other
things, must: Include enforceable emission limitations and other
control measures, means or techniques necessary to meet the
requirements of the CAA; provide for establishment and operation of
appropriate devices, methods, systems and procedures necessary to
monitor ambient air quality; provide for implementation of a source
permit
[[Page 22053]]
program to regulate the modification and construction of any stationary
source within the areas covered by the plan; include provisions for the
implementation of part C, Prevention of Significant Deterioration (PSD)
and part D, NSR permit programs; include criteria for stationary source
emission control measures, monitoring, and reporting; include
provisions for air quality modeling; and provide for public and local
agency participation in planning and emission control rule development.
Section 110(a)(2)(D) of the CAA requires that SIPs contain measures
to prevent sources in a State from significantly contributing to air
quality problems in another State. To implement this provision, EPA has
required certain States to establish programs to address transport of
air pollutants (NOX SIP Call \1\ and Clean Air Interstate
Rule (CAIR) (70 FR 25162, May 12, 2005)). However, the section
110(a)(2)(D) requirements for a State are not linked with a particular
nonattainment area's designation and classification. EPA believes that
the requirements linked with a particular nonattainment area's
designation and classification are the relevant measures to evaluate in
reviewing a redesignation request. The transport SIP submittal
requirements, where applicable, continue to apply to a State regardless
of the designation of any one particular area in the State. Thus, we
believe that these requirements should not be construed to be
applicable requirements for purposes of redesignation.
---------------------------------------------------------------------------
\1\ On October 27, 1998 (63 FR 57356), EPA issued a
NOX SIP Call requiring the District of Columbia and 22
States to reduce emissions of NOX in order to reduce the
transport of ozone and ozone precursors. Wisconsin was not included
in EPA's NOX SIP Call.
---------------------------------------------------------------------------
Further, we believe that the other section 110 elements described
above that are not connected with nonattainment plan submissions and
not linked with an area's attainment status are also not applicable
requirements for purposes of redesignation. A State remains subject to
these requirements after an area is redesignated to attainment. We
conclude that only the section 110 and part D requirements that are
linked with a particular area's designation and classification are the
relevant measures that we may consider in evaluating a redesignation
request. This approach is consistent with EPA's existing policy on
applicability of conformity and oxygenated fuels requirements for
redesignation purposes, as well as with section 184 ozone transport
requirements. See Reading, Pennsylvania, proposed and final rulemakings
(61 FR 53174-53176, October 10, 1996), (62 FR 24826, May 7, 1997);
Cleveland-Akron-Lorain, Ohio, final rulemaking (61 FR 20458, May 7,
1996); and Tampa, Florida, final rulemaking (60 FR 62748, December 7,
1995). See also the discussion on this issue in the Cincinnati, Ohio 1-
hour ozone redesignation (65 FR 37890, June 19, 2000), and in the
Pittsburgh, Pennsylvania 1-hour ozone redesignation (66 FR 50399,
October 19, 2001).
We have reviewed Wisconsin's SIP and have concluded that it meets
the general SIP requirements under section 110 of the CAA to the extent
they are applicable for purposes of redesignation. EPA has previously
approved provisions of the Wisconsin SIP addressing section 110
elements under the 1-hour ozone standard (40 CFR 52.2570). Further, in
a submittal dated December 12, 2007, Wisconsin confirmed that the State
continues to meet the section 110 requirements for the 8-hour ozone
standard. EPA has not yet taken rulemaking action on this submittal;
however, such approval is not necessary for redesignation.
ii. Part D Requirements
EPA has determined that, if EPA finalizes the approval of the base
year emissions inventories discussed in section VI.C. of this
rulemaking, the Wisconsin SIP will meet the applicable SIP requirements
for the Manitowoc County and Door County areas applicable for purposes
of redesignation under part D of the CAA. Subpart 1 of part D, found in
sections 172-176 of the CAA, sets forth the basic nonattainment
requirements applicable to all nonattainment areas. Subpart 2 of part
D, which includes section 182 of the CAA, establishes additional
specific requirements depending on the area's nonattainment
classification.
Since the Manitowoc County and Door County areas were not
classified under subpart 2, of Part D at the time the redesignation
requests were submitted, the subpart 2 requirements do not apply for
purposes of evaluating the State's redesignation requests. The
applicable subpart 1 requirements are contained in sections 172(c)(1)-
(9) and in section 176.
Subpart 1 Section 172 Requirements
For purposes of evaluating these redesignation requests, the
applicable section 172 SIP requirements for the Manitowoc County and
Door County areas are contained in sections 172(c)(1)-(9). A thorough
discussion of the requirements contained in section 172 can be found in
the General Preamble for Implementation of Title I (57 FR 13498, April
16, 1992).
Section 172(c)(1) requires the plans for all nonattainment areas to
provide for the implementation of all RACM as expeditiously as
practicable and to provide for attainment of the primary NAAQS. EPA
interprets this requirement to impose a duty on all nonattainment areas
to consider all available control measures and to adopt and implement
such measures as are reasonably available for implementation in each
area as components of the area's attainment demonstration. Because
attainment has been reached, no additional measures are needed to
provide for attainment, and section 172(c)(1) requirements are no
longer considered to be applicable as long as the area continues to
attain the standard until redesignation. (40 CFR 51.918).
The RFP requirement under section 172(c)(2) is defined as progress
that must be made toward attainment. This requirement is not relevant
for purposes of redesignation because the Manitowoc County and Door
County areas have monitored attainment of the ozone NAAQS. (General
Preamble, 57 FR 13564). See also 40 CFR 51.918. In addition, because
the Manitowoc County and Door County areas have attained the ozone
NAAQS and are no longer subject to an RFP requirement, the requirement
to submit the section 172(c)(9) contingency measures is not applicable
for purposes of redesignation. Id.
Section 172(c)(3) requires submission and approval of a
comprehensive, accurate and current inventory of actual emissions.
Wisconsin submitted 2005 base year emissions inventories on June 12,
2007. As discussed below in section VI.C., EPA is proposing to approve
the 2005 base year inventories as meeting the section 172(c)(3)
emissions inventory requirement for the Manitowoc County and Door
County areas.
Section 172(c)(4) requires the identification and quantification of
allowable emissions for major new and modified stationary sources in an
area, and section 172(c)(5) requires source permits for the
construction and operation of new and modified major stationary sources
anywhere in the nonattainment area. EPA approved Wisconsin's current
NSR program on December 17, 2008 (73 FR 76558 and 76560). Nonetheless,
EPA has determined that, since PSD requirements will apply after
redesignation, areas being redesignated need not comply with the
requirement that a nonattainment NSR program be
[[Page 22054]]
approved prior to redesignation, provided that the area demonstrates
maintenance of the NAAQS without part D NSR. A more detailed rationale
for this view is described in a memorandum from Mary Nichols, Assistant
Administrator for Air and Radiation, dated October 14, 1994, entitled,
``Part D New Source Review Requirements for Areas Requesting
Redesignation to Attainment.'' Wisconsin has demonstrated that the
Manitowoc County and Door County areas will be able to maintain the
standard without part D NSR in effect; therefore, the State need not
have a fully approved part D NSR program prior to approval of the
redesignation request. The State's PSD program will become effective in
the Manitowoc County and Door County areas upon redesignation to
attainment. See rulemakings for Detroit, Michigan (60 FR 12467-12468,
March 7, 1995); Cleveland-Akron-Lorain, Ohio (61 FR 20458, 20469-20470,
May 7, 1996); Louisville, Kentucky (66 FR 53665, October 23, 2001); and
Grand Rapids, Michigan (61 FR 31834-31837, June 21, 1996).
Section 172(c)(6) requires the SIP to contain control measures
necessary to provide for attainment of the standard. Because attainment
has been reached, no additional measures are needed to provide for
attainment.
Section 172(c)(7) requires the SIP to meet the applicable
provisions of section 110(a)(2). As noted above, we believe the
Wisconsin SIP meets the requirements of section 110(a)(2) applicable
for purposes of redesignation.
Subpart 1 Section 176 Conformity Requirements
Section 176(c) of the CAA requires States to establish criteria and
procedures to ensure that Federally-supported or funded activities,
including highway projects, conform to the air quality planning goals
in the applicable SIPs. The requirement to determine conformity applies
to transportation plans, programs and projects developed, funded or
approved under Title 23 of the U.S. Code and the Federal Transit Act
(transportation conformity) as well as to all other Federally-supported
or funded projects (general conformity). State conformity revisions
must be consistent with Federal conformity regulations relating to
consultation, enforcement, and enforceability, which EPA promulgated
pursuant to CAA requirements.
EPA believes that it is reasonable to interpret the conformity SIP
requirements as not applying for purposes of evaluating the
redesignation request under section 107(d) for two reasons. First, the
requirement to submit SIP revisions to comply with the conformity
provisions of the CAA continues to apply to areas after redesignation
to attainment since such areas would be subject to a section 175A
maintenance plan. Second, EPA's Federal conformity rules require the
performance of conformity analyses in the absence of Federally-approved
State rules. Therefore, because areas are subject to the conformity
requirements regardless of whether they are redesignated to attainment
and, because they must implement conformity under Federal rules if
State rules are not yet approved, EPA believes it is reasonable to view
these requirements as not applying for purposes of evaluating a
redesignation request. See Wall v. EPA, 265 F.3d 426 (6th Cir. 2001),
upholding this interpretation. See also 60 FR 62748, 62749-62750 (Dec.
7, 1995) (Tampa, Florida).
EPA approved Wisconsin's general and transportation conformity SIPs
on July 29, 1996 (61 FR 39329), and August 27, 1996 (61 FR 43970),
respectively. Section 176(c) of the CAA was amended by provisions
contained in the Safe, Accountable, Flexible, Efficient Transportation
Equity Act: A Legacy for Users (SAFETEALU), which was signed into law
on August 10, 2005 (Pub. L. 109-59). Among the changes Congress made to
this section of the CAA were streamlined requirements for State
conformity SIPs. Wisconsin is in the process of updating its
transportation conformity SIP to meet these new requirements. Wisconsin
has submitted onroad MVEBs for the Manitowoc County area of 1.76 and
1.25 tpd VOC and 3.76 and 1.86 tpd NOX for the years 2012
and 2020, respectively and MVEBs for the Door County area of 0.78 and
0.53 tpd VOC and 1.55 and 0.74 tpd NOX for the years 2012
and 2020, respectively. The areas must use the MVEBs from the
maintenance plans in any conformity determination that is effective on
or after the effective date of the adequacy finding and/or the
maintenance plans' approval.
b. The Manitowoc County and Door County Areas Have Fully Approved
Applicable SIPs under Section 110(k) of the CAA
If EPA issues a final approval of the base year emissions
inventories, EPA will have fully approved the Wisconsin SIP for the
Manitowoc County and Door County areas under section 110(k) of the CAA
for all requirements applicable for purposes of redesignation. EPA may
rely on prior SIP approvals in approving a redesignation request (See
page 3 of the September 4, 1992, John Calcagni memorandum; Southwestern
Pennsylvania Growth Alliance v. Browner, 144 F.3d 984, 989-990 (6th
Cir. 1998); Wall v. EPA, 265 F.3d 426 (6th Cir. 2001)) plus any
additional measures it may approve in conjunction with a redesignation
action. See 68 FR 25413, 25426 (May 12, 2003). Since the passage of the
CAA of 1970, Wisconsin has adopted and submitted, and EPA has fully
approved, provisions addressing various required SIP elements under the
1-hour ozone standard. In this action, EPA is proposing to approve
Wisconsin's 2005 base year emissions inventories for the Manitowoc
County and Door County areas as meeting the requirement of section
172(c)(3) of the CAA. No Manitowoc County or Door County area SIP
provisions are currently disapproved, conditionally approved, or
partially approved.
3. The Improvement in Air Quality Is Due to Permanent and Enforceable
Reductions in Emissions Resulting From Implementation of the SIP and
Applicable Federal Air Pollution Control Regulations and Other
Permanent and Enforceable Reductions (Section 107(d)(3)(E)(iii))
EPA finds that Wisconsin has demonstrated that the observed air
quality improvement in the Manitowoc County and Door County areas is
due to permanent and enforceable reductions in emissions resulting from
implementation of the SIPs, Federal measures, and other State-adopted
measures.
In making this demonstration, WDNR has calculated the change in
emissions between 2002 and 2007. Wisconsin developed an emissions
inventory for 2002, one of the years used to designate the areas as
nonattainment. The State developed an attainment inventory for 2007,
one of the years the Manitowoc County and Door County areas monitored
attainment. The reduction in emissions and the corresponding
improvement in air quality over this time period can be attributed to a
number of regulatory control measures that Manitowoc and Door Counties
and upwind areas have implemented in recent years.
a. Permanent and Enforceable Controls Implemented
The following is a discussion of permanent and enforceable measures
that have been implemented in the areas:
[[Page 22055]]
i. Federal Emission Control Measures
Reductions in VOC and NOX emissions have occurred
statewide and in upwind areas as a result of Federal emission control
measures, with additional emission reductions expected to occur in the
future. Federal emission control measures include the following.
Tier 2 Emission Standards for Vehicles and Gasoline Sulfur
Standards. These emission control requirements result in lower VOC and
NOX emissions from new cars and light duty trucks, including
sport utility vehicles. The Federal rules were phased in between 2004
and 2009. The EPA has estimated that, by the end of the phase-in
period, the following vehicle NOX emission reductions will
occur nationwide: Passenger cars (light duty vehicles) (77 percent);
light duty trucks, minivans, and sports utility vehicles (86 percent);
and, larger sports utility vehicles, vans, and heavier trucks (69 to 95
percent). VOC emission reductions are expected to range from 12 to 18
percent, depending on vehicle class, over the same period. Some of
these emission reductions occurred by the 2007-2009 period used to
demonstrate attainment, and additional emission reductions will occur
during the maintenance period.
Heavy-Duty Diesel Engine Rule. EPA issued this rule in July 2000.
This rule includes standards limiting the sulfur content of diesel
fuel, which went into effect in 2004. A second phase took effect in
2007 which further reduced the highway diesel fuel sulfur content to 15
ppm, leading to additional reductions in combustion NOX and
VOC emissions. This rule is expected to achieve a 95 percent reduction
in NOX emissions from diesel trucks and busses.
Non-Road Diesel Rule. EPA issued this rule in 2004. This rule
applies to diesel engines used in industries, such as construction,
agriculture, and mining. It is estimated that compliance with this rule
will cut NOX emissions from non-road diesel engines by up to
90 percent. This rule is currently achieving emission reductions, but
will not be fully implemented until 2010.
Maximum Achievable Control Technology (MACT) Rules. EPA has
promulgated numerous MACT standards, many of which limit VOC emissions.
Compliance began for many of the MACT rules from late 2005 through
2007.
ii. Control Measures in Upwind Areas
NOX Reasonably Available Control Technology (RACT). Wisconsin
adopted NOX RACT regulations for the upwind Milwaukee-Racine
area. The emission requirements apply to stationary combustion units at
major sources, with compliance required by May 1, 2009. The RACT rule
is estimated to achieve reductions of over 29,000 tpy of NOX
emissions from 2002 levels.
NOX SIP Call. On October 27, 1998 (63 FR 57356), EPA issued a
NOX SIP Call requiring the District of Columbia and 22
States to reduce emissions of NOX. Affected States were
required to comply with Phase I of the SIP Call beginning in 2004, and
Phase II beginning in 2007. The reduction in NOX emissions
has resulted in lower concentrations of transported ozone entering the
Manitowoc County and Door County areas. Emission reductions resulting
from regulations developed in response to the NOX SIP Call
are permanent and enforceable.
b. Emission Reductions
States are required to develop periodic emissions inventories every
three years. (40 CFR part 51, subpart A). Wisconsin is using the
periodic emissions inventory from 2002 as the nonattainment inventory.
Point source sector emissions inventories were developed using reported
point source emissions, EPA's Clean Air Markets database and approved
EPA techniques for emissions calculations. Emissions were estimated by
collecting process-level information from each facility that qualifies
for inclusion into WDNR's point source database. Process, boiler,
fugitive and tank emissions were typically calculated using throughput
information multiplied by an emission factor for the process. Emission
factor sources included mass balance, stack testing, continuous
emissions monitors, engineering judgment and EPA's Factor Information
Retrieval database.
Area source emissions were generated by backcasting from the 2005
periodic emissions inventory to minimize differences between the
nonattainment and attainment inventories due to changes in methodology.
The backcasting factors were based on 2002-2008 growth factors
including the Census Bureau's County Business Pattern employment data,
growth factors developed for the Lake Michigan Air Directors Consortium
(LADCO) by E.H. Pechan & Associates, Inc. (Pechan); and the Economic
Growth Analysis System (EGAS6.0). Area source emissions estimates for
the 2005 periodic inventory were calculated using population, gasoline
consumption, employment, crop acreages, and other activity surrogates.
The results of an EPA Solvent Mass Balance study were used to estimate
emissions for some categories. Emission factors were derived from local
data, local or national surveys and EPA guidance for the development of
emissions inventories. Point source emissions were subtracted from
total category specific area source emissions to prevent double
counting.
Nonroad mobile source emissions were calculated using EPA's
National Mobile Inventory Model (NMIM) and emissions estimates
developed for commercial marine vessels, aircraft, and railroads (MAR),
three nonroad categories not included in NMIM. Before NMIM was run, the
following modifications and additions were made to the NMIM input data:
(1) Revised activity data for construction equipment using updates
provided by Pechan; (2) revised allocation data for recreational marine
equipment using updates provided by ENVIRON International Corporation
(ENVIRON); (3) added emission factors for diesel tampers/rammers
provided by Pechan; (4) revised population data for construction and
recreational marine equipment using updates provided by Pechan and
ENVIRON, respectively; (5) revised growth rates using updates provided
by Pechan; and (6) revised gasoline parameters, including Reid Vapor
Pressure, oxygenate content and sulfur content, using updates provided
by the States and Pechan. Onroad mobile source emissions were
calculated using the MOBILE6.2 emissions model.
Wisconsin developed a 2007 attainment year inventory using the
methodologies described above to estimate point, nonroad mobile and
onroad mobile sector emissions. Area source emissions were generated by
applying growth factors and applicable emission controls to the 2005
area source sector inventory. Growth factors include the Census
Bureau's County Business Pattern employment data, growth factors
developed for LADCO by Pechan; and EGAS6.0.
Using the inventories described above, Wisconsin's submittal
documents changes in VOC and NOX emissions from 2002 to 2007
for the Manitowoc County and Door County areas. Because Manitowoc and
Door Counties are impacted by transport, WDNR also documented emissions
reductions for the upwind Wisconsin areas of Sheboygan and Milwaukee-
Racine. Emissions data are shown in Tables 2 through 6 below.
BILLING CODE 6560-50-P
[[Page 22056]]
[GRAPHIC] [TIFF OMITTED] TP27AP10.002
BILLING CODE 6560-50-C
[[Page 22057]]
[GRAPHIC] [TIFF OMITTED] TP27AP10.003
Table 4 shows that the Manitowoc County area reduced VOC emissions
by 1.85 tpd and NOX emissions by 2.32 tpd between 2002 and
2007. Table 5 shows that the Door County area reduced VOC emissions by
1.23 tpd and NOX emissions by 2.17 tpd between 2002 and
2007. In addition, as shown in Table 6, the upwind areas of Sheboygan
and Milwaukee-Racine reduced VOC emissions by 39.90 tpd and
NOX emissions by 125.08 tpd between 2002 and 2007. Based on
the information summarized above, Wisconsin has adequately demonstrated
that the improvement in air quality is due to permanent and enforceable
emissions reductions.
4. The Area Has a Fully Approved Maintenance Plan Pursuant to Section
175A of the CAA (Section 107(d)(3)(E)(iv))
In conjunction with its requests to redesignate the Manitowoc
County and Door County nonattainment areas to attainment status,
Wisconsin submitted SIP revisions to provide for the maintenance of the
8-hour ozone NAAQS in the areas through 2020.
a. What is required in a maintenance plan?
Section 175A of the CAA sets forth the required elements of a
maintenance plan for areas seeking redesignation from nonattainment to
attainment. Under section 175A, the plan must demonstrate continued
attainment of the applicable NAAQS for at least ten years after the
Administrator approves a redesignation to attainment. Eight years after
the redesignation, the State must submit a revised maintenance plan
which demonstrates that attainment will continue to be maintained for
ten years following the initial ten-year maintenance period. To address
the possibility of future NAAQS violations, the maintenance plan must
contain contingency measures with a schedule for implementation as EPA
deems necessary to assure prompt correction of any future 8-hour ozone
violations.
The September 4, 1992, John Calcagni memorandum provides additional
guidance on the content of a maintenance plan. The memorandum clarifies
that an ozone maintenance plan should address the following items: the
attainment VOC and NOX emissions inventories, a maintenance
demonstration showing maintenance for the ten years of the maintenance
period, a commitment to maintain the existing monitoring network,
factors and procedures to be used for verification of continued
attainment of the NAAQS, and a contingency plan to prevent or correct
future violations of the NAAQS.
b. Attainment Inventory
The WDNR developed emissions inventories for 2007, one of the years
used to demonstrate monitored attainment of the 8-hour NAAQS, as
described above. The attainment level of emissions is summarized in
Table 3, above.
c. Demonstration of Maintenance
Along with the redesignation requests, WDNR submitted revisions to
the Wisconsin 8-hour ozone SIP to include maintenance plans for the
Manitowoc County and Door County areas, as required by section 175A of
the CAA. These demonstrations show maintenance of the 8-hour ozone
standard through 2020 by showing that current and future emissions of
VOC and NOX for the areas remain at or below attainment year
emission levels. A maintenance demonstration need not be based on
modeling. See Wall v. EPA, 265 F.3d 426 (6th Cir. 2001), Sierra Club v.
EPA, 375 F. 3d 537 (7th Cir. 2004). See also 66 FR 53094, 53099-53100
(October 19, 2001), 68 FR 25413, 25430-25432 (May 12, 2003).
Wisconsin is using emissions inventory projections for the years
2012 and 2020 to demonstrate maintenance. Emissions estimates were
generated for point sources, area sources, and the MAR portion of the
nonroad mobile sector by applying growth factors and applicable
emission controls to the 2005 emissions inventory. The 2005 emissions
inventory was developed following the same methodologies described for
the 2002 inventory, in section VI.A.3.b., above. Growth factors include
the Census Bureau's County Business Pattern employment data, growth
factors developed for LADCO by Pechan; and EGAS6.0. Growth factors were
only available for emission projections to 2018. Emissions for 2020
were estimated using linear interpolation from 2018. For Electric
Generating Unit (EGU) point sources, projections were performed on a
facility by facility basis. The growth in generation emissions
considers corporate utility growth in electricity demand and the
potential dispatch by the regional Midwest Independent Transmission
System Operator to meet broader demand. The growth in electricity
consumption by load type is based on growth rate projections by the
Wisconsin Public Service Commission and historic growth rates. Nonroad
mobile emissions, excluding MAR, were calculated using NMIM with the
modifications and additions to the input data described in section
VI.A.3.b., above. Onroad mobile source emissions were calculated using
the MOBILE6.2 emissions model. Emissions data are shown in Tables 7
through 11, below.
BILLING CODE 6560-50-P
[[Page 22058]]
[GRAPHIC] [TIFF OMITTED] TP27AP10.0