 	ENVIRONMENTAL PROTECTION AGENCY

	40 CFR Parts 52 and 81

	[EPA-R03-OAR-2007-0625; FRL-      ] 

Approval and Promulgation of Air Quality Implementation Plans;
Pennsylvania; Redesignation of the York (York and Adams Counties) 8-hour
Ozone Nonattainment Area to Attainment and Approval of the Area’s
Maintenance Plan and 2002 Base Year Inventory

AGENCY:  Environmental Protection Agency (EPA).

ACTION:  Proposed rule.

SUMMARY:  EPA is proposing to approve a redesignation request and State
Implementation Plan (SIP) revisions submitted by the Commonwealth of
Pennsylvania.  The Pennsylvania Department of Environmental Protection
(PADEP) is requesting that the York (York and Adams Counties) ozone
nonattainment area (York Area) be redesignated as attainment for the
8-hour ozone national ambient air quality standard (NAAQS).  EPA is
proposing to approve the ozone redesignation request for the York Area. 
In conjunction with its redesignation request, the Commonwealth
submitted a SIP revision consisting of a maintenance plan for the York
Area that provides for continued attainment of the 8-hour ozone NAAQS
for at least 10 years after redesignation.  EPA is proposing to make a
determination that the York Area has attained the 8-hour ozone NAAQS,
based upon three years of complete, quality-assured ambient air quality
monitoring data for 2004-2006.  EPA’s proposed approval of the 8-hour
ozone redesignation request is based on its determination that the York
Area has met the criteria for redesignation to attainment specified in
the Clean Air Act (CAA).  In addition, the Commonwealth has also
submitted a 2002 base year inventory for the York Area which EPA is
proposing to approve as a SIP revision.  EPA is also providing
information on the status of its adequacy determination for the motor
vehicle emission budgets (MVEBs) that are identified in the maintenance
plan for the York Area for purposes of transportation conformity, which
EPA is also proposing to approve.  EPA is proposing approval of the
redesignation request and of the maintenance plan and 2002 base year
inventory SIP revisions in accordance with the requirements of the CAA. 

DATES: Written comments must be received on or before [insert date 30
days from date of publication].

ADDRESSES:  Submit your comments, identified by Docket ID Number
EPA-R03-OAR-2007-0625 by one of the following methods:

A.  www.regulations.gov.  Follow the on-line instructions for submitting
comments.

      B.  E-mail:    HYPERLINK "mailto:powers.marilyn@epa.gov" 
powers.marilyn@epa.gov .

C.  Mail:  EPA- R03-OAR-2007-0625, Marilyn Powers, Acting Chief, Air
Quality Planning Branch, Mailcode 3AP21, U.S. Environmental Protection
Agency, Region III, 1650 Arch Street, Philadelphia, Pennsylvania 19103.

      D.  Hand Delivery:  At the previously-listed EPA Region III
address.  Such deliveries are only accepted during the Docket(s normal
hours of operation, and special arrangements should be made for
deliveries of boxed information.

Instructions:  Direct your comments to Docket ID No.
EPA-R03-OAR-2007-0625.  EPA's policy is that all comments received will
be included in the public docket without change, and may be made
available online at www.regulations.gov, including any personal
information provided, unless the comment includes information claimed to
be Confidential Business Information (CBI) or other information whose
disclosure is restricted by statute.  Do not submit information that you
consider to be CBI or otherwise protected through www.regulations.gov or
e-mail.  The www.regulations.gov website 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 
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.



Docket:  All documents in the electronic docket are listed in the
www.regulations.gov index. Although listed in the index, some
information is not publicly available, i.e., CBI or other information
whose disclosure is restricted by statute.  Certain other material, such
as copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form.  Publicly available docket
materials are available either electronically in www.regulations.gov or
in hard copy during normal business hours at the Air Protection
Division, U.S. Environmental Protection Agency, Region III, 1650 Arch
Street, Philadelphia, Pennsylvania 19103.  Copies of the State submittal
are available at the Pennsylvania Department of Environmental Protection
Bureau of Air Quality Control, P.O. Box 8468, 400 Market Street,
Harrisburg, Pennsylvania 17105. 

FOR FURTHER INFORMATION CONTACT:  LaKeshia Robertson, (215) 814-2113, or
by e-mail at   HYPERLINK "mailto:robertson.lakeshia@epa.gov" 
robertson.lakeshia@epa.gov 

SUPPLEMENTARY INFORMATION: 

Throughout this document whenever “we,” “us,” or “our” is
used, we mean EPA.

TABLE OF CONTENTS

 What Are the Actions EPA Is Proposing to Take?

 What Is the Background for These Proposed Actions?

  What Are the Criteria for Redesignation to Attainment?

  Why Is EPA Taking These Actions?

  What Would Be the Effect of These Actions?

  What Is EPA’s Analysis of the Commonwealth’s Request?

  Are the Motor Vehicle Emissions Budgets Established and Identified in
the Maintenance     Plan for the York Area Adequate and Approvable? 

 Proposed Actions

Statutory and Executive Order Reviews

What Are the Actions EPA Is Proposing to Take?

On June 14, 2007, PADEP formally submitted a request to redesignate the
York Area from nonattainment to attainment of the 8-hour NAAQS for
ozone.  Concurrently, Pennsylvania submitted a maintenance plan for the
York Area as a SIP revision to ensure continued attainment in the area
over the next 11 years.  Pennsylvania also submitted a 2002 base year
inventory for the York Area as a SIP revision.  The York Area is
currently designated a basic 8-hour ozone nonattainment area.  EPA is
proposing to determine that the York Area has attained the 8-hour ozone
NAAQS and that it has met the requirements for redesignation pursuant to
section 107(d)(3)(E) of the CAA.  EPA is, therefore, proposing to
approve the redesignation request to change the designation of the York
Area from nonattainment to attainment for the 8-hour ozone NAAQS.  EPA
is also proposing to approve the York Area maintenance plan as a SIP
revision (such approval being one of the CAA criteria for redesignation
to attainment status).  The maintenance plan is designed to ensure
continued attainment in the York Area for the next 11 years.  EPA is
also proposing to approve the 2002 base year inventory for the York Area
as a SIP revision.  Additionally, EPA is announcing its action on the
adequacy process for the MVEBs identified in the York maintenance plan,
and proposing to approve the MVEBs identified for volatile organic
compounds (VOCs) and nitrogen oxides (NOx) for the York Area for
transportation conformity purposes.

II.  What Is the Background for These Proposed Actions?

A.  General

Ground-level ozone is not emitted directly by sources.  Rather,
emissions of NOx and VOC react in the presence of sunlight to form
ground-level ozone.  The air pollutants NOx and VOC are referred to as
precursors of ozone.  The CAA establishes a process for air quality
management through the attainment and maintenance of the NAAQS.

On July 18, 1997, EPA promulgated a revised 8-hour ozone standard of
0.08 parts per million (ppm).  This new standard is more stringent than
the previous 1-hour standard.  EPA designated, as nonattainment, any
area violating the 8-hour ozone NAAQS based on the air quality data for
the three years of 2001-2003.  These were the most recent three years of
data at the time EPA designated 8-hour areas.  The York Area was
designated a basic 8-hour ozone nonattainment area in a Federal Register
notice signed on April 15, 2004 and published on April 30, 2004 (69 FR
23857), based on its exceedance of the 8-hour health-based standard for
ozone during the years 2001-2003.  

On April 30, 2004, EPA issued a final rule (69 FR 23951, 23996) to
revoke the 1-hour ozone NAAQS in the York Area (as well as most other
areas of the country) effective June 15, 2005.  See, 40 CFR 50.9(b); 69
FR at 23966 (April 30, 2004); and 70 FR 44470 (August 3, 2005).

However, o  SEQ CHAPTER \h \r 1 n December 22, 2006, 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).  South Coast Air Quality Management Dist. v. EPA, 472 F.3d
882 (D.C. Cir. 2006) (hereafter “South Coast”).  On June 8, 2007, in
South Coast Air Quality Management Dist. v. EPA, Docket No. 04-1201, in
response to several petitions for rehearing, the D. C. Circuit clarified
that the Phase 1 Rule was vacated only with regard to those parts of the
rule that had been successfully challenged.  Therefore, the Phase 1 Rule
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 remain
effective.  The June 8 decision 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 decision reaffirmed
the December 22, 2006 decision that EPA had improperly failed to retain
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.  

In addition, the June 8 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, which is already
required under EPA’s conformity regulation.  The Court thus clarified
that 1-hour conformity determinations are not required for
anti-backsliding purposes.  The Court upheld EPA’s authority to revoke
the 1-hour standard provided there were adequate anti-backsliding
provisions.  Elsewhere in this document, mainly in section VI. B. “The
York Area Has Met All Applicable Requirements Under Section 110 and Part
D of the CAA and Has a Fully Approved SIP Under Section 110(k) of the
CAA,” EPA discusses its rationale why the decision in South Coast is
not an impediment to redesignating the York Area to attainment of the
8-hour ozone NAAQS.  

The CAA, Title I, Part D, contains two sets of provisions—subpart 1
and subpart 2 –that address planning and control requirements for
nonattainment areas.  Subpart 1 (which EPA refers to as “basic”
nonattainment) contains general, less prescriptive requirements for
nonattainment areas for any pollutant—including ozone—governed by a
NAAQS.  Subpart 2 (which EPA refers to as “classified”
nonattainment) provides more specific requirements for ozone
nonattainment areas.  In 2004, the York Area was classified a basic
8-hour ozone nonattainment area based on air quality monitoring data
from 2001-2003.  Therefore, the York Area is subject to the requirements
of subpart 1 of Part D.

Under 40 CFR part 50, the 8-hour ozone standard is attained when the
3-year average of the annual fourth-highest daily maximum 8-hour average
ambient air quality ozone concentrations is less than or equal to 0.08
ppm (i.e., 0.084 ppm when rounding is considered).  See 69 FR 23857
(April 30, 2004) for further information.  Ambient air quality
monitoring data for the 3-year period must meet data completeness
requirements.  The data completeness requirements are met when the
average percent of days with valid ambient monitoring data is greater
than 90 percent, and no single year has less than 75 percent data
completeness as determined in Appendix I of 40 CFR part 50.  The ozone
monitoring data indicates that the York Area has a design value of 0.081
ppm for the 3-year period of 2004-2006, using complete, quality-assured
data.  Therefore, the ambient ozone data for the York Area indicates no
violations of the 8-hour ozone standard.  

 The York Area

The York Area consists of York and Adams Counties, Pennsylvania.  Prior
to its designation as an 8-hour ozone nonattainment area, the York Area
was a marginal 1-hour ozone nonattainment area, and therefore, was
subject to requirements for marginal nonattainment areas pursuant to
section 182(a) of the CAA.  See 56 FR 56694 (November 6, 1991).  EPA
determined that the York Area has attained the 1-hour ozone NAAQS by the
November 15, 1993 attainment date (60 FR 3349, January 17, 1995).

On June 14, 2007, PADEP requested that the York Area be redesignated to
attainment for the 8-hour ozone standard.  The redesignation request
included three years of complete, quality-assured data for the period of
2004-2006, indicating that the 8-hour NAAQS for ozone had been achieved
in the York Area.  The data satisfies the CAA requirements that the
3-year average of the annual fourth-highest daily maximum 8-hour average
ozone concentration (commonly referred to as the area’s design value),
must be less than or equal to 0.08 ppm (i.e., 0.084 ppm when rounding is
considered).  Under the CAA, a nonattainment area may be redesignated if
sufficient complete, quality-assured data is available to determine that
the area has attained the standard and the area meets the other CAA
redesignation requirements set forth in section 107(d)(3)(E).

III.  What Are the Criteria for Redesignation to Attainment?

The CAA provides the requirements for redesignating a nonattainment area
to attainment.  Specifically, section 107(d)(3)(E) of the CAA, allows
for redesignation, providing that:

(1)  EPA determines that the area has attained the applicable NAAQS; 

(2)  EPA has fully approved the applicable implementation plan for the
area under section 110(k); 

(3)  EPA 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)  EPA 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 redesignations 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 Bill Laxton, 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;

Memorandum from D. Kent Berry, Acting Director, Air Quality Management
Division, to Air Division Directors, Regions 1-10, “Use of Actual
Emissions in Maintenance Demonstrations for Ozone and CO Nonattainment
Areas,” dated 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.

IV.  Why Is EPA Taking These Actions?

On June 14, 2007, PADEP requested redesignation of the York Area to
attainment for the 8-hour ozone standard.  On June 14, 2007, PADEP
submitted a maintenance plan for the York Area as a SIP revision, to
ensure continued attainment of the 8-hour ozone NAAQS over the next 11
years, until 2018.  PADEP also submitted a 2002 base year inventory
concurrently with its maintenance plan as a SIP revision.  EPA has
determined that the York Area has attained the 8-hour ozone standard and
has met the requirements for redesignation set forth in section
107(d)(3)(E).  

V.  What Would Be the Effect of These Actions?

Approval of the redesignation request would change the official
designation of the York Area from nonattainment to attainment for the
8-hour ozone NAAQS found at 40 CFR part 81.  It would also incorporate
into the Pennsylvania SIP a 2002 base year inventory and a maintenance
plan ensuring continued attainment of the 8-hour ozone NAAQS in the York
Area for the next 11 years, until 2018.  The maintenance plan includes
contingency measures to remedy any future violations of the 8-hour NAAQS
(should they occur), and identifies the NOx and VOC MVEBs for
transportation conformity purposes for the years 2009 and 2018.  These
MVEBs are displayed in the following table: 

Table 1:  Motor Vehicle Emissions Budgets in Tons per Summer Day (tpsd)

Year	VOC	NOx

2009 	15.9	22.8

2018	9.0	10.0



VI.  What Is EPA’s Analysis of the Commonwealth’s Request?

EPA is proposing to determine that the York Area has attained the 8-hour
ozone standard and that all other redesignation criteria have been met. 
The following is a description of how the PADEP’s June 14, 2007
submittal satisfies the requirements of section 107(d)(3)(E) of the CAA.

A.  The York Area Has Attained the Ozone NAAQS

EPA is proposing to determine that the York Area has attained the 8-hour
ozone NAAQS.  For ozone, 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 Appendix I of part 50, based on three
complete, consecutive calendar years of quality-assured air quality
monitoring data.  To attain this standard, the design value, which is
the 3-year average of the fourth-highest daily maximum 8-hour average
ozone concentrations, measured at each monitor within the area over each
year, must not exceed the ozone standard of 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 the Air Quality System (AQS).  The monitors
generally should have remained at the same location for the duration of
the monitoring period required for demonstrating attainment.

In the York Area, there are two ozone monitors, located in York County
(York) and another in Adams County (Biglerville) that measures air
quality with respect to ozone.  As part of its redesignation request,
Pennsylvania referenced ozone monitoring data for the years 2004-2006
for the York Area.  This data has been quality assured and is recorded
in the AQS.  PADEP uses the AQS as the permanent database to maintain
its data and quality assures the data transfers and content for
accuracy.  The fourth-highest 8-hour daily maximum concentrations, along
with the three-year average are summarized in Table 2.

Table 2:  York Area Fourth Highest 8-hour Average Values



Monitor/County/AIRS ID	Annual 4th Highest Reading (ppm)

	2004	2005	2006

York County Monitor/AQS ID 42-133-0008	.077	.089	.077

Adams County Monitor/AQS ID 42-001-0002	.072	.080	.074

The average for the 3-year period 2004-2006 is 0.081 ppm

(based on York Monitor/AQS 42-133-0008)



The air quality data for 2004-2006 show that the York Area has attained
the standard with a design value of 0.081 ppm.  The data collected at
the York Area monitor satisfies the CAA requirement that the 3-year
average of the annual fourth-highest daily maximum 8-hour average ozone
concentration is less than or equal to 0.08 ppm.  PADEP’s request for
redesignation for the York Area indicates that the data is complete and
was quality assured in accordance with 40 CFR part 58.  In addition, as
discussed below with respect to the maintenance plan, PADEP has
committed to continue monitoring in accordance with 40 CFR part 58.  In
summary, EPA has determined that the data submitted by Pennsylvania and
data taken from AQS indicate that the York Area has attained the 8-hour
ozone NAAQS.

B.  The York Area Has Met All Applicable Requirements Under Section 110
and Part D of the CAA and Has a Fully Approved SIP Under Section 110(k)
of the CAA

EPA has determined that the York Area has met all SIP requirements
applicable for purposes of this redesignation under section 110 of the
CAA (General SIP Requirements) and that it meets all applicable SIP
requirements under Part D of Title I of the CAA, in accordance with
section 107(d)(3)(E)(v).  In addition, EPA has determined that the SIP
is fully approved with respect to all requirements applicable for
purposes of redesignation in accordance with section 107(d)(3)(E)(ii) of
the CAA.  In making these proposed determinations, EPA ascertained which
requirements are applicable to the York Area and determined that the
applicable portions of the SIP meeting these requirements are fully
approved under section 110(k) of the CAA.  We note that SIPs must be
fully approved only with respect to applicable requirements.

The September 4, 1992 Calcagni memorandum (“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) with respect to
the timing of applicable requirements.  Under this interpretation, to
qualify for redesignation, States requesting redesignation to attainment
must meet only the relevant CAA requirements that came due prior to the
submittal of a complete redesignation request.  See also, Michael
Shapiro memorandum, September 17, 1993, and 60 FR 12459, 12465-66 (March
7, 1995) (redesignation of Detroit-Ann Arbor).  Applicable requirements
of the CAA that come due subsequent to the area’s submittal of a
complete redesignation request remain applicable until a redesignation
is approved, but are not required as a prerequisite to redesignation. 
Section 175A(c) of the CAA.  Sierra Club v. EPA, 375 F.3d 537 (7th Cir.
2004).  See also, 68 FR at 25424, 25427 (May 12, 2003) (redesignation of
St. Louis).

This section sets forth EPA’s views on the potential effect of the
Court’s rulings on this proposed redesignation action.  For the
reasons set forth below, EPA does not believe that the Court’s rulings
alter any requirements relevant to this redesignation action so as to
preclude redesignation, and do not prevent EPA from proposing or
ultimately finalizing this redesignation.  EPA believes that the
Court’s December 22, 2006 and June 8, 2007 decisions impose no
impediment to moving forward with redesignation of this area 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.

1.  Section 110 General SIP Requirements

Section 110(a)(2) of Title I of the CAA delineates the general
requirements for a SIP, which include enforceable emissions limitations
and other control measures, means, or techniques, provisions for the
establishment and operation of appropriate devices necessary to collect
data on ambient air quality, and programs to enforce the limitations. 
The general SIP elements and requirements set forth in section 110(a)(2)
include, but are not limited to the following: 

Submittal of a SIP that has been adopted by the State after reasonable
public notice and hearing;

Provisions for establishment and operation of appropriate procedures
needed to monitor ambient air quality;

Implementation of a source permit program; provisions for the
implementation of part C requirements (Prevention of Significant
Deterioration (PSD));

Provisions for the implementation of part D requirements for NSR permit
programs;

Provisions for air pollution modeling; and

Provisions for public and local agency participation in planning and
emission control rule development.

Section 110(a)(2)(D) requires that SIPs contain certain 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 in accordance with the NOx SIP Call, October 27, 1998 (63
FR 57356), amendments to the NOx SIP Call, May 14, 1999 (64 FR 26298)
and March 2, 2000 (65 FR 11222), and the Clean Air Interstate Rule
(CAIR), May 12, 2005 (70 FR 25162).  However, the section 110(a)(2)(D)
requirements for a State are not linked with a particular nonattainment
area’s designation and classification in that State.  EPA believes
that the requirements linked with a particular nonattainment area’s
designation and classifications 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 do
believe that these requirements are applicable requirements for purposes
of redesignation. 

In addition, EPA believes that the other section 110 elements not
connected with nonattainment plan submissions and not linked with an
area’s attainment status are not applicable requirements for purposes
of redesignation.  The York Area will still be subject to these
requirements after it is redesignated.  The section 110 and Part D
requirements, which are linked with a particular area’s designation
and classification, are the relevant measures to evaluate in reviewing a
redesignation request.  This policy is consistent with EPA’s existing
policy on applicability of conformity (i.e., for redesignations) and
oxygenated fuels requirement.  See, Reading, Pennsylvania, proposed and
final rulemakings (61 FR 53174, 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
redesignation (65 FR at 37890, June 19, 2000), and in the Pittsburgh
redesignation (66 FR at 53099, October 19, 2001).  Similarly, with
respect to the NOx SIP Call rules, EPA noted in its Phase 1 Final Rule
to Implement the 8-hour Ozone NAAQS, that the NOx SIP Call rules are not
“an ‘applicable requirement’ for purposes of section 110(1)
because the NOx rules apply regardless of an area’s attainment or
nonattainment status for the 8-hour (or the 1-hour) NAAQS.” 69 FR
23951, 23983 (April 30, 2004). 

EPA believes that section 110 elements not linked to the area’s
nonattainment status are not applicable for purposes of redesignation. 
As we explain later in this notice, no Part D requirements applicable
for purposes of redesignation under the 8-hour standard became due for
the York Area prior to the submission of the redesignation request.

 

Because the Pennsylvania SIP satisfies all of the applicable general SIP
elements and requirements set forth in section 100(a)(2), EPA concludes
that Pennsylvania has satisfied the criterion of section 107(d)(3)(e)
regarding section 110 of the CAA.

 2.  Part D Nonattainment Requirements Under the 8-Hour Standard 

Pursuant to an April 30, 2004, final rule (69 FR 23951), the York Area
was designated a basic nonattainment area under subpart 1 for the 8-hour
ozone standard.  Sections 172-176 of the CAA, found in subpart 1 of Part
D, set forth the basic nonattainment requirements applicable to all
nonattainment areas.  Section 182 of the CAA, found in subpart 2 of Part
D, establishes additional specific requirements depending on the
area’s nonattainment classification.  

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.  Consequently, it is
possible that this area could, during a remand to EPA, be reclassified
under subpart 2.  Although any future decision by EPA to classify this
area under subpart 2 might trigger additional future requirements for
the area, EPA believes that this does not mean that redesignation of the
area cannot now go forward.  This belief is based upon:  (1) EPA’s
longstanding policy of evaluating redesignation requests 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 in the future be applied.

At the time the redesignation request was submitted, the York Area was
classified under subpart 1 and was obligated to meet subpart 1
requirements.  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,
12465-66 (March 7, 1995) (Redesignation of Detroit-Ann Arbor); Sierra
Club v. EPA, 375 F.3d 537 (7th Cir. 2004), which upheld this
interpretation; 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 D.C. Circuit has recognized the inequity in such
retroactive rulemaking.  See, Sierra Club v. Whitman, 285 F. 3d 63 (D.C.
Cir. 2002), in which the D.C. Circuit upheld a District Court’s ruling
refusing to make retroactive an EPA determination of nonattainment that
was past the statutory due date.  Such determination would have resulted
in the imposition of additional requirements on that 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 area by applying to it for purposes of
redesignation, additional SIP requirements under subpart 2 that were not
in effect at the time it submitted its redesignation request.

With respect to 8-hour subpart 2 requirements, if the York Area
initially had been classified under subpart 2, the first two Part D
subpart 2 requirements applicable to the York Area under section 182(a)
of the CAA would be a base year inventory requirement pursuant to
section 182(a)(1) of the CAA, and the emissions statement requirement
pursuant to section 182(a)(3)(B).

As stated previously, these requirements are not due for purposes of
redesignation of the York Area, but nevertheless, Pennsylvania already
has in its approved SIP, an emissions statement rule for the 1-hour
standard that covers all portions of the designated 8-hour nonattainment
area, and that satisfies the emissions statement requirement for the
8-hour standard.  See, 25 Pa. Code 135.21(a)(1) codified at 40 CFR
52.2020; 60 FR 2881, January 12, 1995.  With respect to the base year
inventory requirement, in this notice of proposed rulemaking, EPA is
proposing to approve the 2002 base year inventory for the York Area,
which was submitted on June 14, 2007, concurrently with its maintenance
plan, into the Pennsylvania SIP.  EPA is proposing to approve the 2002
base year inventory as fulfilling the requirements, if necessary, of
both sections 182(a)(1) and 172(c)(3) of the CAA.  A detailed evaluation
of Pennsylvania’s 2002 base year inventory for the York Area can be
found in a Technical Support Document (TSD) prepared by EPA for this
rulemaking.  EPA has determined that the emission inventory and the
emissions statement for the York Area have been satisfied.

In addition to the fact that Part D requirements applicable for purposes
of redesignation did not become due prior to submission of the
redesignation request, EPA believes that the general conformity and NSR
requirements do not require approval prior to redesignation.

With respect to section 176, Conformity Requirements, section 176(c) of
the CAA requires states to establish criteria and procedures to ensure
that Federally-supported or funded projects conform to the air quality
planning goals in the applicable SIP.  The requirement to determine
conformity applies to transportation plans, programs, and projects
developed, funded or approved under Title 23 U.S.C. 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
that the CAA required the EPA to promulgate.  EPA believes it is
reasonable to interpret the conformity SIP requirements as not applying
for purposes of evaluating the redesignation request under section
107(d) since State conformity rules are still required after
redesignation and Federal conformity rules apply where State rules have
not been approved.  See, Wall v. EPA, 265 F. 3d 426, 438-440 (6th Cir.
2001), upholding this interpretation.  See also, 60 FR 62748 (December
7, 1995).

In the case of the York Area, EPA has also determined that before being
redesignated, the York Area need not comply with the requirement that a
NSR program be approved prior to redesignation.  EPA has also determined
that areas being redesignated need not comply with the requirement that
a NSR program be approved prior to redesignation, provided that the area
demonstrates maintenance of the standard without Part D NSR in effect. 
The rationale for this position is described in a memorandum from Mary
Nichols, Assistant Administrator for Air and Radiation, dated October
14, 1994, entitled, “Part D NSR Requirements of Areas Requesting
Redesignation to Attainment.”  Normally, a State’s Prevention of
Significant Deterioration (PSD) program will become effective in the
area immediately upon redesignation to attainment.  See the more
detailed explanations in the following redesignation rulemakings: 
Detroit, MI (60 FR 12467-12468, March 7, 1995); Cleveland-Akron-Lorrain,
OH (61 FR 20458, 20469-70, May 7, 1996); Louisville, KY (66 FR 53665,
53669, October 23, 2001); Grand Rapids, MI (61 FR 31831, 31836-31837,
June 21, 1996).  In the case of the York Area, the Chapter 127 Part D
NSR regulations in the Pennsylvania SIP (codified at 40 CFR
52.2020(c)(1)) explicitly apply the requirements for NSR in section 184
of the CAA to ozone attainment areas within the ozone transport region
(OTR).  The OTR NSR requirements are more stringent than that required
for a marginal or basic ozone nonattainment area.  On October 19, 2001
(66 FR 53094), EPA fully approved Pennsylvania’s NSR SIP revision
consisting of Pennsylvania’s Chapter 127 Part D NSR regulations that
cover the York Area.

EPA has also interpreted the section 184 OTR requirements, including the
NSR program, as not being applicable for purposes of redesignation.  The
rationale for this is based on two considerations.  First, the
requirement to submit SIP revisions for the section 184 requirements
continues to apply to areas in the OTR after redesignation to
attainment.  Therefore, the State remains obligated to have NSR, as well
as reasonably available control technology (RACT), and Vehicle
Inspection and Maintenance (I/M) programs even after redesignation. 
Second, the section 184 control measures are region-wide requirements
and do not apply to the York Area by virtue of the area’s designation
and classification. See, 61 FR 53174, 53175-53176 (October 10, 1996) and
62 FR 24826, 24830-32 (May 7, 1997). 

3.  Part D Nonattainment Area Requirements Under the 1-Hour Standard 

In its June 8, 2007 decision the Court limited its vacatur so as to
uphold those provisions of the anti-backsliding requirements that were
not successfully challenged.  Therefore the Area must meet the federal
anti-backsliding requirements, see 40 CFR 51.900, et seq.; 70 FR 30592,
30604 (May 26, 2005) which apply by virtue of the area's classification
for the 1-hour ozone NAAQS.  As set forth in more detail below, the area
must also address four additional anti-backsliding provisions identified
by the Court in its decisions.  		

The anti-backsliding provisions at 40 CFR 51.905(a)(1) prescribe 1-hour
ozone NAAQS requirements that continue to apply after revocation of the
1-hour ozone NAAQS to former 1-hour ozone nonattainment areas.  Section
51.905(a)(1)(i) provides that:  

“The area remains subject to the obligation to adopt and implement the
applicable requirements as defined in section 51.900(f), except as
provided in paragraph (a)(1)(iii) of paragraph (b) of this section.” 

Section 51.900(f), as amended by 70 FR 30592, 30604 (May 26, 2005),
states that: 

“Applicable requirements means for an area the following requirements
to the extent such requirements applied to the area for the area's
classification under section 181(a)(1) of the CAA for the 1-hour NAAQS
at the time of designation for the 8-hour NAAQS.

		(1)  RACT.

		(2)  I/M.

		(3)  Major source applicability cut-offs for purposes of RACT.

		(4)  Rate of Progress (ROP) reductions.

		(5)  Stage II vapor recovery.

		(6)  Clean fuels fleet program under section 183(c)(4) of the CAA.

		(7)  Clean fuels for boilers under section 182(e)(3) of the CAA.

		(8)  Transportation Control Measures (TCMs) during heavy traffic hours
as

required by section 182(e)(4) of the CAA.

		(9)  Enhanced (ambient) monitoring under section 182(c)(1) of the CAA.

		(10)  Transportation control measures (TCMs) under section 

182(c)(5) of the CAA.

		(11)  Vehicle miles traveled (VMT) provisions of section 182(d)(1) of
the CAA.

		(12)  NOx requirements under section 182(f) of the CAA.

		(13)  Attainment demonstration or alternative as provided under
section 

51.905(a)(1)(ii).”

Pursuant to 40 CFR 51.905(c), the York Area is subject to the
obligations set forth in 51.905(a) and 51.900(f).  

Prior to its designation as an 8-hour ozone nonattainment area, the York
Area was designated a marginal nonattainment area for the 1-hour
standard.  With respect to the 1-hour standard, the applicable
requirements under the anti-backsliding provisions at 40 CFR
51.905(a)(1) for the York Area are limited to the RACT and I/M programs
specified in section 182 (a) of the CAA and are discussed in the
following paragraghs:

Section 182(a)(2)(A) required SIP revisions to correct or amend RACT for
sources in marginal areas, such as the York Area, that were subject to
control technique guidelines (CTGs) issued before November 15, 1990
pursuant to CAA section 108.  On December 22, 1994, EPA fully approved
into the Pennsylvania SIP all corrections required under section
182(a)(2)(A) of the CAA (59 FR 65971, December 22, 1994).  EPA believes
that this requirement applies only to marginal and higher classified
areas under the 1-hour NAAQS pursuant to the 1990 amendments to the CAA;
therefore, this is a one-time requirement.  After an area has fulfilled
the section 182(a)(2)(A) requirement for the 1-hour NAAQS, there is no
requirement under the 8-hour NAAQS. 

Section 182(a)(2)(B) of the CAA relates to the savings clause for
certain I/M programs.  It requires marginal areas to adopt vehicle I/M
programs.  This provision was not applicable to the York Area because
this area did not have nor was required to have an I/M program before
November 15, 1990.

In addition the Court held that EPA should have retained four additional
measures in its anti-backsliding provisions: (1) Nonattainment area NSR;
(2) Section 185 penalty fees; (3) contingency measures under section
172(c)(9) or 182(c)(9) of the CAA; and (4) 1-hour motor vehicle emission
budgets that were yet not replaced by 8-hour emissions budgets.  These
requirements are addressed below:

With respect to NSR, EPA has determined that areas being redesignated
need not have an approved nonattainment New Source Review program, for
the same reasons discussed previously with respect to the applicable
Part D requirement for the 8-hour standard.  

The section 185 penalty fee requirement applies only to severe and
extreme nonattainment area, and was never applicable in the York 1-hour
marginal nonattainment area.  

With respect to the requirement for submission of contingency measures
for the 1-hour standard, section 182(a) does not require contingency
measures for marginal areas.

  SEQ CHAPTER \h \r 1 The conformity portion of the Court’s ruling
does not impact the redesignation request for the York Area except to
the extent that the Court in its June 8 decision clarified that for
those areas with 1-hour MVEBs, anti-backsliding requires that those
1-hour budgets must be used for 8-hour conformity determinations until
replaced by 8-hour budgets.   There are no applicable 1-hour MVEBs for
the York Area.  (As discussed elsewhere in this document, EPA is
proposing to approve 8-hour MVEBs for the York Area.)  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.  The court clarified that 1-hour conformity determinations are
not required for anti-backsliding purposes.

Thus EPA has concluded that the York Area has met all requirements
applicable for redesignation under the 1-hour standard.

4.  Transport Region Requirements

All areas in the Ozone Transport Region (OTR), both attainment and
nonattainment, are subject to additional control requirements under
section 184 for the purpose of reducing interstate transport of
emissions that may contribute to downwind ozone nonattainment.  The
section 184 requirements include RACT, NSR, enhanced vehicle inspection
and maintenance (I/M), and Stage II vapor recovery or a comparable
measure.   

In the case of the York Area, which is located in the OTR, nonattainment
NSR will continue to be applicable after redesignation.  On October 19,
2001, EPA approved the 1-hour NSR SIP revision for the area.  See 66 FR
53094 (October 19, 2001).   

EPA has also interpreted the section 184 OTR requirements, including
NSR, as not being applicable for purposes of redesignation.  Reading, PA
Redesignation, 61 FR 53174, (October 10, 1996), 62 FR 24826 (May 7,
1997).  The rationale for this is based on two considerations.  First,
the requirement to submit SIP revisions for the section 184 requirements
continues to apply to areas in the OTR after redesignation to
attainment.  Therefore, the State remains obligated to have NSR, as well
as RACT, and I/M even after redesignation.  Second, the section 184
control measures are region-wide requirements and do not apply to the
area by virtue of the area’s nonattainment designation and
classification, and thus are properly considered not relevant to an
action changing an area’s designation.  See 61 FR 53174, 53175-6
(October 10, 1996) and 62 FR 24826, 24830-32 (May 7, 1997).  

5.  York Area has a Fully Approved SIP for Purposes of Redesignation  

EPA has fully approved the Pennsylvania SIP for the purposes of this
redesignation.  EPA may rely on prior SIP approvals in approving a
redesignation request.  Calcagni Memo, p.3; Southwestern Pennsylvania
Growth Alliance v. Browner, 144 F. 3d 984, 989-90 (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 also, 68 FR
at 25425 (May 12, 2003) and citations therein. 

C.  The Air Quality Improvement in the York Area 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

EPA believes that the Commonwealth has demonstrated that the observed
air quality improvement in the York Area is due to permanent and
enforceable reductions in emissions resulting from implementation of the
SIP, Federal measures, and other State-adopted measures.  Emissions
reductions attributable to these rules are shown in Table 3.

Table 3:  Total VOC and NOx Emissions for 2002 and 2004 in tons per
summer day (tpsd)



Volatile Organic Compounds (VOC)

Year	Point	Area	Nonroad	Mobile	Total

2002	8.5	27.1	25.3	10.4	 71.3

2004	5.3	26.8	21.3	10.1	 63.5

Diff.(02-04)	-3.2	-0.3	-4.0	-0.3	 -7.8

Nitrogen Oxides (NOx)

Year	Point	Area	Nonroad	Mobile	Total

2002	70.2	2.9	36.6	14.3	124.0

2004	75.3	3.0	31.9	13.7	123.9

Diff (02-04)	5.1	0.1	-4.7	-0.6	-0.1



Between 2002 and 2004, VOC emissions decreased by 7.8 tpsd, and NOx
emissions decreased by 0.1 tpsd.  These reductions, and anticipated
future reductions, are due to the following permanent and enforceable
measures. 

  Stationary Point Sources 

 Federal NOx SIP Call (66 FR 43795, August 21, 2001)

Stationary Area Sources 

Solvent Cleaning (68 FR 2206, January 16, 2003)

Portable Fuel Containers (69 FR 70893, December 8, 2004)

3.  Highway Vehicle Sources

Federal Motor Vehicle Control Programs (FMVCP)

	-Tier 1 (56 FR 25724, June 5, 1991) 

-Tier 2 (65 FR 6698, February 10, 2000)

Heavy-duty Engine and Vehicle Standards (62 FR 54694, October 21, 1997,
and 65 FR 59896, October 6, 2000)

National Low Emission Vehicle (NLEV) Program (PA) (64 FR 72564, December
28, 1999)

Vehicle Emission Inspection/Maintenance Program (70 FR 58313, October 6,
2005)

4.  Non-Road Sources

Non-road Diesel (69 FR 38958, June 29, 2004)

EPA believes that permanent and enforceable emissions reductions are the
cause of the long-term improvement in ozone levels and are the cause of
the York Area achieving attainment of the 8-hour ozone standard.

D.  The York Area Has a Fully Approvable Maintenance Plan Pursuant to
Section 175A of the CAA

In conjunction with its request to redesignate the York Area to
attainment status, Pennsylvania submitted a SIP revision to provide for
maintenance of the 8-hour ozone NAAQS in the York Area for at least 11
years after redesignation.  The Commonwealth is requesting that EPA
approve this SIP revision as meeting the requirement of CAA 175A.  Once
approved, the maintenance plan for the 8-hour ozone NAAQS will ensure
that the SIP for the York Area meets the requirements of the CAA
regarding maintenance of the applicable 8-hour ozone standard.

What Is Required in a Maintenance Plan?

Section 175 of the CAA sets forth the 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 10 years after approval of a redesignation
of an area to attainment.  Eight years after the redesignation, the
Commonwealth must submit a revised maintenance plan demonstrating that
attainment will continue to be maintained for the 10 years following the
initial 10-year period.  To address the possibility of future NAAQS
violations, the maintenance plan must contain such contingency measures,
with a schedule for implementation, as EPA deems necessary to assure
prompt correction of any future 8-hour ozone violations.  Section 175A
of the CAA sets forth the elements of a maintenance plan for areas
seeking redesignation from nonattainment to attainment.  The Calcagni
memo provides additional guidance on the content of a maintenance plan. 
An ozone maintenance plan should address the following provisions:

(a)  an attainment emissions inventory;

(b)  a maintenance demonstration;

(c)  a monitoring network;

(d)  verification of continued attainment; and

(e)  a contingency plan.

Analysis of the York Area Maintenance Plan

(a) Attainment inventory – An attainment inventory includes the
emissions during the time period associated with the monitoring data
showing attainment.  PADEP determined that the appropriate attainment
inventory year is 2004.  That year establishes a reasonable year within
the three-year block of 2004-2006 as a baseline and accounts for
reductions attributable to implementation of the CAA requirements to
date.  The 2004 inventory is consistent with EPA guidance and is based
on actual “typical summer day” emissions of VOC and NOx during 2004
and consists of a list of sources and their associated emissions.  

The 2002 and 2004 point source data was compiled from actual sources. 
Pennsylvania requires owners and operators of larger facilities to
submit annual production figures and emission calculations each year. 
Throughput data are multiplied by emission factors from Factor
Information Retrieval (FIRE) Data Systems and EPA’s publication series
AP-42, and are based on Source Classification Codes (SCC).  

The 2002 area source data was compiled using county-level activity data,
from census numbers, from county numbers, etc.  The 2004 area source
data was projected from the 2002 inventory using temporal allocations
provided by the Mid-Atlantic Regional Air Management Association
(MARAMA).

The on-road mobile source inventories for 2002 and 2004 were compiled
using MOBILE6.2 and Pennsylvania Department of Transportation (PENNDOT)
estimates for VMT.  The PADEP has provided detailed data summaries to
document the calculations of mobile on-road VOC and NOx emissions for
2002, as well as for the projection years of 2004, 2009, and 2018 (shown
in Tables 5 and 6 below). 

The 2002 and 2004 emissions for the majority of non-road emission source
categories were estimated using the EPA NONROAD 2005 model. The NONROAD
model calculates emissions for diesel, gasoline, liquefied petroleum
gasoline, and compressed natural gas-fueled non-road equipment types and
includes growth factors.  The NONROAD model does not estimate emissions
from locomotives or aircraft.  For 2002 and 2004 locomotive emissions,
the PADEP projected emissions from a 1999 survey using national fuel
consumption information and EPA emission and conversion factors.  There
are no commercial aircraft operations in York and Adams Counties.  For
2002 and 2004 aircraft emissions, PADEP estimated emissions using small
airport operations statistics from   HYPERLINK "http://www.airnav.com" 
www.airnav.com , and emission factors and operational characteristics in
the EPA-approved model, Emissions and Dispersion Modeling System (EDMS).
 

More detailed information on the compilation of the 2002, 2004, 2009,
and 2018 inventories can found in the Technical Appendices, which are
part of the June 14, 2007 state submittal.

Maintenance Demonstration – On June 14, 2007, the PADEP submitted a
maintenance plan as required by section 175A of the CAA.  The York Area
maintenance plan shows maintenance of the 8-hour ozone NAAQS by
demonstrating that current and future emissions of VOC and NOx remain at
or below the attainment year 2004 emissions levels throughout the York
Area through the year 2018.  A maintenance demonstration need not be
based on modeling.  See, Wall v. EPA, supra; Sierra Club v. EPA, supra. 
See also, 66 FR at 53099-53100; 68 FR at 25430-32.

Tables 4 and 5 specify the VOC and NOx emissions for the York Area for
2004, 2009, and 2018.  The PADEP chose 2009 as an interim year in the
maintenance demonstration period to demonstrate that the VOC and NOx
emissions are not projected to increase above the 2004 attainment level
during the time of the maintenance period.

Table 4:  Total VOC Emissions for 2004-2018 (tpsd)

Source Category	2004 VOC 

Emissions	2009 VOC 

Emissions	2018 VOC Emissions

Point*	5.3	8.2	10.1

Area	26.8	26.2	28.9

Mobile**	21.3	15.9	9.0

Nonroad	10.1	8.4	6.9

Total	63.5	58.7	54.9

*The stationary point source emissions shown here do not include
available banked emission credits as indicated in Appendix A-4 submitted
with the maintenance plan.

**Includes safety margin identified in the motor vehicle emission
budgets for transportation conformity.

Table 5:  Total NOx Emissions for 2004-2018 (tpsd)

Source

Category	2004 NOx 

Emissions	2009 NOx

Emissions	2018 NOx 

Emissions

Point*	75.3	74.1	79.7

Area	3.0	3.1	3.3

Mobile**	31.9	22.8	10.0

Non-road	13.7	11.2	6.5

Total	123.9	111.2	99.5

*The stationary point source emissions shown here do not include
available banked emission credits as indicated in Appendix A-4.

**Includes safety margin identified in the motor vehicle emission
budgets for transportation conformity.

Additionally, the following programs are either effective or due to
become effective and will further contribute to the maintenance
demonstration of the 8-hour ozone NAAQS:

The Clean Air Interstate Rule (CAIR)  (71 FR 25328, April 28, 2006).

The Federal NOx SIP Call (66 FR 43795, August 21, 2001).

Area VOC regulations concerning portable fuel containers (69 FR 70893,
December 8, 2004), consumer products (69 FR 70895, December 8, 2004),
and architectural and industrial maintenance coatings (AIM) (69 FR
68080, November 23, 2004).

Federal Motor Vehicle Control Programs (light-duty ) (Tier 1, Tier 2; 56
FR 25724, June 5, 1991; 65 FR 6698, February 10, 2000).

Vehicle emission/inspection/maintenance program (70 FR 58313, October 6,
2005).

Heavy duty diesel on-road (2004/2007) and low sulfur on-road (2006); 66
FR 5002, (January 18, 2001).

Non-road emission standards (2008) and off-road diesel fuel 2007/2010);
69 FR 38958 (June 29, 2004).

NLEV/PA Clean Vehicle Program (54 FR 72564, December 28, 1999) -
Pennsylvania will implement this program in car model year 2008.

Pennsylvania Heavy-Duty Diesel Emissions Control Program. (May 10,
2002).

	

Based on the comparison of the projected emissions and the attainment
year emissions along with the additional measures, EPA concludes that
PADEP has successfully demonstrated that the 8-hour ozone standard
should be maintained in the York Area.

(c)  Monitoring Network – There are currently two monitors measuring
ozone in the York Area.  PADEP will continue to operate its current air
quality monitor (located in York and Adams Counties), in accordance with
40 CFR part 58.

(d)  Verification of Continued Attainment – In addition to maintaining
the key elements of its regulatory program, the Commonwealth will track
the attainment status of the ozone NAAQS in the York Area by reviewing
air quality and emissions data during the maintenance period.  The
Commonwealth will perform an annual evaluation of Vehicle Miles Traveled
(VMT) data and emissions reported from stationary sources, and compare
them to the assumptions about these factors used in the maintenance
plan.  The Commonwealth will also evaluate the periodic (every three
years) emission inventories prepared under EPA’s Consolidated Emission
Reporting Regulation (40 CFR 51, subpart A) to see if they exceed the
attainment year inventory (2004) by more than 10 percent.  PADEP will
also continue to operate the existing ozone monitoring station in the
York Area pursuant to 40 CFR part 58 throughout the maintenance period
and submit quality-assured ozone data to EPA through the AQS system. 
Section 175A(b) of the CAA states that eight years following the
redesignation of the York Area, PADEP will be required to submit a
second maintenance plan that will ensure attainment through 2028.  PADEP
has made that commitment to meet the requirement of section 175A(b).

(e) The Maintenance Plan’s Contingency Measures – The contingency
plan provisions are designed to promptly correct a violation of the
NAAQS that occurs after redesignation.  Section 175A of the CAA requires
that a maintenance plan include such contingency measures as EPA deems
necessary to ensure that the State will promptly correct a violation of
the NAAQS that occurs after redesignation.  The maintenance plan should
identify the events that would “trigger” the adoption and
implementation of a contingency measure(s), the contingency measure(s)
that would be adopted and implemented, and the schedule indicating the
time frame by which the state would adopt and implement the measure(s).

The ability of the York Area to stay in compliance with the 8-hour ozone
standard after redesignation depends upon VOC and NOx emissions in the
area remaining at or below 2004 levels.  The Commonwealth’s
maintenance plan projects VOC and NOx emissions to decrease and stay
below 2004 levels through the year 2018.  The Commonwealth’s
maintenance plan outlines the procedures for the adoption and
implementation of contingency measures to further reduce emissions
should a violation occur.  

Contingency measures will be considered if for two consecutive years the
fourth highest 8-hour ozone concentrations at the York and Adams
Counties monitors are above 84 ppb.  If this trigger point occurs, the
Commonwealth will evaluate whether additional local emission control
measures should be implemented in order to prevent a violation of the
air quality standard.  PADEP will also analyze the conditions leading to
the excessive ozone levels and evaluate which measures might be most
effective in correcting the excessive ozone levels.  PADEP will also
analyze the potential emissions effect of Federal, state, and local
measures that have been adopted but not yet implemented at the time the
excessive ozone levels occurred.  PADEP will then begin the process of
implementing any selected measures.

Contingency measures will also be considered in the event that a
violation of the 8-hour ozone standard occurs at the York and Adams
Counties, Pennsylvania monitors.  In the event of a violation of the
8-hour ozone standard, PADEP will adopt additional emissions reduction
measures as expeditiously as practicable in accordance with the
implementation schedule listed later in this notice and the Pennsylvania
Air Pollution Control Act in order to return the area to attainment with
the standard.  Contingency measures to be considered for the York Area
will include, but not be limited to the following:

Regulatory measures:

- Additional controls on consumer products.

- Additional controls on portable fuel containers.

Non-Regulatory measures:

- Voluntary diesel engine “chip reflash” (installation software to
correct the defeat      device option on certain heavy-duty diesel
engines).			

- Diesel retrofit, including replacement, repowering or alternative fuel
use, for public         or private local on-road or off-road fleets.	

      - Idling reduction technology for Class 2 yard locomotives.

      - Idling reduction technologies or strategies for truck stops,
warehouses and other                 freight- handling facilities.

-  Accelerated turnover of lawn and garden equipment, especially
commercial          equipment, including promotion of electric
equipment.

	      - Additional promotion of alternative fuel (e.g., biodiesel) for
home heating and agricultural use.

The plan lays out a process to have any regulatory contingency measures
in effect within 19 months of the trigger.  The plan also lays out a
process to implement the non-regulatory contingency measures within
12-24 months of the trigger.

VII.  Are the Motor Vehicle Emissions Budgets Established and Identified
in the York Area Maintenance Plan Adequate and Approvable?

A.  What are the Motor Vehicle Emissions Budgets?

Under the CAA, States are required to submit, at various times, control
strategy SIPs and maintenance plans in ozone areas.  These control
strategy SIPs (i.e., RFP SIPs and attainment demonstration SIPs) and
maintenance plans identify and establish MVEBs for certain criteria
pollutants and/or their precursors to address pollution from on-road
mobile sources.  In the maintenance plan, the MVEBs are termed
“on-road mobile source emission budgets.”  Pursuant to 40 CFR part
93 and 51.112, MVEBs must be established in an ozone maintenance plan. 
An MVEB is the portion of the total allowable emissions that is
allocated to highway and transit vehicle use and emissions.  An 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).  The
preamble also describes how to establish and revise the MVEBs in control
strategy SIPs and maintenance plans.

Under section 176(c) of the CAA, new transportation projects, such as
the construction of new highways, must “conform” to (i.e., be
consistent with) the part of the State’s air quality plan that
addresses pollution from cars and trucks.  “Conformity” to the SIP
means that transportation activities will not cause new air quality
violations, worsen existing violations, or delay timely attainment of or
reasonable progress towards the NAAQS.  If a transportation plan does
not “conform,” most new 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 ensuring
conformity of such transportation activities to a SIP.

When reviewing submitted “control strategy” SIPs or maintenance
plans containing MVEBs, EPA must affirmatively find the MVEB contained
therein “adequate” for use in determining transportation conformity.
 After EPA affirmatively finds the submitted MVEB is adequate for
transportation conformity purposes, that MVEB can 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 “adequacy” of a MVEB
are set forth in 40 CFR 93.118(e)(4).

EPA’s process for determining “adequacy” consists of three basic
steps:  public notification of a SIP submission, a public comment
period, and EPA’s adequacy finding.  This process for determining the
adequacy of submitted SIP MVEBs was initially outlined in EPA’s May
14, 1999 guidance, “Conformity Guidance on Implementation of March 2,
1999, Conformity Court Decision.”  This guidance was finalized in the
Transportation Conformity Rule Amendments for the “New 8-Hour Ozone
and PM2.5 National Ambient Air Quality Standards and Miscellaneous
Revisions for Existing Areas; Transportation Conformity Rule Amendments
– Response to Court Decision and Additional Rule Change” on July 1,
2004 (69 FR 40004).  EPA consults this guidance and follows this
rulemaking in making its adequacy determinations.

The MVEBS for the York Area are listed in Table 1 of this document for
2009 and 2018, and are the projected emissions for the on-road mobile
sources plus any portion of the safety margin allocated to the MVEBs
(safety margin allocation for 2009 and 2018 only).  These emission
budgets, when approved by EPA, must be used for transportation
conformity determinations.

B.  What is a Safety Margin?

A safety margin is the difference between the attainment level of
emissions (from all sources) and the projected level of emissions (from
all sources) in the maintenance plan.  The attainment level of emissions
is the level of emissions during one of the years in which the area met
the NAAQS.  The safety margin is the extra emissions that can be
allocated as long as the total attainment level of emissions is
maintained.  The credit, or a portion thereof, can be allocated to any
of the source categories.  The following example is for the 2018 safety
margin:  the York Area first attained the 8-hour ozone NAAQS during the
2002 to 2004 time period.  The Commonwealth used 2004 as a year to
determine attainment levels of emissions for the York Area.

The total emissions from point, area, mobile on-road, and mobile
non-road sources in 2004 equaled 63.5 tpd of VOC and 123.9 tpd of NOx. 
PADEP projected emissions out to the year 2018 and projected a total of
54.9 tpd of VOC and 99.5 tpd of NOx from all sources in the York Area. 
The safety margin for the York Area for 2018 is the difference between
these amounts, or 8.6 tpd of VOC and 24.4 tpd of NOx.  The emissions up
to the level of the attainment year including the safety margins are
projected to maintain the area’s air quality consistent with the
8-hour ozone NAAQS.  Table 6 shows the safety margins for the 2009 and
2018 years.

Table 6:  2009 and 2018 Safety Margins for the York Area

Inventory Year	VOC Emissions (tpd)	NOx Emissions (tpd)

2004 Attainment	63.5	123.9

2009 Interim	58.7	111.2

2009 Safety Margin	4.8	12.7

2004 Attainment	63.5	123.9

2018 Final	54.9	99.5

2018 Safety Margin	8.6	24.4



PADEP allocated 0.8 tpd VOC and 1.0 tpd NOx to the 2009 interim VOC
projected on-road mobile source emissions projection and the 2009
interim NOx projected on-road mobile source emissions projection to
arrive at the 2009 MVEBs.  For the 2018 MVEBs, PADEP allocated 1.1 tpd
VOC and 1.0 tpd NOx from the 2018 safety margins to arrive at the 2018
MVEBs.  Once allocated to the mobile source budgets, these portions of
the safety margins are no longer available, and may not be allocated to
any other source category.  Table 7 shows the final 2009 and 2018 MVEBs
for the York Area.

Table 7:  2009 and 2018 Final MVEBs for the York Area

Inventory Year	VOC Emissions (tpd)	NOx Emissions (tpd)

2009 Projected On-road Mobile Source Projected Emissions	15.1	21.8

2009 Safety Margin Allocated to MVEBs	0.8	1.0

2009 MVEBs	15.9	22.8

2018 Projected On-road Mobile Source Projected Emissions	7.9	9.0

2018 Safety Margin Allocated to MVEBs	1.1	1.0

2018 MVEBs	9.0	10.0

 

C.  Why Are the MVEBs Approvable?

The 2009 and 2018 MVEBs for the York Area are approvable because the
MVEBs for NOx and VOCs continue to maintain the total emissions at or
below the attainment year inventory levels as required by the
transportation conformity regulations.

D.  What Is the Adequacy and Approval Process for the MVEBs in the York
Area Maintenance Plan?

The MVEBs for the York Area maintenance plan are being posted to EPA’s
conformity Website concurrently with this proposal.  The public comment
period will end at the same time as the public comment period for this
proposed rule.  In this case, EPA is concurrently processing the action
on the maintenance plan and the adequacy process for the MVEBs contained
therein.  In this proposed rule, EPA is proposing to find the MVEBs
adequate and also proposing to approve the MVEBs as part of the
maintenance plan.  The MVEBs cannot be used for transportation
conformity until the maintenance plan and associated MVEBs are approved
in a final Federal Register notice, or EPA otherwise finds the budgets
adequate in a separate action following the comment period.

If EPA receives adverse written comments with respect to the proposed
approval of the York Area MVEBs, or any other aspect of our proposed
approval of this updated maintenance plan, we will respond to the
comments on the MVEBs in our final action or proceed with the adequacy
process as a separate action.  Our action on the York Area MVEBs will
also be announced on EPA’s conformity Website:    HYPERLINK
"http://www.epa.gov/otaq/stateresources/transconf/index.htm" 
http://www.epa.gov/otaq/stateresources/transconf/index.htm 

(once there, click on “Adequacy Review of SIP Submissions).

VIII.  Proposed Actions

EPA is proposing to determine that the York Area has attained the 8-hour
ozone NAAQS.  EPA is also proposing to approve the redesignation of the
York Area from nonattainment to attainment for the 8-hour ozone NAAQS. 
EPA has evaluated Pennsylvania’s redesignation request and determined
that it meets the redesignation criteria set forth in section
107(d)(3)(E) of the CAA.  EPA believes that the redesignation request
and monitoring data demonstrate that the York Area has attained the
8-hour ozone standard.  The final approval of this redesignation request
would change the designation of the York Area from nonattainment to
attainment for the 8-hour ozone standard.  EPA is proposing to approve
the maintenance plan for the York Area, submitted on June 14, 2007, as a
revision to the Pennsylvania SIP.  EPA is proposing to approve the
maintenance plan for the York Area because it meets the requirements of
section 175A as described previously in this notice.  EPA is also
proposing to approve the 2002 base-year inventory for the York Area, and
the MVEBs submitted by Pennsylvania for the York Area in conjunction
with its redesignation request.  EPA is soliciting public comments on
the issues discussed in this document.  These comments will be
considered before taking final action.

IX.  Statutory and Executive Order Reviews

Under Executive Order 12866 (58 FR 51735, October 4, 1993), this
proposed action is not a "significant regulatory action" and therefore
is not subject to review by the Office of Management and Budget.  For
this reason, this action is also not subject to Executive Order 13211,
"Actions Concerning Regulations That Significantly Affect Energy Supply,
Distribution, or Use"  (66 Fed. Reg. 28355 (May 22, 2001)).  This action
merely proposes to approve state law as meeting Federal requirements and
imposes no additional requirements beyond those imposed by state law. 
Redesignation of an area to attainment under section 107(d)(3)(e) of the
CAA does not impose any new requirements on small entities. 
Redesignation is an action that affects the status of a geographical
area and does not impose any new regulatory requirements on sources. 
Redesignation of an area to attainment under section 107(d)(3)(E) of the
CAA does not impose any new requirements on small entities. 
Redesignation is an action that affects the status of a geographical
area and does not impose any new regulatory requirements on sources. 
Accordingly, the Administrator certifies that this proposed rule will
not have a significant economic impact on a substantial number of small
entities under the Regulatory Flexibility Act (5 U.S.C. 601 et seq.).  
Because this rule proposes to approve pre-existing requirements under
state law and does not impose any additional enforceable duty beyond
that required by state law, it does not contain any unfunded mandate or
significantly or uniquely affect small governments, as described in the
Unfunded Mandates Reform Act of 1995 (Public Law 104-4).  Because this
action affects the status of a geographical area or allows the state to
avoid adopting or implementing other requirements and because this
action does not impose any new requirements on sources, this proposed
rule also does not have a substantial direct effect on one or more
Indian tribes, on the relationship between the Federal Government and
Indian tribes, or on the distribution of power and responsibilities
between the Federal Government and Indian tribes, as specified by
Executive Order 13175 (65 FR 67249, November 9, 2000), nor will it have
substantial direct effects on the States, on the relationship between
the national government and the States, or on the distribution of power
and responsibilities among the various levels of government, as
specified in Executive Order 13132 (64 FR 43255, August 10, 1999),
because it merely proposes to approve a state rule implementing a
Federal requirement, and does not alter the relationship or the
distribution of power and responsibilities established in the CAA. This
proposed rule also is not subject to Executive Order 13045 (62 FR 19885,
April 23, 1997), because it approves a state rule implementing a Federal
standard.

In reviewing SIP submissions, EPA(s role is to approve state choices,
provided that they meet the criteria of the CAA.  In this context, in
the absence of a prior existing requirement for the State to use
voluntary consensus standards (VCS), EPA has no authority to disapprove
a SIP submission for failure to use VCS.  It would thus be inconsistent
with applicable law for EPA, when it reviews a SIP submission, to use
VCS in place of a SIP submission that otherwise satisfies the provisions
of the CAA.  Redesignation is an action that affects the status of a
geographical area and does not impose any new requirements on sources. 
Thus, the requirements of section 12(d) of the National Technology
Transfer and Advancement Act of 1995 (15 U.S.C. 272 note) do not apply. 
As required by section 3 of Executive Order 12988 (61 FR 4729, February
7, 1996), in issuing this proposed rule, EPA has taken the necessary
steps to eliminate drafting errors and ambiguity, minimize potential
litigation, and provide a clear legal standard for affected conduct. 
EPA has complied with Executive Order 12630 (53 FR 8859, March 15, 1988)
by examining the takings implications of the rule in accordance with the
“Attorney General’s Supplemental Guidelines for the Evaluation of
Risk and Avoidance of Unanticipated Takings” issued under the
executive order.  

This rule, proposing to approve the redesignation of the York Area to
attainment for the 8-hour ozone NAAQS, the associated maintenance plan,
the 2002 base-year inventory, and the MVEBs identified in the
maintenance plan, does not impose an information collection burden under
the provisions of the Paperwork Reduction Act of 1995 (44 U.S.C. 3501 et
seq.).

List of Subjects 

40 CFR Part 52

Environmental protection, Air pollution control, Nitrogen oxides, Ozone,
Reporting and recordkeeping requirements, Volatile organic compounds. 

40 CFR Part 81

Environmental protection, Air pollution control, National parks,
Wilderness Areas.

Authority: 42 U.S.C. 7401 et seq.

                                                                        
                /s/

___________________________           	 ___________________

Dated:   October 16, 2007                              	Donald S. Welsh,

Regional Administrator,

                                                                 	Region
III.

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