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Approval and Promulgation of Implementation Plans; Designation of Areas for Air Quality Planning Purposes; State of California; PM-10; Revision of Designation; Redesignation of the San Joaquin Valley Air Basin PM-10 Nonattainment Area to Attainment; Approval of PM-10 Maintenance Plan for the San Joaquin Valley Air Basin; Approval of Commitments for the East Kern PM-10 Nonattainment Area

PDF Version (12 pp, 230K, About PDF)

[Federal Register: April 25, 2008 (Volume 73, Number 81)]
[Proposed Rules]
[Page 22307-22318]
From the Federal Register Online via GPO Access [wais.access.gpo.gov]
[DOCID:fr25ap08-14]

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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 52 and 81
[EPA-R09-OAR-2008-0306; FRL-8558-7]

Approval and Promulgation of Implementation Plans; Designation of
Areas for Air Quality Planning Purposes; State of California; PM-10;
Revision of Designation; Redesignation of the San Joaquin Valley Air
Basin PM-10 Nonattainment Area to Attainment; Approval of PM-10
Maintenance Plan for the San Joaquin Valley Air Basin; Approval of
Commitments for the East Kern PM-10 Nonattainment Area

AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.

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SUMMARY: EPA is proposing to approve the State of California's request
to revise the designation for the San Joaquin Valley (SJV) serious
nonattainment area for particulate matter of ten microns or less (PM-
10) (SJV nonattainment area) by splitting the area into two separate
nonattainment areas: The San Joaquin Valley Air Basin serious PM-10
nonattainment area and the East Kern serious PM-10 nonattainment area.
EPA is also proposing to redesignate the SJVAB nonattainment area to
attainment for the PM-10 national ambient air quality standard (NAAQS)
and proposing to approve the PM-10 maintenance plan, motor vehicle
emissions budgets and conformity trading mechanism for the area. EPA is
also proposing to exclude from use in determining that the area has
attained the standard two exceedances that EPA has concluded were
caused by exceptional events that occurred on July 4, 2007 and January
4, 2008. Finally, EPA is proposing to approve enforceable commitments
by the Kern County Air Pollution Control District and the California
Air Resources Board to install a PM-10 monitor in the East Kern
nonattainment area and to address Clean Air Act requirements under
section 189(d) as necessary for the area.

DATES: Any comments must arrive by May 27, 2008.

ADDRESSES: Submit comments, identified by docket number EPA-R09-OAR-
2008-0306, by one of the following methods:
    1. Federal eRulemaking Portal: http://www.regulations.gov. Follow
the on-line instructions.
    2. E-mail: lo.doris@epa.gov.
    3. Mail or deliver: Doris Lo (Air-2), U.S. Environmental Protection
Agency Region IX, 75 Hawthorne Street, San Francisco, CA 94105-3901.
    Instructions: All comments will be included in the public docket
without change and may be made available online at http://
www.regulations.gov, including any personal information provided,
unless the comment includes Confidential Business Information (CBI) or
other information whose disclosure is restricted by statute.
Information that you consider CBI or otherwise protected should be
clearly identified as such and should not be submitted through http://
www.regulations.gov or e-mail. http://www.regulations.gov is an
``anonymous access'' system, and EPA will not know your identity or
contact information unless you provide it in the body of your comment.
If you send e-mail directly to EPA, your e-mail address will be
automatically captured and included as part of the public comment. 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.
    Docket: The index to the docket for this action is available
electronically at http://www.regulations.gov and in hard copy at EPA
Region IX, 75 Hawthorne Street, San Francisco, California. While all
documents in the docket are listed in the index, some information may
be publicly available only at the hard copy location (e.g., copyrighted
material), and some may not be publicly available in either location
(e.g., CBI). To inspect the hard copy materials, please schedule an
appointment during normal business hours with the contact listed in the
FOR FURTHER INFORMATION CONTACT section.

FOR FURTHER INFORMATION CONTACT: Doris Lo, EPA Region IX, (415) 972-
3959, lo.doris@epa.gov.

SUPPLEMENTARY INFORMATION: Throughout this document, ``we'' ``us'' and
``our'' refer to EPA.

Table of Contents

I. Background
II. Summary of EPA's Proposed Actions
III. Proposed Revised Boundary Redesignation

[[Page 22308]]

    A. State's Submittal
    B. EPA's Evaluation of Request to Revise Boundary Designation
IV. Proposed Redesignation of the SJV Air Basin to Attainment for
the PM-10 Standard and Approval of PM-10 Maintenance Plan
    A. EPA has determined that the area has attained the NAAQS
    B. The applicable implementation plan has been fully approved by
EPA under section 110(k) of the CAA
    C. EPA has determined that the improvement in air quality is due
to permanent and enforceable reductions in emissions
    D. The State has met all applicable requirements for the area
under section 110 and Part D of the CAA
    1. Basic SIP Requirements under CAA Section 110
    2. SIP Requirements under Part D
    E. EPA has fully approved a maintenance plan, including a
contingency plan, for the area under section 175A of the CAA
    1. An attainment emissions inventory to identify the level of
emissions in the area sufficient to attain the NAAQS
    2. A demonstration of maintenance of the NAAQS for 10 years
after redesignation
    3. Verification of continued attainment through operation of an
appropriate air quality monitoring network
    4. Contingency provisions to promptly correct any violation of
the NAAQS that occurs after redesignation of the area
    F. Transportation conformity and motor vehicle emissions budgets
    1. CARB Methodology for Estimating PM-10 in the Emissions Budgets
    2. Adequacy of the 2007 Plan's Budgets
    3. Trading Mechanism
V. Proposed Commitments for East Kern
VI. Proposed Actions
VII. Statutory and Executive Order Reviews

I. Background

    On May 26, 2004, EPA approved the serious area PM-10 plan for the
SJV nonattainment area, ``2003 PM10 Plan, San Joaquin Valley Plan to
Attain Federal Standards for Particulate Matter 10 Microns and
Smaller'' submitted by the State on August 19, 2003 and amendments to
that plan submitted on December 30, 2003 (collectively, 2003 Plan). See
69 FR 30006; 40 CFR 81.305. This plan provided for, among other things,
the implementation of best available control measures (BACM). In
addition, since the SJV nonattainment area had failed to meet its
original serious area attainment deadline of December 31, 2001, the
State was required under section 189(d) of the Clean Air Act (CAA or
the Act) to submit a plan that provided for an annual reduction in PM-
10 or PM-10 precursors of not less than five percent until attainment.
A detailed discussion of the history of PM-10 planning in the SJV
nonattainment area and of EPA's approval of the 2003 Plan can be found
in its proposed and final actions and the associated dockets. 69 FR
5412 (February 4, 2004); 69 FR 30006.
    On October 30, 2006, EPA determined that the SJV nonattainment area
had attained the 24-hour PM-10 standard \1\ based on air quality data
from 2003 through 2005. In this action we noted that there were several
exceedances of the PM-10 standard that were likely due to exceptional
events which EPA would address in subsequent actions. 71 FR 63642.
Subsequently EPA issued a final action affirming that the PM-10
standard has been attained in the SJV nonattainment area based on air
quality data from 2004 through 2006. 73 FR 14687 (March 19, 2008).
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    \1\ The level of the national primary 24-hour ambient air
quality standard for particulate matter is 150 micrograms per cubic
meter (μg/m\3\). The standard is attained when the expected
number of days per calendar year with a 24-hour average concentration
above 150 μg/m\3\, as determined in accordance with appendix K to 40
CFR part 50, is equal to or less than one. See 40 CFR 50.6.
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    On November 16, 2007, the State submitted to EPA the ``2007 PM10
Maintenance Plan and Request for Redesignation,'' September 20, 2007,
for the San Joaquin Valley Air Pollution Control District (SJVAPCD or
the District) (2007 Plan).\2\ On January 31, 2008, the State submitted
a request to split the existing SJV serious PM-10 nonattainment area
into two separate nonattainment areas: (1) The San Joaquin Valley Air
Basin and (2) the western portion of the Kern County Air Pollution
Control District (KCAPCD). Letter from James N. Goldstene, California
Air Resources Board (CARB), to Deborah Jordan, EPA, with attachments,
January 31, 2008 (Goldstene letter).
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    \2\ The SJVAPCD District adopted the 2007 Plan on September 20,
2007 and submitted it to the State on September 21, 2007. The State
``* * * updated the attainment inventory * * * to reflect emission
reductions achieved by ARB adopted measures that had not been
accounted for'' before submitting the 2007 Plan to EPA on November
16, 2007. (Staff Report, Analysis of the San Joaquin Valley 2007
PM10 Maintenance Plan, Air Resources Board, Release Date: October
12, 2007 (ARB Staff Report), pp. 7-8 and Appendix B). Thus the
applicable emissions inventories in the 2007 Plan are found in the
ARB Staff Report.
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    On February 29, 2008, the State submitted enforceable commitments
by CARB and the KCAPCD to monitor for PM-10 in the western portion of
the KCAPCD and to address CAA State Implementation Plan (SIP)
requirements for this area as necessary. Letter from James N.
Goldstene, CARB, to Wayne Nastri, EPA, with enclosures, February 29, 2008.
    Finally, on January 23, 2008, the State submitted to EPA the
``Exceptional Event Documentation, PM10, Fireworks, Bakersfield, CA,
July 4, 2007'' and on April 15, 2008, the State submitted to EPA the
``Natural Event Documentation, Bakersfield, California, January 4, 2008.''

II. Summary of EPA's Proposed Actions

    First, EPA is proposing to grant the State's request to split the
existing SJV nonattainment area into two separate nonattainment areas.
EPA is then proposing to grant the State's request to redesignate the
portion of the SJV nonattainment area located in the San Joaquin Valley
Air Basin to attainment for the PM-10 standard and to approve the PM-10
maintenance plan, motor vehicle emissions budgets and conformity
trading mechanism for the area. EPA is also proposing to exclude from
use in determining that the area has attained the PM-10 standard data
showing exceedances caused by exceptional events that occurred on July
4, 2007 and January 4, 2008. Finally, EPA is proposing to approve
commitments by CARB and the KCAPCD to monitor for PM-10 in the western
portion of the KCAPCD and to address CAA SIP requirements for the area
as necessary.

III. Proposed Revised Boundary Designation

A. State's Submittal

    As stated above, on January 31, 2008, the State submitted a request
to EPA to split the existing SJV PM-10 nonattainment area into two
separate nonattainment areas: (1) The San Joaquin Valley Air Basin and
(2) the western portion of the KCAPCD. The State's submittal states
that ``[t]his change will address the inconsistency between
California's adopted air basin boundary for the San Joaquin Valley and
the boundary U.S. EPA is using for PM10 planning.'' The State's
submittal includes information about jurisdiction, geography,
population and degree of urbanization, employment and traffic/commuting
patterns, and emissions and air quality which supports the revised
boundary designation. See Goldstene letter.

B. EPA's Evaluation of Request To Revise Boundary Designation

    The existing SJV nonattainment area includes the entire counties of
San Joaquin, Fresno, Kings, Madera, Merced, Stanislaus and Tulare and
part of Kern County. The part of Kern County in the existing SJV
nonattainment area is a region that straddles the Sierra Nevada and
Tehachapi mountains and is located in two separate air basins: the SJV Air
Basin and the Mojave Desert Air Basin (MDAB). The dividing line between

[[Page 22309]]

these two air basins coincides with the jurisdictional boundary between
the KCAPCD and the SJVAPCD. This dividing line also coincides with the
boundary that we are today proposing to draw between the two
nonattainment areas which we are proposing to designate as the SJV Air
Basin (SJVAB) PM-10 nonattainment area and the East Kern PM-10
nonattainment area.\3\ Thus, if we finalize the revision to the
boundary designation, the SJVAB nonattainment area will include only
those areas that are in the SJV Air Basin (i.e., all of the seven
counties mentioned above and the part of Kern County that is under the
jurisdiction of the SJVAPCD) and the East Kern PM-10 nonattainment area
will include the part of Kern County that is currently in the existing
SJV nonattainment area, is in the MDAB and is under the jurisdiction of
the KCAPCD.\4\ Together, these two new PM-10 nonattainment areas will cover
the same geographic area as the original SJV PM-10 nonattainment area.
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    \3\ We are proposing to call the new area ``East Kern'' because
it is the eastern part of Kern County that is currently within the
existing SJV nonattainment area.
    \4\ The KCAPCD's jurisdiction also includes the remaining part
of Kern County which extends eastward beyond the proposed East Kern area.
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    Under section 107(d)(3)(D) of the CAA, the Governor of any state
may, on the Governor's own motion, submit to EPA a revised designation
of any area or portion thereof within the state.\5\ EPA is required to
approve or deny a submittal of a revised designation within 18 months
of receipt. The type of revised designation that the State of
California submitted on January 31, 2008 involves a boundary change
only and does not involve a change in status (e.g., from
``nonattainment,'' to ``attainment'' or ``unclassifiable'') of any area.
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    \5\ Boundary changes are an inherent part of a designation or
redesignation of an area under the CAA. See CAA section 107(d)(1)(B)(ii).
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    In determining whether to approve or deny a state's submittal of a
request for a revised boundary designation under section 107(d)(3)(D),
EPA uses the same factors Congress directed EPA to consider when the
Agency initiates a revision to a designation of an area on its own
motion under section 107(d)(3)(A). These factors include ``air quality
data, planning and control considerations, or any other air quality-
related considerations the Administrator deems appropriate.'' In
addition, because the State's revised designation involves
nonattainment areas, we also take into account CAA section
107(d)(1)(A), which provides that nonattainment areas are to include
the geographic area that does not meet, or that contributes to ambient
air quality in a nearby area that does not meet, the NAAQS for a given
pollutant.
    California has provided a compelling technical justification as to
why the proposed SJVAB and East Kern nonattainment areas should be
designated as separate PM-10 planning areas. A summary of the State's
reasoning follows:
    Jurisdiction. The proposed SJVAB area is under the jurisdiction of
the SJVAPCD and the proposed East Kern area is under the jurisdiction
of the KCAPCD. The proposed revised designation will align the boundary
along these jurisdictional lines. This realignment will make the air
quality planning and implementation process more efficient and
straightforward since the local air pollution control agencies, SJVAPCD
and KCAPCD, can only adopt and implement plans and rules in the area
for which they have jurisdiction.
    Geography. The East Kern area is in the MDAB, a different air basin
than the SJVAB area; it is separated from the SJVAB area by the Sierra
Nevada and Tehachapi Mountain Ranges at elevations up to 7,500 feet.
The Kern River Valley and the Cummings Valley in the East Kern area are
located at approximately 2600 feet and 3800 feet, respectively. These
elevations are comparable to other areas in the MDAB and much higher
than the average elevation in the western portion of Kern County in the
SJVAB which is between 450 and 500 feet. Eastern Kern County, which
includes the proposed East Kern nonattainment area, is a vast arid
desert while the SJVAB portion of Kern County is part of the urbanized,
agricultural, and industrial SJV. The mountains surrounding the SJVAB
form a bowl trapping air pollutants in the SJVAB, but the East Kern
area is located above the inversion layer which traps air pollutants in
the SJVAB and thus, experiences different weather from the SJVAB.
    Population and Degree of Urbanization. There are no major or fast
growing population centers in eastern Kern County. Eastern Kern County
covers approximately 3800 square miles, with a total population of
approximately 131,000 (in 2005) and a low population density of
approximately 35 persons per square mile. In the last decade (1995-
2005), population increased by 15,000 persons. The Kern River Valley
and Cummings Valley, which are in the East Kern area, are sparsely
populated; the greater Lake Isabella region in the Kern River Valley
has approximately 15,000 inhabitants; and the west Tehachapi area in
the Cummings Valley has approximately 13,000 inhabitants. In contrast,
the western portion of Kern County in the SJVAB extends over 4400
square miles, includes the urban Bakersfield area, housed 640,000
persons (in 2005), and has a population density of approximately 145
persons per square mile, which is four times the population density of
eastern Kern County. In the last decade, the total population in
western Kern County grew by 136,000 persons, nine times the population
growth in eastern Kern County.
    Employment and Traffic/Commuting Patterns. Eastern Kern County,
which includes the proposed East Kern nonattainment area, is not
strongly integrated economically with western Kern County. People tend
to live and work in eastern Kern County, and because of its geographic
isolation there is no convenient commute to cities outside the region.
The economy of western Kern is largely based on the oil and
agricultural industries. The primary employer in eastern Kern County is
the Tehachapi State Prison. Due to the geographic isolation, there is
no convenient commute to cities outside the area. In 2005, vehicles
traveled approximately 5.1 million miles per day throughout eastern
Kern County. In contrast, in western Kern County vehicles traveled
approximately 19.8 million miles per day, close to 4 times the average
travel in eastern Kern County. Also, eastern Kern residents are not
dependent on western Kern for economic activities such as employment,
shopping, or other services. There are no significant commute patterns
from eastern Kern County into the SJVAB, the MDAB, or the South Coast
Air Basin or vice versa.
    Emissions. There are only a handful of major emission sources in
eastern Kern County, which includes the proposed East Kern area, and
projected source and industrial growth is minimal. Total primary PM-10
emissions as well as nitrogen oxide emissions (NOX), the
main precursor of secondary PM-10 in the area, are declining. Major
sources of primary PM-10 include the Tehachapi State Prison (11.5 tons
per year (tpy) in 2005), followed by two aggregate operations (9.7 tpy
and 8.5 tpy); the two largest NOX sources are the Tehachapi
State Prison (12.8 tpy) and two natural gas pumps that lift water to
Tehachapi (14.8 tpy and 12.2 tpy). In contrast, western Kern County
houses 35 major sources of primary PM-10 with emissions over 10 tpy and
47 major sources of NOX with emissions over 10 tpy. Compared
to the entire SJV PM-10 nonattainment area, sources in all of eastern
Kern County contributed only eight percent of the direct PM-10

[[Page 22310]]

emissions and eight percent of the NOX emissions in 2005.
    Air Quality. The chemical composition of PM-10 in eastern Kern
County, which includes the proposed East Kern area, differs
significantly from the PM-10 chemical composition in the SJVAB area.
While dust is the main component of PM-10 in eastern Kern County,
NOX has been determined to be the only significant precursor
for the SJVAB area. 69 FR 30006. Currently there is no Federal
Reference Method (FRM) or Federal Equivalent Method (FEM) monitoring of
PM-10 in the East Kern area. However, there is an Interagency
Monitoring of Protected Visual Environments (IMPROVE) monitor located
in the Kern River Valley. This IMPROVE monitor has, since February
2000, consistently measured PM-10 concentrations far below the PM-10
standard. A summary of the maximum PM-10 daily values at the IMPROVE
monitor is provided in Table 1 below.

         Table 1.--Summary of Maximum PM-10 Daily Values for the Domelands IMPROVE Monitor (μg/m\3\)
----------------------------------------------------------------------------------------------------------------
                      Year                            1st max         2nd max         3rd max         4th max
----------------------------------------------------------------------------------------------------------------
2001............................................              33              33              32              32
2002............................................             109              53              49              49
2003............................................              66              42              37              37
2004............................................              52              50              47              45
2005............................................              21              14               6               5
2006............................................              39              36              35             34
----------------------------------------------------------------------------------------------------------------
Source: IMPROVE Web site, http://vista.cira.colostate.edu/improve/Default.htm Exit Disclaimer

    Based on the factors set forth above, EPA has considered the
State's request in accordance with the criteria listed in CAA section
107(d)(3)(A). We find that the State has sufficiently demonstrated that
the SJVAB and East Kern should be separate nonattainment areas because
they lie in separate air basins, are under different local
jurisdictions, have different population densities and growth levels,
do not share commute patterns, have different emissions sources and
have different types of air pollutants. Pursuant to CAA section
107(d)(3)(D), EPA is therefore proposing to approve the State's request
to revise the boundary designation of the existing SJV PM-10
nonattainment area by splitting the area into two separate PM-10
nonattainment areas, the SJVAB and East Kern.
    As explained below, we are further proposing to redesignate the
SJVAB to attainment for PM-10. Pending further air quality monitoring
and until such time as the East Kern nonattainment area meets the CAA
requirements for redesignation, the East Kern area would be classified
as a serious PM-10 nonattainment area. Thus the East Kern nonattainment
area would retain the classification and nonattainment designation that
applied to it when it was part of the SJV nonattainment area and would
likewise retain the attainment determination applicable to that area.
In order to address the serious area PM-10 statutory requirements,
KCAPCD and CARB have made the enforceable commitments discussed in
section V. below.

IV. Proposed Redesignation of the SJVAB to Attainment for the PM-10 Standard

    On November 16, 2007, the State submitted to EPA the 2007 Plan
which addresses PM-10 maintenance plan requirements and includes a
discussion of how the SJVAB (i.e., the portion of the current
nonattainment area under the jurisdiction of the SJVAPCD) meets the CAA
redesignation requirements.
    Section 107(d)(3)(E) of the CAA states that an area can be
redesignated to attainment if the following conditions are met:
    (1) EPA has determined that the area has attained the NAAQS.
    (2) The applicable implementation plan has been fully approved by
EPA under section 110(k) of the CAA.
    (3) EPA has determined that the improvement in air quality is due
to permanent and enforceable reductions in emissions.
    (4) The State has met all applicable requirements for the area
under section 110 and Part D of the CAA.
    (5) EPA has fully approved a maintenance plan, including a
contingency plan, for the area under section 175A of the CAA.
    These requirements are discussed in more detail in a September 4,
1992 EPA Memorandum, ``Procedures for Processing Request to Redesignate
Areas to Attainment, John Calcagni, Director, Air Quality Management
Division'' (Calcagni memo). We discuss how these requirements are met
for the SJVAB in detail below.

A. EPA Has Determined That the Area Has Attained the NAAQS

    The Calcagni memo states that there are two components involved in
meeting this requirement. The first component relies on an analysis of
quality-assured ambient air quality data and an ambient air monitoring
network that is representative of the area of highest concentrations.
For PM-10 in the SJVAB, EPA has reviewed the ambient air quality data
and determined and affirmed that the PM-10 NAAQS has been attained for
the years 2003 through 2006. See 71 FR 40952, 71 FR 63642, 72 FR 49046
and 73 FR 14687. These determinations also discuss the adequacy of the
monitoring network for the SJVAB.
    EPA has also evaluated the air quality data in EPA's Air Quality
System (AQS) database for 2007 and through February 2008. This data has
been included in the docket for this proposed rule. A summary of the
2005-2007 data is provided in Table 2 below.

                           Table 2.--Summary of 2005--2007 PM-10 Attainment Statistics
                               [Based on Federal Reference Method PM-10 monitors]
----------------------------------------------------------------------------------------------------------------
                                                 Observed three   Estimated 24-
                                                  year 24-hour        hour
                Monitoring site                  maximum (μg/   exceedance           Attainment status
                                                      m\3\)           days
----------------------------------------------------------------------------------------------------------------
Fresno-Drummond................................             132               0  Attainment.
Fresno-1st Street..............................             117               0  Attainment.

[[Page 22311]]

Clovis.........................................             116               0  Attainment.
Bakersfield-Golden State Highway...............             154               0  Attainment.
Bakersfield-California Ave.....................             153               0  Attainment.
Oildale........................................             145               0  Attainment.
Corcoran.......................................             140               0  Attainment.
Hanford........................................             142               0  Attainment.
Merced.........................................              94               0  Attainment.
Stockton-Hazelton..............................              82               0  Attainment.
Stockton-Wagner................................              69               0  Attainment.
Modesto........................................              96               0  Attainment.
Turlock........................................              97               0  Attainment.
Visalia........................................             141               0  Attainment.
----------------------------------------------------------------------------------------------------------------
Source: EPA Air Quality System (AQS) Database.

    One exceedance of the PM-10 standard was recorded at the
Bakersfield-Golden FEM \6\ on July 4, 2007. The State has flagged this
exceedance as being caused by an exceptional event, fourth of July
fireworks celebrations. EPA has reviewed the documentation for this
event and has concurred with the State's request. Letter from Wayne
Nastri, EPA, to Mary D. Nichols, California Environmental Protection
Agency, April 21, 2008. For 2008, one exceedance of the PM-10 standard
was recorded also at the Bakersfield-Golden federal equivalent monitor
\7\ on January 4. The State has flagged this exceedance as being caused
by an exceptional event, high winds. EPA has reviewed the documentation
for this event and has concurred with the State's request. Letter from
Wayne Nastri, EPA, to Mary D. Nichols, California Environmental
Protection Agency, April 21, 2008.
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    \6\ The Bakersfield-Golden monitoring site includes a special
purpose FEM known as a Tapered Element Oscillating Microbalance
(TEOM) continuous automated analyzer. The exceedances on July 4,
2007 and January 4, 2008 were recorded on the TEOM. Data are
collected at the site using both a TEOM, which provides continuous
PM-10 data for public reporting purposes, and a high-volume FRM. The
FRM operates at a less than everyday schedule, as allowed by EPA
regulations, and was not operating on July 4, 2007 or January 4, 2008.
    \7\ See footnote 6 above.
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    Under EPA's Exceptional Events Rule, the Agency may exclude data
from regulatory determinations related to exceedances or violations of
the NAAQS if the state adequately demonstrates that an exceptional
event caused the exceedance or violation. 40 CFR Sections 50.1, 50.14.
Therefore, for the reasons set forth in the concurrence letters, EPA is
proposing to exclude data showing exceedances on July 4, 2007 and
January 4, 2008 in determining whether the SJVAB has continued to
attain the PM-10 standard in 2007 and through February 2008. The
concurrence letters explain how the State has met its burden to
demonstrate that these exceedances qualify as exceptional events. Thus,
EPA believes that according to the ambient air monitoring data for the
SJVAB, the PM-10 NAAQS has been attained.
    The second component that may be included in the showing that a PM-
10 area has met the requirement that the NAAQS has been attained
involves an analysis using air quality modeling. This component is
addressed under the maintenance plan requirements discussion below.

B. The Applicable Implementation Plan Has Been Fully Approved by EPA
Under Section 110(k) of the CAA

    The Calcagni memo states that the SIP for the area must be fully
approved under section 110(k) of the CAA and must satisfy all
requirements that apply to the area. Section 107(d)(3)(E)(ii). As
stated above, on August 19, 2003 and December 30, 2003, the State
submitted the 2003 Plan. This plan addressed all applicable
requirements for the SJV serious PM-10 nonattainment area. On May 24,
2004, EPA approved all components of the 2003 Plan except for the
plan's contingency measures. EPA may rely on prior SIP approvals in
approving a redesignation request. See Calcagni memo, p. 3;
Southwestern Pennsylvania Growth Alliance v. Browner, 144 F.3d 984,
989-990 (6th Cir. 1998), Wall v. EPA, 265 F.3d 526 (6th Cir. 2001). The
contingency measure requirement under CAA section 172(c)(9) was
subsequently suspended on October 30, 2006 pursuant to EPA's
determination of attainment under its Clean Data Policy. See 71 FR
63642, 63663. Thus, since contingency measures are no longer a required
element for the SJVAB, all applicable requirements have been approved
under 110(k) of the CAA. See also section IV.D. below.

C. EPA Has Determined That the Improvement in Air Quality Is Due to
Permanent and Enforceable Reductions in Emissions

    The Calcagni memo states that the state must be able to reasonably
attribute the improvement in air quality to emission reductions which
are permanent and enforceable, (CAA section 107(d)(3)(E)(iii)) and the
improvement should not be a result of temporary reductions (e.g.,
economic downturns or shutdowns) or unusually favorable meteorology. In
making this showing, the state should estimate the emission reductions
from adopted and implemented Federal, State and local control measures,
and consider the emission rates, production capacities, and other
related information to show that the air quality improvements are the
result of implemented controls.
    The 2007 Plan provides a discussion and comparison of the air
quality, meteorology and emissions trends since 1990. See 2007 Plan,
pp. 23-28. First, the 2007 Plan discusses the significant improvements
in PM-10 air quality since 1990, noting that from 1990 to 1992 there
were 33 estimated exceedance days, from 1998 to 2000 there were 5.9
exceedance days and from 2002 to 2004 there were 2.9 exceedance days.
Id. Next the 2007 Plan states that this improvement has occurred while
air quality plans and regulations have been adopted and notes that in
the late 1980's, before the adoption of plans and regulations, ``* * *
it was not uncommon to have 50

[[Page 22312]]

or more estimated annual exceedances of the 24-hour PM10 standard
[with] peak measurements well above 250 micrograms per cubic meter
(μg/m\3\), and annual averages of 80 μg/m\3\.'' Id.
    The 2007 Plan also states that since 1990 the Valley has
experienced rapid economic growth, citing to increases in population
and vehicle miles traveled (2007 Plan, p. 26, Figure 3), while at the
same time the PM-10 and PM-10 precursor emissions were decreasing (2007
Plan, p. 26, Figure 4). The 2007 Plan also did not find any major
sector-wide shutdowns, identifying at most ``* * * about 2 tons per day
of PM-10 reductions from shutdowns during the attainment period of
interest.'' 2007 Plan, p. 25. Thus, it does not appear that the air
quality improvements were due to any economic downturns or shutdowns.
    The 2007 Plan also provides an analysis of the meteorological
conditions, including wind speeds, precipitation, temperature and
atmospheric stability, to determine if there were any favorable
meteorological conditions that may have led to the improvement in air
quality during 2003-2006. 2007 Plan, p. 27 and Appendix C. The 2007
Plan found that compared to long-term averages, the period from 2003 to
2006 had: No variation in average annual wind speeds; a higher than
average level of precipitation with two dry years (2003 and 2004) and
two wet years (2005 and 2006); warmer than average temperatures; and a
lower than average stability level. The higher than average
precipitation would favor lower PM-10 levels, but it is important to
note that 2003 and 2004 were in fact dry years, ranking 98th and 122nd
in wetness over a period of 128 years (1878 to 2006). The higher than
average temperature could have increased the potential for high PM-10
levels, but the higher stability level could have decreased the
potential by providing more dispersion. The 2007 Plan concludes that
these analyses indicate that there is no consistent pattern to show
that there was favorable meteorology leading to the improvement in PM-
10 levels during 2003 to 2006. Id.
    The 2007 Plan further states that the SJVAPCD has adopted over 500
new rules and amendments since 1992, many of which are for the purpose
of reducing PM-10 or PM-10 precursor emissions. The 2007 Plan shows
that all of the rules and commitments in the 2003 Plan have been
adopted by the SJVAPCD and many of them have been approved by EPA and
are thus federally enforceable. The SJVAPCD has adopted rules which
control NOX and PM-10 emissions from cotton gins, boilers,
steam generators, and process heaters, agricultural sources, dryers,
dehydrators and ovens, glass melting furnaces, fugitive dust sources,
open burning and other source categories. 2007 Plan, p. 27 and Appendix
B. In addition, the State has adopted measures to meet its commitments
in the 2003 Plan to achieve 10 tons per day (tpd) of NOX
reductions and 0.5 tpd of PM-10 reductions. 2007 Plan, p. 17. The air
quality improvements described above can be attributed to the reductions
in NOX and PM-10 emissions achieved by these measures.
    The 2007 Plan shows decreases in the emissions inventories for the
SJVAB from approximately 1000 tpd in 2000 to approximately 900 tpd in
2005 and to approximately 800 tpd in 2010. ARB Staff Report, Appendix
B. As discussed further in Section E.1. below, the emissions
inventories are a summary of all source categories in the SJVAB and are
developed based on information about emission rates, production
capacities, and other source-related information. The emissions
inventories in the 2007 Plan also include reductions from adopted and
implemented Federal, State and local control measures. ARB Staff
Report, Appendix B.
    EPA believes that the 2007 Plan has demonstrated that the
improvement in PM-10 air quality for the SJVAB is a result of permanent
and enforceable reductions in emissions and the improvement is not a
result of temporary reductions or unusually favorable meteorology. The
fact that, as discussed above, there were no economic downturns,
shutdowns or meteorology impacting air quality and that the number of
exceedance days and the estimated emissions have decreased over time
while the population and vehicle miles traveled in the SJVAB have
increased shows that the improvement in air quality can reasonably be
attributed to the adoption of air quality plans and regulations during
this time.

D. The State Has Met All Applicable Requirements for the Area Under
Section 110 and Part D of the CAA

    The Calcagni memo states that a state must meet those requirements
of section 110 and part D of the CAA that were applicable prior to the
submittal of the redesignation request. CAA section 107(d)(3)(E)(v).
1. Basic SIP Requirements Under CAA Section 110
    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
requirement for Prevention of Significant Deterioration (PSD);
provisions for the implementation of part D requirements for New Source
Review (NSR) permit programs; provisions for air pollution modeling;
and provisions for public and local agency participation in planning
and emission control rule development.
    On numerous occasions over the past 35 years, CARB and the SJVAPCD
have submitted and we have approved provisions addressing the basic CAA
section 110 provisions. There are no outstanding or disapproved
applicable section 110 SIP submittals with respect to the State and the
SJVAPCD.\8\ We propose to conclude that CARB and SJVAPCD have met all
SIP requirements for the SJVAB area applicable for purposes of
redesignation under section 110 of the CAA (General SIP Requirements).
---------------------------------------------------------------------------

    \8\ The applicable California SIP for the SJV nonattainment area
can be found at: http://yosemite.epa.gov/r9/r9sips.nsf/
Casips?readform&count=100&state=California.
---------------------------------------------------------------------------

    Moreover, we note that SIPs must be fully approved only with
respect to applicable requirements for purposes of redesignation in
accordance with CAA section 107(d)(3)(E)(ii). Thus, for example, CAA
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. 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 not believe that these requirements should be construed
to be 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

[[Page 22313]]

redesignation. The State will still be subject to these requirements
after the SJVAB area is redesignated. The section 110 and part D
requirements, which are linked to 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 the conformity SIP requirement for
redesignations. See Reading, Pennsylvania proposed and final
rulemakings at 61 FR 53174-53176 (October 10, 1996), 62 FR 24816 (May
7, 1997); Cleveland-Akron-Lorain, Ohio final rulemaking at 61 FR 20458
(May 7, 1996); and Tampa, Florida final rulemaking at 60 FR 62748
(December 7, 1995). See also the discussion of this issue in the
Cincinnati redesignation at 65 FR 37890 (June 19, 2000), and in the
Pittsburgh redesignation at 66 FR 50399 (October 19, 2001). EPA
believes that section 110 elements not linked to the area's
nonattainment status are not applicable for purposes of redesignation.
2. SIP Requirements Under Part D
    Subparts 1 and 4 of part D, title 1 of the CAA contain air quality
planning requirements for PM-10 nonattainment areas. Subpart 1 of part
D contains general requirements for areas designated as nonattainment.
Subpart 4 of part D contains specific planning and scheduling
requirements for particulate matter nonattainment areas. Subpart 4 of
part D, section 189(a), (b) and (c) requirements apply to moderate and
serious PM-10 nonattainment areas and 189(d) applies to areas which
failed to attain by their serious area deadline. These requirements
include: (1) An approved permit program for construction of new and
modified major stationary sources; (2) provisions to ensure that
reasonably available control technology (RACT) and reasonably available
control measures (RACM) are implemented; (3) provisions to ensure that
best available control measures (BACM) are implemented; (4)
quantitative milestones to be achieved every 3 years and which
demonstrate reasonable further progress (RFP) toward attainment by the
applicable attainment date; (5) provisions to ensure that the control
requirements applicable to major stationary sources of PM-10 also apply
to major stationary sources of PM-10 precursors except where the
Administrator determined that such sources do not contribute
significantly to PM-10 levels which exceed the NAAQS in the area;
and(6) a demonstration of attainment and an annual PM-10 or PM-10
precursor reduction of not less than five percent from the most recent
emission inventory until attainment.
    In addition to these specific requirements for serious PM-10
nonattainment areas, nonattainment areas must also meet the general
planning requirements in subpart 1, section 172(c). These requirements
include, among other things, provisions for the implementation of RACT,
RFP, emissions inventories, and contingency measures.
    For the SJVAB, EPA determined that these requirements were met in
its approval of the 2003 Plan with the exception of the contingency
measure requirement that was subsequently suspended by the
determination of attainment in accordance with EPA's Clean Data Policy
and the NSR permit program for construction of new and modified major
stationary sources. 69 FR 30006 and 71 FR 63642.
    EPA fully approved SJVAPCD NSR rules 2020 and 2201 on May 17, 2004
(69 FR 27837). Recently we proposed to: (1) Correct aspects of that
approval, and (2) approve revisions to the NSR rules that explicitly
exempt certain small or minor agricultural sources from permitting
requirements. 73 FR 9260 (February 20, 2008). In this proposed
rulemaking, we stated that ``we believe that the adoption of the
proposed revisions in place of the SIP as proposed to be corrected
would not result in any change in emissions, any change in air quality,
or any change in the area's ability to attain or maintain the NAAQS.
Accordingly, we conclude that this SIP revision, if approved, will not
interfere with any applicable requirements for attainment and
reasonable further progress or any other applicable requirement of the
CAA and is approvable under section 110(l).'' 73 FR 9265.
    Although the SJVAPCD NSR program has been approved, and we have
proposed approval of revisions to the rule, we also note that final
approval of the NSR revisions is not a necessary prerequisite to
finalizing our proposed approval of the State's redesignation request.
EPA has determined in past redesignations that a NSR program does not
have to 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 or Areas Requesting
Redesignation to Attainment.'' See the more detailed explanations in
the following redesignation rulemakings: Detroit, MI (60 FR 12467-
12468, March 7, 1996); Cleveland-Akron-Lorrain, OH (61 FR 20458, 20469-
20470, May 7, 1996); Louisville, KY (66 FR 53665, 53669, October 23,
2001); Grand Rapids, MI (61 FR 31831, 31836-31837, June 21, 1996).
    The requirements of the PSD program will apply once the area has
been redesignated. Thus, new major sources with significant PM-10
emissions and major modifications of PM-10 at major sources as defined
under 40 CFR 52.21 will be required to obtain a PSD permit. Currently,
EPA is the PSD permitting authority in the SJVAB under a Federal
implementation plan. See 40 CFR 52.270. However, the SJVAPCD can
implement the Federal PSD program through a delegation agreement with
EPA or, assuming that the SJVAPCD makes necessary modifications to its
PSD rules, under an EPA-approved rule.
    With respect to the conformity requirement, 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 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 a redesignation request
under section 107(d) because state conformity rules are still required
after redesignation and Federal conformity rules apply where state
rules have not been approved. See Wall v. EPA, 265f 3d 426 (6th Cir.
2001), upholding this interpretation. See, also, 60 FR 62748 (December
7, 1995).
    Thus, EPA concludes that the State has met all requirements
applicable under section 110 and part D for the SJVAB for purposes of
redesignation. CAA Section 107(d)(3)(E)(v).

E. EPA Has Fully Approved a Maintenance Plan, Including a Contingency
Plan, for the Area Under Section 175A of the CAA

    Section 175A of the CAA provides the requirements for maintenance
plans. These requirements are further clarified in the Calcagni memo.
The provisions to be included in maintenance plans are:

[[Page 22314]]

    (1) An attainment emissions inventory to identify the level of
emissions in the area sufficient to attain the NAAQS;
    (2) A demonstration of maintenance of the NAAQS for 10 years after
redesignation;
    (3) Verification of continued attainment through operation of an
appropriate air quality monitoring network; and
    (4) Contingency provisions that EPA deems necessary to assure that
the State will promptly correct any violation of the NAAQS that occurs
after redesignation of the area. We discuss how these requirements are
met for the SJVAB below.
1. An Attainment Emissions Inventory To Identify the Level of Emissions
in the Area Sufficient To Attain the NAAQS
    Section 172(c)(3) of the CAA requires all plan submittals to
include a comprehensive, accurate, and current inventory of actual
emissions from all sources in the nonattainment area. In demonstrating
maintenance in accordance with CAA section 175A and the Calcagni memo,
the state should provide an attainment emissions inventory to identify
the level of emissions in the area sufficient to attain the NAAQS.
Where the state has made an adequate demonstration that air quality has
improved as a result of the SIP, the attainment inventory will
generally be an inventory of actual emissions at the time the area
attained the standard. EPA's primary guidance in evaluating these
inventories is the document entitled, ``PM-10 Emissions Inventory
Requirements,'' EPA, OAQPS, EPA-454/R-94-033 (September 1994) which can
be found at: http://www.epa.gov/ttn/chief/eidocs/pm10eir.pdf.
    The 2007 Plan includes detailed emissions inventories for
NOX, directly emitted PM-10, volatile organic compounds
(VOC) and oxides of sulfur (SOX).\9\ The emissions
inventories are projected from a 2002 baseyear inventory because it was
the most comprehensive inventory available. The baseyear inventory
meets the CAA requirement for a comprehensive, accurate and current
inventory and is used as the basis for forecasting future year inventories.
---------------------------------------------------------------------------

    \9\ The 2007 Plan's emissions inventories are found in Appendix
B of the ARB Staff Report. As mentioned above and in the ARB Staff
Report, the State ``* * * updated the attainment inventory * * * to
reflect emission reductions achieved by ARB adopted measures that
had not been accounted for'' before submitting the 2007 Plan to EPA
on November 16, 2007.
---------------------------------------------------------------------------

    The 2007 Plan includes projected inventories for 2005, 2010 and
2020 for NOX, PM-10, VOC and SOX. The baseyear
and projected year inventories all include a detailed breakdown of the
stationary and mobile source emissions categories. The emissions for
each of the categories are estimated based on the best available
information on number of sources, size of sources, growth, control
measures, emissions factors, and other criteria.
    The 2007 Plan selects the 2005 PM-10 and NOX inventories
as the attainment emission inventories because the SJV nonattainment
area first attained the PM-10 standard during 2003-2005 (and continues
to attain the standard through February 2008). 2007 Plan, pp. 5-6. The
2007 Plan also includes inventories for VOC and SOx; however, EPA has
determined that NOX is the only significant PM-10 precursor
for the SJV nonattainment area and thus the proposed SJVAB. 69 FR 30006.
Table 3 summarizes the 2007 Plan's NOX and PM-10 emissions.

        Table 3.--Annual PM-10 and NOX Emissions (Tons Per Day) 2007 Plan (ARB Staff Report, Appendix B)
----------------------------------------------------------------------------------------------------------------
                                                                       2005            2010            2020
----------------------------------------------------------------------------------------------------------------
PM-10...........................................................             284             282             290
NOX.............................................................             606             521             328
----------------------------------------------------------------------------------------------------------------

    The NOX emission inventory continues to be reduced
substantially in the future. While the PM-10 emission inventory is
projected to increase slightly in 2020, we believe the increase is
insignificant when compared to the substantial NOX
decreases. See 2007 Plan, pp. 5-6 and Appendix B of the ARB Staff Report.
    EPA believes that the selection of 2005 for the attainment year
inventory and 2020 for the maintenance year inventory is appropriate
since the SJVAB was determined to have attained the PM-10 NAAQS in
2005. We have reviewed the 2007 Plan's attainment year and maintenance
year emissions inventories and determined that they are accurate and
comprehensive and meet the requirements of EPA guidance and the CAA.
2. A Demonstration of Maintenance of the NAAQS for 10 Years After
Redesignation
    Section 175A of the CAA requires a demonstration of maintenance of
the NAAQS for 10 years after designation. A state may generally
demonstrate maintenance of the NAAQS by either showing that future
emissions of a pollutant or its precursors will not exceed the level of
the attainment inventory, or by modeling to show that the future
anticipated mix of sources and emission rates will not cause a
violation of the NAAQS. Under the Act, the showing should be based on
the same level of modeling used for the attainment demonstration
required as part of the approved attainment plan.
    Consistent with EPA's modeling guidance (The Guideline on Air
Quality Models (GAQM), 40 CFR part 51, Appendix W and the PM-10 SIP
Development Guideline (PMSDG), EPA 450/2-86-001, June 1987), the 2003
Plan's attainment demonstration was based on the use of two receptor
models: Chemical Mass Balance (CMB) and rollback. 69 FR 5412, 5424-5425
and 69 FR 30006. The 2007 Plan also uses CMB and rollback to
demonstrate maintenance of the 24-hour PM-10 standard until 2020.\10\
See 2007 Plan, pp. 6-11. The results of the modeling show that all
monitoring sites in the SJVAB nonattainment area will be below the
NAAQS in 2020, with the highest projected value of 134 μg/m\3\ at
Bakersfield-Golden and Corcoran. See 2007 Plan, Table 2.
---------------------------------------------------------------------------

    \10\ The 2007 Plan also includes a maintenance demonstration for
the annual PM-10 standard; however, the annual PM-10 standard was
revoked effective December 18, 2006. 71 FR 61144 (October 17, 2006).
Therefore we do not address this demonstration here.
---------------------------------------------------------------------------

    In addition to the modeling for the maintenance plan, the 2007 Plan
shows that total annual emissions of NOX will decrease from
606 tpd in 2005 to 521 tpd in 2010 and 328 tpd in 2020 and total annual
emissions of PM-10 will decrease from 284 tpd in 2005 to 282 tpd in
2010 and slightly increase to 290 tpd in 2020. As discussed above, the
emissions inventories meet EPA

[[Page 22315]]

requirements and the general decline in inventories provides assurance
that the SJVAB will maintain its attainment levels through 2020.
    Based on our review of the information presented in the 2007 Plan,
we believe that the State has met EPA requirements for demonstrating
maintenance of the PM-10 standard for the SJVAB.
3. Verification of Continued Attainment Through Operation of an
Appropriate Air Quality Monitoring Network
    In demonstrating maintenance, continued attainment of the NAAQS can
be verified through operation of an appropriate air quality monitoring
network. The Calcagni memo states that the maintenance plan should
contain provisions for continued operation of air quality monitors that
will provide such verification. The memo also states that states should
ensure that they have the legal authority to implement and enforce all
measures necessary to attain and to maintain the NAAQS. Finally, the
memo states that the state submittal should indicate how it will track
the progress of the maintenance plan (e.g., with periodic emissions
inventory updates or modeling input updates) and monitor the triggers
for contingency measures.
    In the 2007 Plan the SJVAPCD commits to continued operation of its
air quality monitoring network for verification of attainment. See 2007
Plan, pp. 12-13. The SJVAPCD's authority to continue operating after
redesignation to attainment is provided for in the California Health
and Safety Code sections 40150 and 40161. Id. at 15. The SJVAPCD also
plans to verify continued attainment of the PM-10 standard through an
annual report to its Board which will include, among other things,
tracking of adoption and implementation of control measures, tracking
of air quality data and comparison of predicted versus current
emissions reductions estimates. Id. As discussed further below, since
the SJVAPCD has selected a contingency measure trigger that is based on
ambient air quality levels, the continued operation of the monitoring
network and tracking of its data will provide adequate notice of when
contingency measures are needed.
4. Contingency Provisions to Promptly Correct Any Violation of the
NAAQS That Occurs After Redesignation of the Area
    Contingency provisions are required under section 175A of the CAA.
These contingency measures are distinguished from those generally
required for nonattainment areas under section 172(c)(9) in that they
are not required to be fully adopted measures that will take effect
without further action by the State in order for the maintenance plan
to be approved. The Calcagni memo states that the contingency
provisions of the maintenance plan should clearly identify the measures
to be adopted, a schedule and procedure for adoption and
implementation, and a specific time limit for action by the state. The
memo also states that the contingency provisions should identify
indicators or triggers which will be used to determine when the
contingency measures need to be implemented. While the memo suggests
inventory or monitoring indicators, it states that contingency
provisions will be evaluated on a case-by-case basis. Finally, the
Calcagni memo states that the contingency provisions must require the
state to implement all measures contained in the part D nonattainment
plan for the area prior to redesignation.
    The 2007 Plan selects an action level or trigger based on an
exceedance of the PM-10 NAAQS of 155 μg/m\3\.\11\ See 2007 Plan, p.
16. In addition, the District may also consider other factors such as a
succession of values just below but near the level of the PM-10
standard. Id. EPA believes that an exceedance of 155 μg/m\3\ is an
appropriate trigger level. The SJVAB has several continuous PM-10
monitors, and a single measurement of 155 μg/m\3\ at one of these
monitors would not constitute a violation of the PM-10 NAAQS. Even if a
measurement of 155 μg/m\3\ is recorded at a one-in-six day FEM, a
violation is not necessarily being recorded as the State might need to
evaluate the possibility that the measurement is due to an exceptional
event.
---------------------------------------------------------------------------

    \11\ An exceedance is defined as a daily value that is above the
level of the 24-hour standard (150 μg/m\3\) after rounding to the
nearest 10 μg/m\3\ (i.e. values ending in 5 or greater are to be
rounded up). Thus, a recorded value of 154 μg/m\3\ would not be
an exceedance since it would be rounded to 150 μg/m\3\ whereas a
recorded value of 155 μg/m\3\ would be an exceedance since it would be
rounded to 160 μg/m\3\. See 40 CFR part 50, appendix K, section 1.0.
---------------------------------------------------------------------------

    The 2007 Plan states that if the SJVAB monitors an exceedance of
155 μg/m\3\, the District commits to take appropriate action within
18 months of the exceedance date. This action will first involve a
determination of whether the exceedance was due to an exceptional event
in accordance with EPA's Exceptional Events Rule and an analysis of
what caused the exceedance and the necessary controls to address it.
Id. If the exceedance is not due to an exceptional event, the District
commits to determine the possible causes of the exceedance and to
determine if emissions reductions from adopted measures that are not
needed to maintain the PM-10 NAAQS are available to serve as
contingency measures. These measures can be found in the SJVAPCD's 2007
Ozone Plan (April 30, 2007) and the SJVAPCD's Proposed 2008 PM2.5 Plan
(March 13, 2008) and include more stringent controls on open burning,
gas turbines, boilers, glass melting, residential water heaters, wood
burning fireplaces and heaters and commercial charbroiling. See Table
6-1 of SJVAPCD's 2007 Ozone Plan and Table 6-3 of SJVAPCD's Proposed
2008 PM2.5 Plan.
    If there are no reductions available from adopted measures, the
District commits in the 2007 Plan to proceed with identifying control
measures from feasibility studies such as those found in its 2007 Ozone
Plan and Proposed 2008 PM2.5 Plan (see Table 6-2 of 2007 Ozone Plan and
Table 6-5 of Proposed PM2.5 Plan) and prioritize measures most relevant
for reducing PM-10 emissions. 2007 Plan, pp. 16-17. The SJVAPCD has
also provided clarification that if additional control measures are
necessary, the SJVAPCD will adopt and implement the control measures
within the 18-month timeframe for appropriate action. Letter from Seyed
Sadredin, SJVAPCD, to Deborah Jordan, EPA, April 17, 2008.
    Finally, the 2007 Plan states that the State, District and local
governments have adopted and implemented all measures in the 2003 Plan.
2007 Plan, p. 17 and Appendix B.
    Based on the discussion above and EPA's review of the 2007 Plan, we
believe the plan adequately addresses the contingency measure
requirement under section 175A of the CAA.
Conclusion
    Based on our review of the 2007 Plan, and for the reasons discussed
above, we conclude that the CAA section 107(d)(3)(E) requirements for
redesignation to attainment and an approvable maintenance plan for the
SJVAB have been met. We are therefore proposing to approve the 2007
Plan as meeting the requirements of section 175A of the CAA and
proposing to redesignate the SJVAB nonattainment area to attainment for
the PM-10 NAAQS.

F. Transportation Conformity and Motor Vehicle Emissions Budgets

    Under section 176(c) of the CAA, transportation plans, programs and
projects in the nonattainment or maintenance areas that are funded or

[[Page 22316]]

approved under title 23 U.S.C. and the Federal Transit Laws (49 U.S.C.
Chapter 53) must conform to the applicable SIP. In short, a
transportation plan and program are deemed to conform to the applicable
SIP if the emissions resulting from the implementation of that
transportation plan and program are less than or equal to the motor
vehicle emissions budget (MVEB) established in the SIP for the
attainment year, maintenance year and other analysis years. See,
generally, 40 CFR part 93.
    The 2007 Plan provides for attainment year MVEBs for 2005 and
maintenance year MVEBs for 2020.\12\ The 2005 attainment year MVEBs
will replace the current MVEBs for 2008 and 2010 from the 2003 Plan.
See 40 CFR 93.118(a).
---------------------------------------------------------------------------

    \12\ See footnotes 2 and 9 above.
---------------------------------------------------------------------------

    Before an emissions budget in a submitted SIP revision may be used
in a conformity determination, we must first determine that it is
adequate. The criteria by which we determine whether a SIP's motor
vehicle emissions budgets are adequate for transportation conformity
purposes are outlined in 40 CFR 93.118(e)(4). We have described our
process for determining the adequacy of submitted SIP budgets in the
preamble to revisions to EPA's conformity regulations. 69 FR 40004
(July 1, 2004). Applicability of emission trading between conformity
budgets for conformity purposes is described in 40 CFR 93.124(b).
1. CARB Methodology for Estimating PM-10 in the Emissions Budgets
    CARB's mobile source emission model, EMFAC2007, was used to
estimate direct PM-10 and NOX emissions from motor vehicles
in the 2007 Plan. EMFAC2007 was approved by EPA on January 18, 2007 (72
FR 733464), for use in SIPs and transportation conformity analyses.
EMFAC2007 produces emissions for a wide range of motor vehicles
(passenger cars, trucks, motorcycles, buses and motor homes) for
calendar years out to 2040. Particulate emissions include tire and
brake wear as well as vehicle exhaust and evaporative emissions.
    The methodology used in the 2007 Plan to estimate fugitive dust
(e.g., paved and unpaved road emissions) is consistent with the methods
previously approved in EPA's action on the 2003 Plan. 69 FR 30006 and
69 FR 5412, 5414. No further action is required to approve these
methodologies for use in future transportation conformity
determinations in the SJVAB.
2. Adequacy of the 2007 Plan's Budgets
    The 2007 Plan includes county by county subarea motor vehicle
emissions budgets for 2005 and 2020 for direct PM-10 and
NOX. The 2007 Plan budgets are first summarized in Table 6,
``Revised Motor Vehicle Emission Budgets for the Attainment Year, (tons
per average annual day),'' and in Table 7, ``Motor Vehicle Emission
Budgets for Maintenance of PM10 NAAQS, (tons per average annual day),''
of the 2007 Plan; however, these estimates were updated by CARB, based
on updated vehicle activity data, and the updated budgets were included
in the ARB Staff Report (p. 12) as part of the 2007 Plan submittal to
EPA. Thus, the budgets found on page 12 of ARB Staff Report supercede
the budgets in Tables 6 and 7 of the locally adopted 2007 Plan. See
November 16, 2007 submittal letter from James N. Goldstene, CARB, to
Wayne Nastri, EPA, enclosure ``V. Updated transportation conformity
budgets and supporting documentation.'' Table 4 below reflects the
updated and submitted transportation conformity budgets for the 2007
Plan. The direct PM-10 budgets include emissions of re-entrained dust
from motor vehicle travel on paved and unpaved roads, vehicular
exhaust, vehicle brake and tire wear, and emissions from highway and
transit project construction. The emissions budgets for NOX
include only exhaust from on-road vehicles. Since the 2007 Plan does
not consider VOC to be a significant contributor to the PM-10
nonattainment problem, in accordance with 40 CFR 93.102(b)(2)(iii), no
VOC budgets are included. Additional details regarding the budgets are
presented in the 2007 Plan, Appendix D, "Detailed Conformity Calculations."
    Based on our evaluation of the criteria outlined in section
93.118(e)(4) of the conformity rule, EPA proposes to find the PM-10 and
NOX motor vehicle emissions budgets contained in the 2007
Plan (and in Table 4 below) adequate and proposes to approve them. EPA
proposes to approve the budgets because they come from a SIP which EPA
concludes demonstrates timely attainment and maintenance and the
budgets are consistent with all of the control measures assumed in the
attainment demonstration and maintenance plan. We also find adequate
and propose to approve the individual county level subarea budgets for
NOX and PM-10, as shown in Table 4 below, consistent with
section 93.124(d), which allows for a nonattainment area with more than
one Metropolitan Planning Organization (MPO) to establish subarea
emission budgets for each MPO or make a collective conformity
determination for the entire nonattainment area. Note that, if an
individual MPO cannot show conformity to its individual county budget,
then the remaining MPOs in the SJVAB cannot make any new conformity
determinations.\13\ If approved, the 2005 and 2020 motor vehicle
emissions budgets must be used for transportation conformity purposes.
As mentioned earlier, the county subarea motor vehicle emissions
budgets that EPA is proposing to approve are listed in Table 4 below.
---------------------------------------------------------------------------

    \13\ CAA section 176(c) states that conformity applies to SIPs
in nonattainment and maintenance areas, rather than individual
metropolitan planning areas within a single state. When subarea
budgets area created for each MPO, the sum of the subarea budgets
equals the total amount of emissions the area can have from the
transportation sector and still attain and maintain the NAAQS. When
one subarea lapses, then the other MPOs cannot show that their
planned transportation activities would conform to the SIP for the
whole area until the lapse is resolved. See ``Companion Guidance for
the July 1, 2004, Final Transportation Conformity Rule: Conformity
Implementation in Multi-Jurisdictional Nonattainment and Maintenance
Areas for Existing and New Air Quality Standards'' (EPA 420-B-04-012).

               Table 4.--Motor Vehicle Emissions Subarea Budgets (Tons Per Day) 2007 PM-10 Plan *
----------------------------------------------------------------------------------------------------------------
                                                               2005                            2020
                     County                      ---------------------------------------------------------------
                                                       PM-10            NOx            PM-10            NOx
----------------------------------------------------------------------------------------------------------------
Fresno..........................................            13.5            59.2            16.1            23.2
Kern **.........................................            12.1            88.3            14.7            39.5
Kings...........................................             3.1            16.7             3.6             6.8
Madera..........................................             3.6            13.9             4.7             6.5
Merced..........................................             6.2            39.2             6.5            13.9
San Joaquin.....................................             9.1            42.6            10.6            16.7
Stanislaus......................................             5.6            29.7             6.7            10.7

[[Page 22317]]

Tulare..........................................             7.3            25.1             9.3            10.1
                                                 ---------------------------------------------------------------
    Total.......................................            60.5           314.7            72.2          127.4
----------------------------------------------------------------------------------------------------------------
* The budgets are based on attainment and maintenance of the 24-hour PM-10 NAAQS.
** MVEBs in Table 2 are only for the SJVAB portion of Kern County.

3. Trading Mechanism
    Transportation conformity is demonstrated for each county in the
SJVAB when emissions for both PM-10 and NOX are estimated to
be below the motor vehicle emission budgets for each pollutant for all
analysis years. However, for analysis years beyond 2010, in our prior
approval of the 2003 Plan, we approved a trading mechanism that allows
emissions to be traded from NOX to PM-10 budgets. 69 FR 30006 
and 69 FR 5412, 5414.
    The trading mechanism specified that if, after including reductions
from additional measures, the direct PM-10 budget still cannot be met,
an MPO could adjust (i.e., increase) its PM-10 subarea budget by
trading from its NOX budget. This trade from the
NOX subarea budget to the PM-10 subarea budget can only
occur if the estimated emissions of NOX from the planned
transportation network are less than the NOX subarea budget
for a given analysis year. The 1.5 tpd NOX to 1 tpd PM-10
ratio would be used, as follows, to determine the NOX
reductions needed to offset the excess direct PM-10 emissions:

(PM-10 estimate--PM-10 budget) * 1.5 = tpd of NOX reductions
needed to offset excess PM-10

    A subarea has demonstrated conformity if, after trading, the
estimates of NOX and PM-10 emissions from the planned
transportation network are at or below the adjusted NOX and
direct PM-10 budgets. For every analysis year, and in each subsequent
conformity determination, the transportation agency must repeat these
steps to determine whether the budgets can be met, or whether they need
to be adjusted using this trading mechanism.
    The 2007 Plan requests that this trading mechanism remain
unchanged, but available for use after 2005, the revised attainment
year. Since the first analysis year, for conformity purposes, will be
2010, EPA is proposing to continue to approve use of the trading
mechanism for conformity analysis years after 2005. As stated in the
2003 Plan approval (69 FR 5412, 5414-5417; 69 FR 30006), EPA continues
to believe that trading mechanisms cannot be reviewed through the adequacy
process, and instead need full EPA approval before they can be used.

V. Proposed Commitments for East Kern

    In order to address CAA requirements for the East Kern
nonattainment area, the State submitted on February 29, 2008
enforceable commitments to install a FRM/FEM in East Kern and if a
violation is recorded to submit the appropriate SIP. Specifically, the
State submitted a resolution approved by the Governing Board of the
KCAPCD on February 27, 2008 committing to, with assistance from the
State, install a FRM/FEM. Kern County Air Pollution Control Board
Resolution 2008-001-02. Further, the resolution states that the KCAPCD
will develop for submittal through the State to EPA, a serious
nonattainment area SIP that meets the requirements of CAA section 189
in the event of a violation of the PM-10 standard. Id. On March 3,
2008, CARB's Executive Officer issued Executive Order S-08-004
approving as a SIP revision the KCAPCD commitments and committing to
submit a SIP addressing section 189 in the event that the area violates
the PM-10 standard. Given the low concentrations recorded at the
IMPROVE monitor and the relatively minimal expected growth, we believe
this is a reasonable approach for the area.

VI. Proposed Actions

    Based on our review of the State's request, EPA believes the State
has addressed all the necessary requirements for a revised designation
and is proposing to approve the State's request under section
107(d)(3)(D) to revise the designation for the SJV PM-10 nonattainment
area by splitting the area into two separate serious PM-10
nonattainment areas, the SJVAB PM-10 nonattainment area and the East
Kern PM-10 nonattainment area. Also, based on EPA's review of the 2007
Plan submitted by the State, EPA believes that the CAA requirements
under section 107(d)(3)(E) for redesignations and section 175A for
maintenance plans have been met for the SJVAB and EPA is therefore
proposing to redesignate the newly created serious SJVAB nonattainment
area to attainment for the PM-10 NAAQS and to approve the SJVAPCD's PM-
10 maintenance plan, budgets and conformity trading mechanism for the
area. EPA is also proposing to exclude from use in determining that the
SJVAB has attained the PM-10 NAAQS two exceedances that it has
concluded were caused by exceptional events on July 4, 2007 and January
4, 2008. Finally, EPA is proposing to approve commitments from KCAPCD
and CARB to install a FRM/FED in the newly created East Kern serious
PM-10 nonattainment area and to address section 189(d) CAA requirements
for it in the event the FRM/FED records a violation of the PM-10 standard.

VII. 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 FR 28355, May 22, 2001). This
action merely proposes to approve a revised boundary designation, a
redesignation to attainment for the SJVAB, a maintenance plan for the
SJVAB, motor vehicle emissions budgets and conformity trading mechanism
for the area and commitments for East Kern, all of which are either
requested or submitted by the State, and does not impose any additional
requirements. 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 proposed rule does not impose
any additional enforceable duty, it does not contain any unfunded
mandate or significantly or uniquely affect small

[[Page 22318]]

governments, as described in the Unfunded Mandates Reform Act of 1995
(Pub. L. 104-4).
    Executive Order 13175 (59 FR 22951, November 9, 2000) requires EPA
to develop an accountable process to ensure ``meaningful and timely
input by tribal officials in the development of regulatory policies
that have tribal implications.'' Seven Indian tribes have reservations
located within the boundaries of the proposed SJVAB. EPA plans to
consult with representatives of the seven Tribes and will continue to
work with the Tribes, as provided for in Executive Order 13175.
Accordingly, EPA has addressed Executive Order 13175 to the extent that
it applies to this action. This proposed action also does not have
Federalism implications because it does not have substantial direct
effects on the States, on the relationship between the national
government and the States, or on the distribution of power and
responsibilities among the various levels of government, as specified
in Executive Order 13132 (64 FR 43255, August 10, 1999). This proposed
action merely proposes to approve requests or submittals from the State
and does not alter the relationship or the distribution of power and
responsibilities established in the CAA. Executive Order 12898
establishes a Federal policy for incorporating environmental justice
into Federal agency actions by directing agencies to identify and
address, as appropriate, disproportionately high and adverse human
health or environmental effects of their programs, policies, and
activities on minority and low-income populations. Today's action
involves proposed approvals of a revised boundary designation, a
redesignation to attainment for the SJVAB, a maintenance plan for the
SJVAB, motor vehicle emissions budgets and conformity trading mechanism
for the area and commitments for East Kern. It will not have
disproportionately high and adverse effects on any communities in the
area, including minority and low-income communities.
    This proposed rule also is not subject to Executive Order 13045
``Protection of Children from Environmental Health Risks and Safety
Risks'' (62 FR 19885, April 23, 1997), because it is not economically
significant. 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. This proposed rule 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 Parts 52

    Environmental protection, Air pollution control, Incorporation by
reference, Intergovernmental relations, Particulate matter, Reporting
and recordkeeping requirements.

40 CFR Part 81

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

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

     Dated: April 21, 2008.
Laura Yoshii,
Acting Regional Administrator, Region IX.
[FR Doc. E8-9139 Filed 4-24-08; 8:45 am]
BILLING CODE 6560-50-P

 
 


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