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CA ID: [CA258-0442(A); FRL-7645-7]
SUBJECT CATEGORY: Determination of Attainment of the 1-Hour Ozone Standard; Determination Regarding Applicability of Certain Clean Air Act Requirements; Approval and Promulgation of Ozone Attainment Plan; San Francisco Bay Area, CA
DOCUMENT SUMMARY: EPA is determining that the San Francisco Bay Area (Bay Area) ozone nonattainment area has attained the 1hour ozone national ambient air quality standard (NAAQS) by the deadline required by the Clean Air Act (CAA), September 20, 2006. Based on this determination, we are also determining that the CAA's requirements for reasonable further progress and attainment demonstrations and for contingency measures for the 1 hour ozone standard are not applicable to the area for so long as the Bay Area continues to attain the 1hour ozone standard.
In addition, EPA is approving the following elements of the 2001 ozone attainment plan for the Bay Area (2001 Plan): Emissions inventory, reasonably available control measures (RACM); commitments to adopt and implement specific control measures; motor vehicle emissions budgets (MVEBs); and commitments for further study measures.
In 2001, EPA disapproved certain components of the 1999 ozone attainment plan for the Bay Area: The RACM demonstration, the attainment demonstration, and the MVEBs. Because of this disapproval the 2 to 1 offset sanction under CAA section 179(b)(2) was imposed in the Bay Area on April 22, 2003. Based on the proposed approval of these elements of the 2001 Plan, EPA made an interim final determination that resulted in a stay of the offset sanction and deferral of the highway sanction. EPA's approval of RACM and the MVEBs in the 2001 Plan terminates the sanctions clock for those plan elements.
Based on the attainment determination for the Bay Area, elsewhere in this Federal Register EPA is taking interim final action to stay the offset sanction and defer the highway sanction triggered by the attainment demonstration disapproval for as long as the area continues to attain the 1hour ozone standard because that plan requirement has been suspended.
SUMMARY: California,
A. Attainment Finding
B. EPA's Responses to Comments on the Proposed Finding of Attainment
1. Comments Regarding Timing of the Finding of Attainment
2. Comments Regarding the Data on Which the Attainment Finding Is Based
3. Comments Regarding the Impact of an Attainment Finding on the 2001 Plan and on Air Quality in the Bay Area
C. Applicability of Clean Air Act Planning Requirements in Areas Attaining the 1Hour Ozone Standard
D. EPA Responses to Comments on Applicability of Clean Air Act Requirements
1. Comments Regarding EPA's Clean Data Policy
2. Comments Regarding the Applicability of EPA Policies to the Bay Area
E. Effects of the Attainment Finding on the Bay Area and of a Future Violation of the 1Hour Ozone NAAQS
III. Approval of Bay Area 2001 Plan
A. Approval of Bay Area 2001 Plan
B. EPA's Responses to Comments on the Proposed Approval of the 2001 Plan
1. Comments on the Proposed Approval of the Emissions Inventory
2. Comments on the Proposed Approval of RACM
3. Comments on the Proposed Approval of the Control Measure Commitments
4. Comments on the Downwind Transport of Air Pollution
5. Comments on Additional Plan Elements
6. Comments on the Impact of the State Law and Court Orders
7. Comments on the Interim Final Determination
IV. Effect of the Attainment Determination and 2001 Plan Action on Transportation Conformity
V. Statutory and Executive Order Reviews
Upon enactment of the Clean Air Act Amendments of 1990, the Bay Area was classified as a moderate nonattainment area for the 1hour ozone NAAQS. 56 FR 56694 (November 6, 1991). EPA redesignated the Bay Area to attainment in 1995, based on then current air quality data (60 FR 27029, May 22, 1995), and subsequently redesignated the area back to nonattainment without classification on July 10, 1998 (63 FR 37258), following renewed violations of the 1hour ozone standard. Upon the Bay Area's redesignation to nonattainment, we required the State to submit a state implementation plan (SIP) addressing applicable CAA provisions, including a demonstration of attainment as expeditiously as practicable but no later than November 15, 2000.
The Bay Area Air Quality Management District (District or BAAQMD),
along with its colead agenciesthe Metropolitan Transportation Commission and the
[[Page 21718]]
Association of Bay Area Governmentsprepared a 1hour ozone attainment
plan, which was submitted to EPA by the California Air Resources Board
(CARB) on August 13, 1999. On September 20, 2001 (66 FR 48340), we
approved the emissions inventories, reasonable further progress (RFP)
provisions, control measure commitments, and contingency measures in
that plan. In the same rulemaking, we disapproved the remaining
portions of the SIP, i.e., the attainment demonstration, MVEB, and RACM
demonstration, issued a finding that the area failed to attain by the
applicable deadline, and set a new attainment deadline of as
expeditiously as practicable but no later than September 20, 2006. The
effective date of the final disapproval (October 22, 2001) started an
18month clock for the imposition of sanctions pursuant to CAA section
179(a) and 40 CFR 52.31, and a 2year clock for EPA to promulgate a
federal implementation plan (FIP) under CAA section 110(c)(1). 62 FR
43796 (August 15, 1997). The Bay Area became subject to the 2 to 1
offset sanction under CAA section 179(b)(2) on April 22, 2003.
On November 30, 2001, CARB submitted the 2001 Plan for the Bay Area addressing the new attainment deadline. On February 14, 2002, we found the MVEBs in the 2001 Plan adequate. 67 FR 8017 (February 21, 2002). On July 16, 2003 (68 FR 42174), we proposed to approve the following elements of the 2001 Plan: Emissions inventory, RACM demonstration, attainment assessment, MVEBs, and commitments to adopt control measures and to adopt and submit a plan revision by April 15, 2004 based on new modeling. On the same date, we issued an interim final determination that the 2001 Plan corrects the deficiencies in the 1999 Plan, thereby staying the CAA section 179 offset sanction and deferring the imposition of the highway sanction triggered by our September 20, 2001 disapproval. 68 FR 42172.
On October 31, 2003 (68 FR 62041), we proposed to find that the San Francisco Bay Area ozone nonattainment area had attained the 1hour ozone standard by its CAA mandated attainment date of September 20, 2006. Based on this proposed finding, we also proposed to suspend the attainment demonstration, RFP and contingency measure requirements of the CAA for the Bay Area for so long as the area continues to attain the 1hour ozone standard.
On January 30, 2004, CARB withdrew the attainment assessment, the
RFP demonstration, the contingency measures, and the technical
correction to the attainment assessment (Appendix F) in the 2001 Plan
from EPA's consideration as revisions to the Bay Area SIP.\1\ In the
same letter, the State also specifically requested that EPA approve the motor vehicle emissions budgets in the 2001 Plan.
\1\ See January 30, 2004 letter from Catherine Witherspoon,
Executive Officer, CARB, to Wayne Nastri, Regional Administrator,
U.S. EPA Region 9. This letter is subsequently referred to as the 1/ 30/04 Witherspoon letter.
II. Attainment Finding for the Bay Area
In this action, EPA is finalizing its proposed finding of attainment for the Bay Area. The 1hour ozone NAAQS is 0.12 parts per million (ppm) not to be exceeded on average more than one day per year over any threeyear period. 40 CFR 50.9 and appendix H. We determine if an area has attained the 1hour standard by calculating, at each monitor, the average number of days over the standard per year during the preceding threeyear period.\2\ We use all available, quality assured monitoring data and we generally base our determination of attainment or failure to attain on the area's design value as of its applicable attainment deadline. In this case, the attainment deadline (September 20, 2006) has not been reached, so we are making our attainment finding based on the Bay Area's current air quality data and design value, which demonstrate attainment of the 1hour standard. See section II.E. for a discussion of consequences of future violations. \2\ See generally 57 FR 13506 (April 16, 1992) and Memorandum from D. Kent Berry, Acting Director, Air Quality Management Division, EPA, to Regional Air Office Directors; ``Procedures for Processing Bump Ups and Extensions for Marginal Ozone Nonattainment Areas,'' February 3, 1994 (Berry memorandum). While explicitly applicable only to marginal areas, the general procedures for evaluating attainment in this memorandum apply regardless of the initial classification of an area because all findings of attainment are made pursuant to the same procedures.
The design value for the Bay Area for 20012003 was 0.123 ppm, which is below the 0.12 ppm standard using the applicable rounding convention discussed below. No monitor in the Bay Area recorded an average of more than one exceedance of the 1hour ozone standard per year during the 2001 to 2003 period. Documentation of the monitoring data and design value calculation can be found in the docket for this rulemaking.
Our October 31, 2003 proposed attainment finding was based on all
available air quality data collected from the monitoring network, which
we determined met our regulations for state air quality monitoring
networks. On November 12, 2003, the District submitted an interim
certification that the data had been quality assured.\3\ On December 1,
2003, Jack Broadbent, Executive Officer/Air Pollution Control Officer,
BAAQMD, sent a letter to Deborah Jordan, EPA, (12/1/03 Broadbent
letter) transmitting the District's formal certification in accordance
with 40 CFR part 58 that the ozone ambient air monitoring data
submitted to EPA are complete and accurate. The quality assurance process did not result in any changes to the data.
\3\ See November 12, 2003 email from Mark Stoelting, BAAQMD, to
Catherine Brown, EPA, and Catherine Brown's November 21, 2003 response.
Because the Bay Area's design value was below the 0.12 ppm 1hour ozone standard and the area averaged one or fewer exceedances per year at each monitor for the 2001 to 2003 period, we find that the Bay Area attained the 1hour ozone standard by its CAA mandated attainment deadline of September 20, 2006. Based on this final attainment determination, we are also determining that the CAA requirements for RFP, an attainment demonstration and contingency measures for the 1 hour ozone standard are not applicable to the Bay Area for so long as the area continues to attain the standard. For a discussion of EPA's policy and legal basis for suspending these requirements, see our proposed attainment determination at 68 FR 62044.
Finally, based on our final attainment determination, elsewhere in
this Federal Register, we are taking interim final action to stay the
offset sanction and defer the highway sanction for the attainment
demonstration because that plan requirement has been suspended. The
stay/deferral will remain in effect for as long as the area continues to attain the 1hour ozone standard.
B. EPA's Responses to Comments on the Proposed Finding of Attainment
EPA's proposed action provided a 30day public comment period. During this period, we received comments from seven parties. We summarize the most significant comments and provide our responses below; the entire set of comments and responses can be found in the docket in a separate Response to Comment document (RTC).
Comment 1: Several commenters expressed support for a determination that the Bay Area has attained the 1
[[Page 21719]]
hour ozone standard. Another commenter concurred with the determination
that Bay Area's monitoring network meets or exceeds EPA's specified
requirements. In contrast, other commenters pointed to the Bay Area's
prior history of slipping back out of attainment following EPA action
redesignating the area to attainment in 1995 and recent yeartoyear
differences in design values as a reason for exercising caution in
making an attainment finding. One commenter stated that, in light of
the small margin of attainment, EPA should scrutinize the foundation for the asserted finding of attainment.
Response: A determination that an area has attained the standard is based on an objective review of air quality data. The 1hour ozone NAAQS is 0.12 ppm, not to be exceeded on average more than one day per year over any three year period. A review of the data from the prior three years (20012003) indicates that the Bay Area has met this standard. 68 FR 6204262043.
The redesignation of an area to attainment under CAA section 107(d)(3)(E) is a separate process from a finding of attainment. Unlike an attainment finding where we need only determine that the area has had the prerequisite number of clean years, a redesignation requires multiple determinations. Under section 107(d)(3)(E) these
1. We must determine, at the time of the redesignation, that the area has attained the relevant NAAQS.
2. The state must have a fully approved SIP for the area.
3. We must determine that the improvements in air quality are due to permanent and enforceable reductions in emissions resulting from implementation of the SIP and applicable federal regulations and other permanent and enforceable reductions.
4. We must have fully approved a maintenance plan for the area under section 175A.
5. The state must have met all the nonattainment area requirements applicable to the area.
2. Comments Regarding the Data on Which the Attainment Finding is Based
Comment 2: The data do not support a finding of attainment. The District previously reported two separate exceedances on July 10, 2002, of 160 parts per billion (ppb) and 151 ppb, respectively, and stated that EPA should recognize the July 10, 2002 reading of 151 ppb at 4 p.m. as a separate exceedance from the 160 parts per billion (ppb) exceedance from earlier that day. As of December 1, 2003, the District's website stated that the region experienced three violations of the 1hour ozone NAAQS at Livermore in 2002.
Response: An area's ozone attainment status is determined by calculating the average number of days over a threeyear period on which it exceeds the ozone standard. See 40 CFR 50.9(a) and 40 CFR part 50, Appendix H. Therefore, multiple hourly exceedances on any single day count as only one exceedance. The Bay Area's website apparently mistakenly counted a reading of 0.123 ppm at Livermore on August 9, 2002 as an exceedance of the 1hour ozone NAAQS. As explained at length in the proposed finding of attainment (68 FR 62043, October 31, 2003), and discussed below (see response to comment 6), rounding conventions and the form of the standard dictate that values between 0.120 and 0.124, inclusive, are to be rounded to 0.12 parts per million.
Comment 3: According to EPA guidance, an attainment finding should
be based on certified data, however, the proposal was published before
the data were certified. EPA's guidance demands quality assured data
from states to establish evidence of attainment. The EPA memorandum
``Procedures for Processing Requests to Redesignate Areas to
Attainment'' signed by John Calcagni, Director Air Quality Management
Division, OAQPS, dated September 4, 1992 (9/4/92 Calcagni memo)\4\
states that ``[t]he data should be collected and qualityassured in
accordance with 40 CFR 58 and recorded in the Aerometric Information
Retrieval System (AIRS) in order for it to be available for the public
to review.'' EPA has cited this memo as applicable authority for the
proposed rulemaking, and cannot pick and choose portions as applicable
and inapplicable without explanation. The Administrative Procedure Act
(APA) and CAA direct that EPA's decisionmaking must be based on data
and information in the record and available to the public, and the law
of the Ninth Circuit clearly requires that when EPA acts on SIPs, it
must comply with its own rules. Delaney v. EPA, 898 F.2d 687, 693 (9th
Cir. 1990). The data and information purportedly supporting the
proposed action are simply unavailable, or were unavailable during the comment period.
\4\ This memo is available online at http://www.epa.gov/ttn/naaqs/ozone/ozonetech/940904.pdf .
Response: Air quality data are available to EPA and the general
public on a realtime basis from the District's website. EPA based its
proposal on this publicly available monitoring data that indicated the
Bay Area had attained the 1hour ozone standard. While the data for
2003 had not yet been quality assured at the time of the proposal, the
District maintains a monitoring network that meets or exceeds all
applicable requirements. See 68 FR 6204262043 and ``System Audit of
the Ambient Monitoring Program of Bay Area Air Quality Management
District,'' available online at http://www.epa.gov/region09/air/sfbayoz/tsd1003.pdf. EPA had no reason to believe the quality assurance
process would indicate there had been problems with the data and so proceeded with the proposed finding.
On November 12, 2003, the District notified EPA that it had qualityassured the data from the 2003 ozone season and submitted it to AIRS. See footnote 3. Thus the qualityassured data were accessible to the public on that date, i.e., during the public comment period. The November 12, 2003 notification was followed by the 12/1/03 Broadbent letter, which confirmed that the data had been collected and quality assured in conformance with 40 CFR part 58. The quality assurance process did not result in any changes to the data. While the proposal was published shortly before the data were certified, this final rulemaking is based on data that were collected and quality assured in conformance with EPA regulations.
Comment 4: Improved air quality in the Bay Area is not the product of real, permanent, surplus, and enforceable emissions reductions, as required by the CAA and EPA policy and guidance. It came as a result of a significant economic downturn that reduced, temporarily, emissions from all sectors of the emissions inventory and the weather had not been particularly ozone conducive. Because recent Bay Area ozone levels result from a combination of temporarily favorable economic and meteorological conditions rather than documentation of the effectiveness of permanent and enforceable measures, an attainment finding is inappropriate and obligations for RFP, attainment demonstration and contingency measure should not be suspended in the Bay Area.
Response: The requirement to determine that clean air is the result of permanent and enforceable emissions reductions is a criterion for the redesignation of an area to attainment under CAA section 107(d)(3)(E). It need not be met for a finding of attainment or for the suspension of the associated RFP, attainment demonstration, and contingency measure requirements.
That aside, we believe that the finding of attainment itself addresses in part the
[[Page 21720]]
concern about unusually favorable meteorological conditions. We have
long recognized that meteorological conditions have a profound effect
on ambient ozone concentrations. In setting the current 1hour ozone
standard in 1979, we changed the form of the standard, i.e., the
criterion for determining attainment, from a deterministic form ``no
more than once per year'' to a statistical form ``when the expected
number of days per year is less than or equal to one'' over a three
year period in order to properly account for the random nature of
meteorological variations. The threeyear period for averaging the
expected number of exceedances was a reasoned balance between evening
out meteorological effects and properly addressing real changes in
emission levels. See the proposed and final actions promulgating the
current 1hour ozone standard at 43 FR 26962, 26968 (June 22, 1978) and 44 FR 8202, 8218 (February 8, 1979).
Comment 5: Even if EPA has the discretion to dismiss SIP requirements upon a finding of attainment, it would be an abuse of discretion to dismiss these requirements without a finding that the reductions are permanent and enforceable in the circumstances of the Bay Area's recession and weather conditions. Given the narrow margin of attainment, it is inappropriate to relax the SIP through elimination of the RFP, attainment demonstration, and contingency measures requirements.
Response: As noted above, EPA is not dismissing or eliminating these requirements. Rather, we interpret the requirements for an attainment demonstration, an RFP demonstration and contingency measures as inapplicable to an area that has attained the standard, but only for so long as the area remains in attainment. The requirements will again apply if such an area violates the standard. In order to be redesignated to attainment of the ozone standard, the State will be required to demonstrate, among other things, that the reductions contributing to the attainment record are permanent and enforceable, and that atypical weather conditions were not responsible for the improvement in air quality. CAA section 107(d)(3)(E)(iii).
Comment 6: EPA's methodology for rounding off conflicts with Congress's intent that 0.12 ppm should be read as 0.120 ppm, as evidenced by section 181 of the CAA, at Table 1. See also 40 CFR 50.9, which states that the equivalent unit for the standard is 235 ug/m\3\. (Livermore's design value is 245 ug/m\3\). Finally, the specific regulation for the ozone standard contains no provision for rounding off, unlike the regulation for CO. (Compare 40 CFR 50.9 with 40 CFR 50.8(d)).
Response: In our proposed finding of attainment, we explained that
the 1hour ozone NAAQS is 0.12 partspermillion; it is not expressed
in partsperbillion, nor does it contain three digits.\5\ Because air
quality monitors and models express results in three digits, EPA
applies the established rounding convention to determine whether the
measurements meet or exceed the standard. Under the rounding
convention, 0.005 rounds upward and 0.004 rounds downward, so that a
0.124 parts per billion (ppb) ozone level meets the NAAQS of 0.12 ppm,
while a 0.125 parts per billion (ppb) ozone level rounds up to 0.13 ppm
and thus exceeds the NAAQS. The use of rounding neither changes the NAAQS nor relaxes it.
\5\ See 40 CFR 50.9(a) and footnote 8 of the October 31, 2003
proposal (68 FR 62043). Also see ``Guideline for the Interpretation
of Ozone Air Quality Standards.'' U.S. Environmental Protection
Agency, Office of Air, Noise and Radiation, Office of Air Quality
Planning and Standards, Research Triangle Park, North Carolina
27711, January 1979, EPA450/479003, OAQPS No. 1.2108. In the
1979 guidance document, EPA states, ``[i]t should be noted that the
stated level of the standard is taken as defining the number of
significant figures to be used in comparisons with the standard. For
example, a standard level of .12 ppm means that measurements are to
be rounded to two decimal places (.005 rounds up), and, therefore,
.125 ppm is the smallest concentration value in excess of the level
of the standard.'' This document is available on line at http://www.epa.gov/ttn/naaqs/ozone/ozonetech/guideo3.htm .
The commenter's reliance on the design values set forth in Table 1 of section 181(a)(1) is misplaced. These design values are used to classify nonattainment areas, not to determine whether an area has attained the standard. See American Trucking Associations, Inc. v. EPA, 175 F.3d 1027, 1047 (D.C. Cir. 1999) (``* * * although the numbers in the classification table are based upon the 0.12 ppm ozone NAAQS, they are neither equivalent to nor a codification of the NAAQS.'').
EPA's procedure for calculating the design value for classification
purposes is different from the analysis used for purposes of
determining attainment. Under EPA's classification procedures, it is
possible for an area that lacks a full set of monitoring data to be
designated nonattainment and to have a design value of less than 0.125
parts per billion (ppb). Under these circumstances, the area would be
classified as a marginal nonattainment area. See Memorandum from
William G. Laxton dated June 18, 1990, ``Ozone and Carbon Monoxide
Design Value Calculations'' (Laxton Memo), available at http://www.epa.gov.ttn/naaqs/ozone/ozonetech/laxton.htm. The procedures set
forth in the Laxton Memo constitute the ``interpretation methodology
issued by the Administrator most recently before November 15, 1990.''
Finally, the translation of the standard from ppm to ug/m3 is provided
for informational purposes only and does not constitute an alternative form of the standard.
3. Comments Regarding the Impact of an Attainment Finding on the 2001 Plan and on Air Quality in the Bay Area
Comment 7: EPA should direct the District to include in the next SIP submittal a safety margin of additional emissions reductions to compensate for the narrow margin of attainment. EPA should also mandate that the 2004 SIP contain sufficient contingency measures to achieve emissions reductions totaling 3% of the emissions inventory should the region experience a subsequent violation. See ``General Preamble for the Interpretation of Title I of the Clean Air Act Amendments of 1990'' (General Preamble), 57 FR 1351011, April 16, 1992. EPA should institute extraordinary measures to respond immediately in the event of a future violation. The Bay Area's design value, which is just 2 parts per billion (ppb) below the attainment level, indicates that contingency measures must be included in the upcoming SIP. Only the requirement of federally enforceable contingency measures can provide any reasonable assurance that air pollution control efforts and emissions reductions will continue aggressively in the likely event that the area subsequently exceeds the 1hour ozone standard once again. EPA should change course and take final action on the 2001 SIP as submitted and require appropriate emissions inventory adjustments to incorporate the effect of episodic control measures and reduced emissions activity from the economic recession experienced during modeled episode days.
Response: As noted above, our determination that the Bay Area has
attained the standard is based on an objective review of air quality
data. No information has been presented that casts doubt on the
accuracy of the data, therefore we are proceeding with our finding of
attainment. Our guidance provides for the suspension of the attainment
demonstration, RFP and contingency measure requirements applicable to
the Bay Area upon such a finding.\6\ In our proposed action on the [[Page 21721]]
2001 plan, we proposed to approve as part of the attainment assessment
the commitment by CARB and the colead agencies to submit a SIP
revision by April 15, 2004 (68 FR 42181, July 16, 2003). Consistent
with the suspension of the attainment demonstration requirement, the
State has withdrawn the commitment in the 2001 plan to submit a 2004
SIP revision from EPA consideration.\7\ Therefore EPA cannot act on
this commitment and, as a result, there is currently no federally enforceable requirement for a 2004 SIP.
\6\ Memorandum from John S. Seitz, Director, OAQPS, EPA, to
Regional Air Directors, entitled ``Reasonable Further Progress,
Attainment Demonstrations, and Related Requirements for Ozone
Nonattainment Areas Meeting the Ozone National Ambient Air Quality
Standard,'' May 10, 1995 (http://www.epa.gov/ttn/oarpg/t1/memoranda/clean15.pdf ). This memo is subsequently referred to as the ``Clean
Data Policy'' or the ``Seitz memo.''
The colead agencies have, however, expressed their intent to shift
their focus to developing a maintenance plan to support a redesignation
request if EPA finalizes its finding of attainment. Should the Bay Area
violate the 1hour standard prior to redesignation, the attainment
demonstration, RFP and contingency measure requirements will be once
again imposed. Also note that, among other things, an approvable
maintenance plan must include contingency measures that are designed to
promptly address a violation of the standard. Finally, even without the
adoption of additional measures, ozone precursor emissions in the Bay
Area will continue to decline as a result of previously adopted state,
local, and federal measures. Between 2003 and 2006, emissions of oxides
of nitrogen (NO
Comment 8: While EPA's Notice of Proposed Rulemaking on the determination of attainment specified three SIP elements that ``no longer apply to the Bay Area'' EPA did not elect to change or withdraw the District's outstanding enforceable commitment to secure 26 tpd of additional VOC emissions reductions. In light of the data indicating attainment, there could be some question whether all of the enforceable commitments remain valid, but EPA did not in the Notice of Proposed Rulemaking, authorize the rescission of the commitment to achieve an additional 26 tpd of reductions. Given the restatement of commitment by State and local agencies and EPA's failure to specify which, if any of the State's prior ``enforceable commitments'' should not be included in the 2004 midcourse review, the District must completely fulfill its ``enforceable commitments'' as pledged as part of the 2001 SIP submittal package. EPA has endorsed this concept in the proposed 8hr implementation policy. Other commenters stated that EPA should expressly determine that the 26 tpd reduction is no longer necessary for the Bay Area to reach attainment.
Response: In our proposed finding of attainment, we discussed the
CAA requirements that would be suspended should we finalize the
proposal. 68 FR 62044. Those requirements are the RFP, the attainment
demonstration, and contingency measure requirements. The suspension of
these requirements, and our rationale supporting it, apply so long as
the area continues to attain the 1hour ozone NAAQS. Consistent with
the suspension of the attainment demonstration requirement, the State
has withdrawn the attainment assessment in the 2001 Plan, which
includes the associated commitments to undertake a midcourse review
and to achieve additional reductions as necessary to attain the 1hour
ozone standard. See 1/30/04 Witherspoon letter. A midcourse review,
the purpose of which is to evaluate progress toward attainment, and a
commitment to adopt the measures necessary to attain the standard are
unnecessary in an area that has attained the standard. Finally we note
that our final implementation guidance for the 8hour standard has not yet been issued.\8\
\8\ On June 2, 2003, EPA published in the Federal Register a
proposed rule to implement the 8hour ozone NAAQS. 68 FR 32803.
Comment 9: A loss of progress could occur as a result of a finding of attainment. The proposed finding of attainment provides an incentive for areas to defer SIP preparation in hopes that they might achieve clean data before the deadline to perform a deferred SIP element preparation arrives. Part of the State's rationale for employing the midcourse review was the absence of competent modeling to demonstrate attainment in the Bay Area. EPA's proposed action undermines the State's prior commitment to use the more technically robust CCOS \9\ model and more recent data to both model attainment in the Bay Area and quantify the effect of Bay Area emissions upon downwind district attainment. As the District has finally developed a model through the CCOS process, EPA must insist on the completion of the modeling exercise in the 2004 midcourse review SIP to identify issues associated with the federal 1hour ozone standard, the state ozone standard, the 8 hour federal ozone standard, and transport issues. \9\ In an effort to establish a more reliable database for ozone analysis, the Central California Ozone Study (CCOS), a large field measurement program, was conducted in the summer of 2000.
Response: We disagree with the commenter's assessment of the impact
of the attainment finding. The State and the colead agencies have all
acknowledged the need to address the state ozone standard, the federal
8hour standard, and downwind transport of air pollution and have
pledged to continue their efforts.\10\ Despite the commenters'
concerns, work on the CCOS modeling does not appear to have slackened.
In fact, given the technical challenges, EPA is satisfied that work is
progressing as quickly as could be expected. Should the Bay Area once
again violate the standard, new modeling based on CCOS data would be
available to support an attainment demonstration. In addition, much of
the work being done to prepare a maintenance plan and to prepare the
state clean air plan will be transferrable to the nonattainment requirements that would once again apply.
\10\ In the District's October 16, 2003 letter to Catherine
Witherspoon, CARB (10/16/03 Norton letter), Executive Officer
William Norton states that the District ``want[s] to reduce local
ozone and transport, and to maintain progress toward the state
standard.'' In a January 16, 2004 letter to Catherine Witherspoon,
CARB (1/16/04 colead agencies letter), the directors of the colead
agencies recognize that they ``have a continuing obligation to
reduce emissions further in order to attain and maintain all
national ambient air quality standards and to make expeditious
progress toward California standards.'' They state their commitment
to ``continuing [their] ozone control program in order to reduce
ozone levels in the Bay Area and to address transport to downwind
regions.'' In closing, they acknowledge the ``need to make progress
toward the California 1hour standard, address transport to downwind
regions, and meet the national 8hour ozone standard.'' In the 1/30/
04 Witherspoon letter, the State recognizes ``the importance of a
continuing commitment to further emission reductions that will * * * contribute to better air quality in downwind areas.''
Comment 10: The steps and delays that are embedded in EPA's
proposed approach in the event of a future exceedance verify that EPA's
future actions will be ineffective at bringing the region back onto the
path of true attainment. EPA should make a commitment in its final
notice to act immediately upon the observance of a single Livermore
violation because, even if the EPA were to move swiftly, it could take
three years to get a new attainment plan in place (6 months for
rulemaking, 12 months for plan submittal, 18 months to act). Commenters
fear that EPA will wait until the end of the ozone season, then [[Page 21722]]
await quality assured data, which would add 12 months to the process.
Commenters request that EPA specify the protocol for making a
determination of a violation in the event of an exceedance [at Livermore] in July, 2004.
Response: As described in the proposed rule, should the Bay Area violate the 1hour standard prior to EPA redesignating the area to attainment, we will notify the State that we have determined that the area is no longer attaining the 1hour standard. We will also provide notice to the public in the Federal Register and will at that time indicate what pertinent SIP provisions apply and when a SIP revision addressing those provisions must be submitted. The public will have an opportunity to comment on our determinations. In the event of an exceedance, EPA will work closely with the District to facilitate prompt quality assurance of the data. We also note we would not be precluded from initiating the above process in advance of submittal of quality assured data. In setting the due date for submittal of the SIP revisions, EPA will consider all the relevant circumstances. For example, should the Bay Area violate the 1hour standard, EPA will take into account the history of the area and the date on which the Bay Area violates the 1hour standard.
Comment 11: The CAA states that an area shall be classified as nonattainment if the area contributes to ambient air quality in a nearby area that does not meet the federal standard (CAA section 107(d)(1)(A)(i)). Activities in the Bay Area that generate ozone precursors translate into substantial contributions to ozone nonattainment status in the Sacramento Valley and San Joaquin Valley air basins; CARB has concluded that pollution generated in the Bay Area has a significant, and at least in one case, overwhelming impact on the Sacramento region.
Another commenter noted that the federal CAA and case law establish that downwind ozone transport concerns are an appropriate basis to deny designation of ozone attainment status to an upwind area even if monitoring limited to the upwind area shows compliance. Air district boundaries established to regulate localized pollutants cannot be used to ignore adverse effects which emanate beyond these boundaries when highly mobile pollutants such as ozone precursors are involved. Until EPA takes regulatory action to designate the Bay Area nonattainment for the 8hour ozone standard it is premature to rely on that designation to deal with as yet unresolved transport issues. Because the Bay Area plan has not addressed transport contribution to downwind areas it is premature to relieve the area of the nonattainment designation and reasonably available control technology (RACT) and other requirements that are needed to demonstrate attainment in the downwind areas.
Response: CAA section 107(d)(1)(A)(i) applies to the submission by
state governors of initial designations following promulgation of new
or revised standards and is thus unrelated to determinations of
attainment. Similarly, the cases cited \11\ concern the permissible
scope of EPA's authority in redesignating areas from nonattainment to
attainment. Moreover, in determining whether an area has attained the
1hour ozone standard, EPA does not evaluate whether it meets all other
requirements of the Act. Thus, while EPA does interpret CAA section
110(a)(2)(A) and (D) to require States to address intrastate and
interstate transport, EPA does not need to determine whether the State
has regulated emissions from the Bay Area for purposes of transport in
determining whether the Bay Area has attained the ozone standard. To
the extent that emissions from the Bay Area significantly contribute to
nonattainment or maintenance of the ozone standard in downwind areas,
the State will need to address those contributing emissions in the
context of an attainment demonstration for the downwind areas. Further,
as a result of our attainment finding, certain CAA requirements are
suspended but will once again be imposed should the Bay Area violate
the standard prior to redesignation. As described in our response to
comment 1, a redesignation to attainment requires that several
additional requirements be fulfilled. Finally, note that in today's
action, EPA is approving the RACT control measure commitments included in the 2001 Plan.
\11\ Illinois State Chamber of Commerce v. USEPA, 775 F.2d 1141
(7th Cir. 1985) and State of Ohio v. Ruckelshaus, 776 F.2d 1333 (6th Cir. 1985).
Comment 12: Under the Clean Data Policy, EPA must ensure that the Bay Area submits the CCOS local attainment demonstration and regional assessment of the influence of Bay Area transported air pollution. (Seitz memo, page 7.)
Response: The Seitz memo provides that ``[d]eterminations made by EPA in accordance with the [Clean Data Policy] would not shield an area from EPA action to require emission reductions from sources in the area where there is evidence, such as photochemical grid modeling, showing that emissions from sources in the area contribute significantly to nonattainment in, or interfere with maintenance by, other nonattainment areas. EPA has the authority under the Act (* * * section 110(a)(2)(A) in the case of intrastate areas) to require emissions reductions if necessary and appropriate to deal with transport situations.'' For many years, the effort to address transport has been stymied by an inability to define the transport problem due to lack of data. At the present time, the Bay Area District, several downwind areas, and CARB are engaged in an effort to refine modeling based on the CCOS. Once complete, the modeling should provide a better understanding of the degree to which air pollution generated in the Bay Area affects air quality in downwind areas. The colead agencies and CARB have acknowledged the need to address transport \12\ in addition to their obligations to achieve the state 1hr and new federal 8hr ozone standard. As a result, EPA fully expects that diligent efforts to finalize CCOS modeling will continue and that those results will be used to revise SIPs if appropriate.
Comment 13: Commenters expressed concern with the fate of the motor
vehicle emissions budgets submitted with the 2001 Plan,\13\ and the
conformity and emissions consequence if those budgets were not
approved. One commenter noted that the conformity budgets are an
important tool to limit transported emissions from the Bay Area and
argued that the budgets must remain in effect, if not be made more
stringent, to further mitigate transported emissions. Another commenter
urged that EPA maintain MVEBs consistent with attainment during periods
of normal economic activity until the area has qualified for redesignation.
\13\ On February 14, 2002, EPA found the motor vehicle emission
budgets in the 2001 Plan to be adequate for transportation
conformity purposes. EPA's letter to CARB conveying the adequacy
finding, along with responses to public comments regarding the
adequacy of the budgets can be found at http://www.epa.gov/region09/air/sfbayoz/#0202 .
Reponse: As noted above and discussed in section IV below, the co
lead agencies and CARB have requested that EPA fully approve the motor
vehicle emissions budgets in the 2001 Plan. In this action, EPA is finalizing its approval of those budgets.
C. Applicability of Clean Air Act Planning Requirements in Areas Attaining the 1Hour Ozone Standard
When we redesignated the Bay Area back to nonattainment in 1998, we
concluded that the area became subject to the provisions of subpart 1
rather than subpart 2 of part D of the Clean Air Act. 63 FR 37258 (July 10, 1998). CAA
[[Page 21723]]
subpart 1 at section 172(c) requires states to submit plans with
certain revisions that are tied to the attainment demonstration:
1. A demonstration that the plan will result in annual incremental reductions in emissions of ozone precursors for the purposes of ensuring attainment of the 1hour ozone standard by 2006. This provision is known as the reasonable further progress (RFP) demonstration or plan, CAA section 172(c)(2);
2. A demonstration that the plan will result in attainment of the 1hour ozone standard as expeditiously as practicable but not later than September 20, 2006, CAA section 172(c)(1);
3. Contingency measures that will be undertaken if the area fails to make reasonable further progress to attain the standard by the applicable attainment date, CAA section 172(c)(9).
We believe that it is reasonable to interpret the CAA to not
require these provisions for ozone nonattainment areas that are
determined to be meeting the 1hour ozone standard. We discuss our
reasoning in the Seitz memo, in the proposal for this action, and below in our response to comments.\14\
\14\ We have also explained at length in other actions our
rationale for the reasonableness of this interpretation of the Act
and incorporate those explanations by reference here. See 61 FR
20458 (May 7, 1996) (ClevelandAkronLorrain, Ohio); 60 FR 36723
(July 18, 1995) (Salt Lake and Davis Counties, Utah); 60 FR 37366
(July 20, 1995) and 61 FR 3183233 (June 21, 1996) (Grand Rapids,
MI). Our interpretation has also been upheld by the U.S. Court of
Appeals for the Tenth Circuit in Sierra Club v. EPA, 99 F.3d 1551 (10th Cir. 1996).
We received comments on the proposed attainment determination regarding the applicability of certain CAA planning requirements to the Bay Area. The comments and our responses are summarized below. D. EPA Responses to Comments Regarding Applicability of Clean Air Act Requirements
Comment 14: Several commenters concurred with EPA's determination that attainment demonstration, contingency measures and RFP requirements do not apply. In contrast, a number of commenters contend that EPA has no authority in this situation to eliminate SIP requirements without a formal redesignation. Congress created a process for determining whether a region should be treated differently as to its requirements for planning and pollution controls if the region monitored attainment. That process is called redesignation under section 107(d)(3) of the Act. Redesignation actions involve a more complete and robust State submittal, and have the additional security of data collected during the period between the end of the attainment demonstration period and EPA's action on redesignation. Under the Act designation determines the applicable controls. There is nothing in the CAA that explicitly states that upon only a finding of attainment, the EPA can jettison SIP requirements. EPA says it is implicit, but that would require splitting apart an explicit redesignation process. Congress did not provide for that, and such an action would frustrate the purposes of the Act and redesignation process.
Response: In today's action, we are finalizing our determination
that the Bay Area has attained the 1hour ozone standard by its
statutory deadline of September 20, 2006 as demonstrated by three
consecutive years without a violation. As a result, we are also
finalizing our determination that certain Clean Air Act requirements
are not applicable to the Bay Area. The statutory basis for finding
that these planning requirements are not applicable is described in the
proposal and in the Clean Data Policy. See 68 FR 62041, 6204462045;
Seitz memo at 25. Contrary to the commenter's assertion, we are not
eliminating any applicable requirements. Rather, we have interpreted
the requirements of sections 172(c)(1), 172(c)(2), and 172(c)(9) as not
being applicable once an area has attained the standard, as long as it
continues to do so. This is not a waiver of requirements that by their
terms clearly apply; it is a determination that certain requirements
are written so as to be operative only if the area is not attaining the
standard. Our interpretation is consistent both with the CAA's goal of
achieving and maintaining clean air, and with the concomitant policy
goal of avoiding costly and unnecessary emission reductions, and, as
mentioned above, has been upheld in the Tenth Circuit in Sierra Club v. EPA, 99 F.3d 1551.
2. Comments Regarding the Applicability of EPA Policies to the Bay Area
Comment 15: EPA cites Sierra Club v. EPA, 99 F.3d 1551 (10th Cir. 1996) as authority for the waiver of CAA requirements. Several commenters, however, contend that the case was incorrectly decided. Further, commenters argue that the Bay Area is distinguishable from Utah in several respects:
In contrast to the 0.123 ppm design value in the Bay Area, the design value in Utah is 0.111 ppm, well below the 1hour standard.
The emissions that achieved improved air quality were determined by the court to be enforceable (unlike the Spare the Air program).
The Bay Area is recognized to be a nonattainment area for the 8 hour ozone standard.
The Bay Area is an upwind district for transport purposes. The court observed that air quality controls designed to surpass the applicable ozone standard would be costly and unnecessary.
Response: In Sierra Club, the Tenth Circuit Court of Appeals upheld
the rationale in the Seitz memo as it applies to moderate ozone
nonattainment areas. There, pending completion of the redesignation
process, and based on three years of air quality data, EPA found that
two Utah Counties designated as nonattainment for ozone and classified
as moderate had attained the ozone NAAQS. As a result, EPA determined
that the CAA's moderate area requirements for attainment and RFP
demonstrations, and contingency measures (sections 182(b)(1)(A) and
172(c)(9)) were inapplicable. Finding that this determination was a
logical extension of EPA's original interpretation in the General Preamble, the Court accorded deference to EPA's statutory
interpretation that once a moderate ozone nonattainment area has
attained the NAAQS, the moderate area CAA requirements for RFP,
attainment and contingency measures no longer apply. Id. at 1556.
Although the Bay Area is a nonclassified nonattainment area, there is
no doubt that the analogous subpart 1 area provisions serve exactly the
same purpose as the provisions at issue in Sierra Club for moderate
areas. Thus the Court's reasoning in that case applies equally to the
Bay Area situation. Finally, EPA expects that fact patterns will vary
from one area to the next but we do not believe such variations
undermine the legal and policy bases for our interpretation of the
applicability of CAA requirements in areas that have attained the standard.
Comment 16: In a similarly situated area, EPA did not determine attainment until it was able to redesignate the area to attainment and thus its residents had assurance of maintenance in the form of a maintenance plan. See EPA's St. Louis rulemaking, 68 FR 25418, May 12, 2003.
Response: CAA section 179(c) provides that ``[a]s expeditiously as
practicable after the applicable attainment date for any nonattainment
area, but not later than 6 months after such date, the Administrator
[of EPA] shall determine, based on the area's air quality as of the attainment date, whether the area attained the standard
[[Page 21724]]
by that date.'' See also CAA section 181(b)(2). Thus the statute
provides for findings of attainment based on air quality. The Clean
Data Policy provides for such findings prior to the attainment date
applicable to a nonattainment area. The policy indicates that EPA's
regional offices will conduct individual rulemakings concerning areas
that have three consecutive years of clean data demonstrating
attainment to make binding determinations that such areas have attained
the standard and need not submit SIP revisions addressing the CAA
requirements that are no longer applicable. Seitz memo, p. 6. Thus the
timing of attainment findings is authorized by the statute and dictated by longstanding Agency policy.
Comment 17: EPA's Clean Data Policy only addresses subpart 2 authority. Since the Bay Area is designated nonattainment under subpart 1, it is not applicable to the Bay Area.
Response: EPA's Clean Data Policy specifically addresses the RFP requirement in CAA section 172(c)(as defined in section (171(1)) and the contingency measure requirement in section 172(c)(9). Both of these statutory provisions apply to the 2001 Plan. With respect to the attainment requirement, the policy addresses the attainment requirement in section 182 which does not apply to the Bay Area plan. However, the analysis of that requirement applies equally to the section 172(c)(1) attainment requirement that does apply to the 2001 Plan. See Seitz memo, pages 35.
Comment 18: EPA's action is not supported by EPA's adopted guidance and policy documents. Specifically, John Calcagni's October 28, 1992 memo entitled ``State Implementation Plan (SIP) Actions Submitted in Response to Clean Air Act (Act) Deadlines' (10/28/92 Calcagni memo) is inconsistent with EPA proposed action on the specific issue of whether the Bay Area's SIP requirements may be relaxed at this stage. ``States, however, are statutorily obligated to meet SIP requirements that become due any time before an area is actually redesignated to attainment. [. . .] Hence, if there is a failure of the State to meet a statutory deadline [and, ergo, a SIP commitment to midcourse review] for an area, (before EPA has redesignated the area as attainment), a finding of failure to submit should be made. This, in turn, begins the sanctions process.'' 10/28/92 Calcagni memo, pages 34. This properly describes how the Act worksareas must still meet all SIP commitments after a determination of attainment, but before the redesignation is complete. Otherwise there is a gap in SIP coverage that is irrational and illegal. Logically, since an area must meet all applicable part D SIP requirements, including section 172(c) elements, in order to gain redesignation, section 107(d)(3)(E), these SIP requirements must be present at the time of redesignation. It would make little sense to excuse their inclusion now, then to require their adoption immediately prior to redesignation. The SIP must be continually effective during the period between determination of attainment and redesignation. EPA cannot rewrite the Act and waive the otherwise applicable part D SIP requirements during this ``gap'' period.
Response: The 10/28/92 Calcagni memo addresses the historical
situation in which certain states were planning to submit redesignation
requests prior to November 15, 1992 in an attempt to be exempted from
implementing mandatory CAA programs due to start in November of that
year (e.g., oxygenated fuels program, stage II vapor recovery rules,
etc.). The memo explains that while the approvability of a
redesignation request is based on requirements in place on the date of
the complete submittal, until the redesignation was finalized, states
would be statutorily bound to implement those programs. The types of
mandatory programs covered by the 10/28/92 Calcagni memo are
distinguishable from the planning requirements suspended by a finding
of attainment. In the Clean Data Policy, EPA has interpreted the
attainment demonstration, RFP, and contingency provisions of the Act to
be inapplicable to an area that is attaining the ozone standard as long
as the area continues to attain or is redesignated to attainment.\15\
This interpretation is based on the language and purpose of those
provisions. By contrast, the requirements for mandatory programs
addressed by the 10/28/92 Calcagni memo do not contain qualifying
language tied to attainment, such as ``for the purpose of ensuring
attainment of the applicable ambient air quality by the applicable
date.'' Compare, e.g., stage II vapor recovery (section 182(b)(3)) with RFP (section 171(1)).
\15\ See also 9/4/92 Calcagni memo at p. 6: ``The requirements
for reasonable further progress, identification of certain emissions
increases, and other measures needed for attainment will not apply
for redesignations because they only have meaning for areas not attaining the standard.''
Comment 19: The 9/4/92 Calcagni memo indicates that the Bay Area retains its obligation to model attainment as required by the mid course review commitment as part of its redesignation showing: ``No such supplemental modeling is required for O3 nonattainment areas seeking redesignation'' (page 3, emphasis added). The term ``supplemental'' reflects EPA's requirement that ordinary modeling of attainment, as required for all SIPS and which is contained in and was deferred by California's ``enforceable commitment'' must still be provided. EPA explains the purpose for supplemental modeling, which applies with vigor to the initial modeling requirement as follows: ``Modeling may be necessary to determine the representativeness of the monitored data. Id., page 3. If the data should be supported by modeling for redesignation, it should similarly be supported by modeling to support the determination of attainment, particularly where the region's actual emissions inventory has been depressed by economic forces and the District stands at the cusp of finalizing the modeling it has postponed for over a decade. While commenters recognize that the 9/4/1992 Calcagni memo purports to address redesignation actions, they assert that EPA itself cites this guidance as authority supporting EPA's proposal to delete RFP, attainment demonstration and contingency measure requirements from the Bay Area SIP. 68 FR 62044.
Response: EPA disagrees that its reference to the 9/4/92 Calcagni memo somehow retroactively modifies the scope of that memo. The purpose of our reference to the memo was to illustrate the consistency of our position that RFP becomes unnecessary when an area attains the standard. On page 6, the memo states that the ``requirements for reasonable further progress * * * will not apply for redesignation because they only have meaning for areas not attaining the standard.'' Emphasis added.
The 9/4/92 Calcagni memo states the following: ``The state must
show that the area is attaining the applicable NAAQS. There are two
components involved in making this demonstration which should be
considered interdependently. The first component relies upon ambient
air quality data. * * * The second component relies upon supplemental
EPAapproved air quality modeling. No such supplemental modeling is
required for O3 (ozone) nonattainment areas seeking redesignation * * *
'' (pages 2 and 3). This document explains that supplemental modeling
may be needed, for example, in sulfur dioxide and carbon monoxide
areas, where emissions are localized and a small number of monitors may
not be representative of air quality (page 3). In contrast, ozone is not a localized
[[Page 21725]]
pollutant, and the Bay Area has an extensive monitoring network
consisting of 24 monitors operating each year from 2001 through 2003 as
described in EPA's proposal at 68 FR 62043. Consistent with the
language in the memo and the rationale in calling for modeling in some
cases for some pollutants and not in other cases, modeling would not be
required for redesignation of ozone areas. The memo should not be read
to create a requirement for modeling in an area that has been determined to be attaining the ozone standard.
Finally, we reiterate that a finding of attainment does not delete
CAA requirements. The requirements for an attainment demonstration,
RFP, and contingency measures are suspended by the finding only as long
as the area continues to attain the standard or until the area is formally redesignated.
E. Effects of the Attainment Finding on the Bay Area and of a Future Violation of the 1Hour Ozone NAAQS
Based on our finding that the Bay Area is attaining the 1hour ozone standard, we are finding that the State of California is no longer required to submit an RFP plan, an attainment demonstration, or contingency measures for the area.
The lack of a requirement to submit these SIP revisions will exist only as long as the Bay Area continues to attain the 1hour ozone standard. If we subsequently determine that the area has violated the 1hour ozone standard (prior to a redesignation to attainment), the basis for the determination that the area need not make these SIP revisions would no longer exist. Thus, a determination that an area need not submit these SIP revisions amounts to no more than a suspension of the requirements for so long as the area continues to attain the standard.
Should the Bay Area begin to violate the 1hour standard, we will
notify California that we have determined that the area is no longer
attaining the 1hour standard. We also will provide notice to the
public in the Federal Register. Once we determine that the area is no
longer attaining the 1hour ozone standard then California will be
required to address the pertinent SIP requirements within a reasonable
amount of time. We will set the deadline for the State to submit the
required SIP revisions at the time we make a nonattainment finding.
California must continue to operate an appropriate air quality
monitoring network, in accordance with 40 CFR part 58, to verify the
attainment status of the area. The air quality data relied upon to
determine that the area is attaining the ozone standard must be
consistent with 40 CFR part 58 requirements and other relevant EPA guidance.
III. Approval of Bay Area 2001 Plan
In this action, EPA is finalizing its proposed approval of the
following elements of the 2001 Plan: The emissions inventories, RACM,
commitments to adopt and implement specific control measures, the motor
vehicle emissions budgets, and further study commitments. The
commitments to adopt and implement specific control measures \16\ are
listed in Tables 1, 2, and 3 below, and the commitments to conduct
further study of potential control measures, are listed in Table 4
below. We are approving a VOC motor vehicle emissions budget of 164.0
tons per day and a NO
\16\ We are approving the adoption and implementation dates of
the new measures and the total emissions reductions they are
cumulatively projected to achieve. We are approving all dates,
including those that have passed, in order to make the commitments enforceable by EPA and citizens under the CAA.
Table 1.New Stationary and Area Source Control Measures
Estimated VOC Estimated NOX
Adoption on Implementation reduction reduction
2001 SIP No. BAAQMD regulation No. Source category date date (tpd), 2000 to (tpd), 2000 to
2006 2006
Measures To Be Adopted by the BAAQMD
SS11...................... 83........................ Improved Architectural \17\2001 20032004 2.9 ...............
Coatings Rule.
SS12...................... 85........................ Improved Storage of 2002 2002 1.9 ...............
Organic Liquids Rule.
SS13...................... 814 and 819.............. Surface Preparation and 2002 2003 0.3 ...............
Cleanup Standards for
Metal Parts Coating.
SS14...................... 816....................... Aqueous Solvents.......... 2002 2003 3.0 ...............
SS15...................... TBD........................ Petroleum Refinery Flare 2003 2004 \18\ TBD ...............
Monitoring.
SS16...................... 818....................... LowEmission Refinery 2003 2004 TBD ...............
Valves.
SS17...................... 810....................... Improved Process Vessel 2003 2004 0.1 ...............
Depressurization Rule.
Total.................. ........................... .......................... ............... ............... 8.2 0.0
\17\ For commitments in the plan that do not identify the month,
as in Tables 1, 2, and 3, or the day of the month, as in Table 4,
EPA interprets the deadline to be no later December 31st of the noted year or the last day of the month, respectively.
\18\ At the time of plan adoption, the BAAQMD was not able to
determine the amount of emissions reductions that could be achieved
by adoption of rules implementing SS15 and 16. The District
indicated that the reductions were to be determined (TBD).
Therefore, the emission reduction total for SS11 through SS17 does not include reductions from these two measures.
Table 2.New Mobile Source Control Measure
Estimated VOC Estimated NOX
Request \19\ Implementation reduction reduction
2001 SIP No. Source category date date (tpd), 2000 to (tpd), 2000 to
2006 2006
Measure To Be Requested by the BAAQMD
MS1.................. Motor Vehicle 2002 20022003 4.0 ...............
FOR FURTHER INFORMATION CONTACT Ginger Vagenas, EPA Region IX, (415) 9723964, vagenas.ginger@epa.gov.
14 CFR Part 39 40 CFR Part 52 14 CFR Part 71 33 CFR Part 165 50 CFR Part 679 26 CFR Part 1 40 CFR Part 180 47 CFR Part 73 50 CFR Part 17 33 CFR Part 117 44 CFR Part 67 50 CFR Part 648 14 CFR Part 97 33 CFR Part 100 40 CFR Part 63 50 CFR Part 622 26 CFR Part 301 39 CFR Part 111 40 CFR Part 300 50 CFR Part 660 44 CFR Part 65 40 CFR Parts 52 and 81 40 CFR Part 271 47 CFR Part 64 50 CFR Part 665 47 CFR Part 76 50 CFR Part 229 14 CFR Part 23 14 CFR Part 25 21 CFR Part 522