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, 66759-66775 [E8-26500]
Download as PDF
Federal Register / Vol. 73, No. 219 / Wednesday, November 12, 2008 / Rules and Regulations
E. Executive Order 13211 (Energy
Effects)
This rulemaking is not a significant
energy action under Executive Order
13211 because this rulemaking is not
likely to have a significant adverse effect
on the supply, distribution, or use of
energy. Therefore, a Statement of Energy
Effects is not required under Executive
Order 13211 (May 18, 2001).
mandate that will result in the
expenditure by the private sector of 100
million dollars (as adjusted) or more in
any one year, and will not significantly
or uniquely affect small governments.
Therefore, no actions are necessary
under the provisions of the Unfunded
Mandates Reform Act of 1995. See 2
U.S.C. 1501 et seq.
F. Executive Order 12988 (Civil Justice
Reform)
This rulemaking meets applicable
standards to minimize litigation,
eliminate ambiguity, and reduce burden
as set forth in sections 3(a) and 3(b)(2)
of Executive Order 12988 (Feb. 5, 1996).
This rulemaking will not have any
effect on the quality of environment and
is thus categorically excluded from
review under the National
Environmental Policy Act of 1969. See
42 U.S.C. 4321 et seq.
G. Executive Order 13045 (Protection of
Children)
This rulemaking does not concern an
environmental risk to health or safety
that may disproportionately affect
children under Executive Order 13045
(Apr. 21, 1997).
H. Executive Order 12630 (Taking of
Private Property)
This rulemaking will not effect a
taking of private property or otherwise
have taking implications under
Executive Order 12630 (Mar. 15, 1988).
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I. Congressional Review Act
Under the Congressional Review Act
provisions of the Small Business
Regulatory Enforcement Fairness Act of
1996 (5 U.S.C. 801 et seq.), prior to
issuing any final rule, the United States
Patent and Trademark Office will
submit a report containing this final rule
and other required information to the
U.S. Senate, the U.S. House of
Representatives and the Comptroller
General of the Government
Accountability Office. The changes in
this final rule are not expected to result
in an annual effect on the economy of
100 million dollars or more, a major
increase in costs or prices, or significant
adverse effects on competition,
employment, investment, productivity,
innovation, or the ability of United
States-based enterprises to compete
with foreign-based enterprises in
domestic and export markets. Therefore,
this final rule is not a ‘‘major rule’’ as
defined in 5 U.S.C. 804(2).
J. Unfunded Mandates Reform Act of
1995
The changes in this final rule do not
involve a Federal intergovernmental
mandate that will result in the
expenditure by State, local, and tribal
governments, in the aggregate, of 100
million dollars (as adjusted) or more in
any one year, or a Federal private sector
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K. National Environmental Policy Act
L. National Technology Transfer and
Advancement Act
The requirements of section 12(d) of
the National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note) are inapplicable because this
rulemaking does not contain provisions
which involve the use of technical
standards.
M. Paperwork Reduction Act
The changes in this final rule involve
information collection requirements
which are subject to review by the
Office of Management and Budget
(OMB) under the Paperwork Reduction
Act of 1995 (44 U.S.C. 3501 et seq.). The
collection of information involved in
this notice has been reviewed and
approved by OMB under OMB control
number 0651–0021. The Office did not
resubmit an information collection
package to OMB for its review and
approval because the changes in this
final rule concern revised fees for
existing information collection
requirements associated with the
information collection under OMB
control number 0651–0021. The Office
will submit fee revision changes to the
inventory of the information collection
under OMB control number 0651–0021.
Notwithstanding any other provision
of law, no person is required to respond
to nor shall a person be subject to a
penalty for failure to comply with a
collection of information subject to the
requirements of the Paperwork
Reduction Act unless that collection of
information displays a currently valid
OMB control number.
List of Subjects
37 CFR Part 1
Administrative practice and
procedure, Courts, Freedom of
Information, Inventions and patents,
Reporting and record keeping
requirements, Small Businesses.
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66759
PART 1—RULES OF PRACTICE IN
PATENT CASES
1. The authority citation for 37 CFR
Part 1 continues to read as follows:
■
Authority: 35 U.S.C. 2(b)(2).
2. The authority citation for subpart is
revised to read as follows:
■
Authority: Secs. 1.401 to 1.499 also issued
under 35 U.S.C. 41 and 351 through 376.
3. Section 1.445 is amended by
revising paragraphs (a)(1), (a)(2) and
(a)(3) to read as follows:
■
§ 1.445 International application filing,
processing and search fees.
(a) * * *
(1) A transmittal fee (see 35
U.S.C. 361(d) and PCT Rule
14) .............................................
(2) A search fee (see 35 U.S.C.
361(d) and PCT Rule 16) .........
(3) A supplemental search fee
when required, per additional
invention ..................................
*
*
*
*
$240.00
$2,080.00
$2,080.00
*
Dated: October 21, 2008.
Jon W. Dudas,
Under Secretary of Commerce for Intellectual
Property and Director of the United States
Patent and Trademark Office.
[FR Doc. E8–26711 Filed 11–10–08; 8:45 am]
BILLING CODE 3510–16–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 52 and 81
[EPA–R09–OAR–2008–0306; FRL–8724–7]
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
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: EPA is approving the State of
California’s request under the Clean Air
Act (CAA or the Act) 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
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Federal Register / Vol. 73, No. 219 / Wednesday, November 12, 2008 / Rules and Regulations
I. Background
II. Public Comments and EPA Responses
A. Area Has Attained
B. Fully Approved SIP
C. Improvements in Air Quality are Due to
Permanent and Enforceable Emission
Reductions
D. Area Has Met All Applicable CAA
Section 110 and Part D Requirements
E. Maintenance Plan
F. Revision of Boundary Designation
G. Miscellaneous Comments
III. Final Actions
IV. Statutory and Executive Order Reviews
• Approval of the State of California’s
request to revise the designation for the
SJV serious PM–10 nonattainment area
by splitting the area into two separate
nonattainment areas, the SJVAB serious
PM–10 nonattainment area and the East
Kern serious PM–10 nonattainment
area.
• Redesignation of the SJVAB
nonattainment area to attainment for the
PM–10 NAAQS and approval of the
maintenance plan, motor vehicle
emissions budgets and conformity
trading mechanism for the SJVAB area.
• Exclusion from use in determining
that the SJVAB 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.
• Approval of enforceable
commitments by the Kern County Air
Pollution Control District (KCAPCD)
and the California Air Resources Board
(CARB) to install a PM–10 monitor in
the East Kern nonattainment area and to
address CAA requirements under
section 189(d) as necessary for the East
Kern area.
Subsequently, On May 23, 2008, EPA
extended the public comment period for
two weeks, until June 10, 2008. 73 FR
30029. EPA issued the extension in
order to notify the public of a minor
change in the motor vehicle emissions
budgets and to provide the public with
the opportunity to consider these
technical corrections.
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.1 EPA is
required to approve or deny the revised
designation within 18 months of receipt.
On January 31, 2008, the State
submitted to EPA a revised designation
that involves a boundary change only
and not a change in status (e.g., from
‘‘nonattainment,’’ to ‘‘attainment’’ or
‘‘unclassifiable’’) of any area.
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.
I. Background
On April 25, 2008 (73 FR 22307), EPA
proposed the following actions:
1 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).
Valley Air Basin (SJVAB) serious PM–10
nonattainment area and the East Kern
serious PM–10 nonattainment area. EPA
is also redesignating the SJVAB
nonattainment area to attainment for the
PM–10 national ambient air quality
standard (NAAQS) and approving the
PM–10 maintenance plan, motor vehicle
emissions budgets and conformity
trading mechanism for the area. EPA is
also excluding from use in determining
that the area has attained the standard
exceedances on July 4, 2007, and
January 4, 2008, that EPA has concluded
were caused by exceptional events.
Finally, EPA is approving 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 CAA
requirements under section 189(d) as
necessary for the area.
DATE: This rule is effective on December
12, 2008. The motor vehicle emission
budgets are applicable as of November
12, 2008.
ADDRESSES: EPA has established docket
number EPA-R09–OAR–2008–0306 for
this action. The docket is available
electronically at 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.
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(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 memorandum).
The proposed rule provides a more
detailed discussion of the background
pertinent to this final action.
II. Public Comments and EPA
Responses
EPA received one letter in support of
EPA’s proposed actions from the San
Joaquin Valley Air Pollution Control
District (SJVAPCD or the District) and
two letters with adverse comments. As
EPA sets forth in detail in its responses
to comments below, in taking final
action EPA has fully considered all data
pertinent for regulatory use in
determining attainment in the SJVAB
area and EPA continues to believe that
the area has attained the PM–10
standard. EPA has also determined that
the State’s request for redesignation and
the maintenance plan for the SJVAB
area meet the applicable requirements of
the CAA. In addition, EPA is granting
the State’s request for a boundary
revision for the area based on a
multiplicity of factors. The available
monitoring data for the East Kern area,
while limited, also indicate that
concentrations are well below the
NAAQS. Thus, for the reasons set forth
in the responses to comments below, as
well as in the proposed rule, EPA is
finalizing its proposed determinations
as fully meeting the requirements of the
CAA.
A. Area Has Attained
Comment 1: Earthjustice (EJ) states
that the first condition that a
nonattainment area must meet in order
to be redesignated to attainment under
CAA section 107(d)(3)(E) is that EPA
has determined that the area has
actually attained the NAAQS. EJ alleges
that the SJV nonattainment area has
recorded multiple exceedances of the
standard during the period that EPA is
relying on to demonstrate attainment
and that EPA is thus ignoring a serious
air quality problem and the health
impacts associated with it. EJ
incorporates by reference and attaches
its previous comments on EPA’s
attainment determination that claim the
problem EPA is ignoring has existed for
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Federal Register / Vol. 73, No. 219 / Wednesday, November 12, 2008 / Rules and Regulations
many years, is part of what led EPA to
designate the SJV area nonattainment in
the first place and is caused by ongoing
human activity that is not reasonably
controlled.
Response 1: The previous comments
to which EJ refers in its June 10, 2008
comment letter on the proposed rule are
contained in its August 18, 2006
comment letter with attachments A–H,
October 26, 2007 comment letter,
December 29, 2006 Petition for
Reconsideration and March 21, 2007
Petition for Withdrawal, with attached
declarations from Sarah Jackson and Jan
Null. EJ raised the same issues as it
raises here during EPA’s rulemakings
regarding the 2006 determination of
attainment for the SJV nonattainment
area and 2008 affirmation of that
determination. EPA fully responded to
EJ’s comments at that time. See the final
rules at 71 FR 63642 (October 30, 2006)
and 73 FR 14687 (March 19, 2008). See
also the proposed rules for these actions
at 71 FR 40952 (July 19, 2006) and 72
FR 49046 (August 27, 2007). As we
explained in our responses to EJ’s
comments in the final rules, EPA
believes that the SJV area has attained
the PM–10 NAAQS and that the
exceedances noted by EJ were properly
excluded from consideration under the
Agency’s Exceptional Events Rule
(EER)(72 FR 13560; March 22, 2007).
EJ subsequently filed petitions for
review of the October 2006 and March
2008 final rules in the U.S. Court of
Appeals for the Ninth Circuit. Latino
Issues Forum, et al. v. EPA, Nos. 06–
75831 and 08–71238.2 In its opening
brief in these cases, filed on June 16,
2008, EJ again raises these issues. In its
brief in opposition, filed on September
3, 2008, EPA again responds to EJ’s
arguments. EJ was required to raise any
issues regarding the 2006 attainment
determination and 2008 affirmation of
that determination during those
rulemakings and in the Ninth Circuit in
Latino Issues Forum and cannot
relitigate the same issues here.
Moreover, in the proposed rule for
today’s final action we proposed to
exclude under the EER data showing
exceedances in the SJV nonattainment
area on July 4, 2007 and January 8,
2008, and concluded that the area
continued to attain the PM–10 standard
through February 2008. We did not
receive any adverse comments on this
aspect of our proposed rule. In this final
action, for the reasons set forth in the
proposed rule and in EPA’s concurrence
letters to which it refers, we are
concurring with the State’s flagging of
2 The
Ninth Circuit has consolidated the two
petitions for review.
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18:26 Nov 10, 2008
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those data as caused by fireworks and
high wind exceptional events, and
excluding those data from consideration
in determining that the SJVAB area
continues to attain the standard.
Finally, EPA is aware of PM–10
exceedances recorded on May 21, 2008
at the Corcoran and Bakersfield Federal
Equivalent Method (FEM) monitors and
the Corcoran Federal Reference Method
(FRM) monitor, and on May 22, 2008 at
the Corcoran FEM. On June 24, 2008,
the District posted on its website
documentation that these exceedances
were caused by a natural event, i.e.,
high winds. The comment period ended
on July 24, 2008 and no public
comments were received. The
documentation was submitted to EPA
on August 12, 2008 and EPA has
concurred that these exceedances
should be flagged as exceptional events.
Letter from Wayne Nastri, EPA to Mary
D. Nichols, CARB, September 24, 2008.
EPA is not taking comment on
whether the May 2008 exceedances
should be excluded from the
determination in this final rule that the
SJVAB area continues to attain the PM–
10 standard. The determination of
whether an area has attained the PM–10
standard is based on the most recent
three consecutive calendar years of data.
As mentioned above and in other EPA
actions, the SJVAB area has attained the
PM–10 standard based on data for the
three-year period from 2003 through
2005 and the three-year period from
2005 through 2007. See 71 FR 63642
and 73 FR 14687. Because 2008 has not
ended, EPA cannot determine whether
the area has attained the standard based
on the three-year period from 2006
through 2008. We can, however,
determine with less than three years of
data whether the SJVAB area has failed
to attain in the period from 2006 to date.
See 40 CFR part 50, appendix K, section
2.3(c) and 71 FR 63642, footnote 26.
Because the May 21 and 22, 2008
exceedances are the only exceedances at
the Corcoran monitors since 2006 not
excluded through notice and comment
rulemaking from regulatory
consideration, the expected number of
exceedances recorded at the FRM
monitor, based on the May 21
exceedance, is three and the expected
number of exceedances recorded at the
FEM monitor on May 21 and May 22 is
two.3 Similarly, because the May 21,
3 Note that the Corcoran FRM operates on a onein-three day schedule and that EPA does not
combine PM–10 data collected with different
monitoring methods, i.e., FRMs and FEMs. See
Memorandum from Gerald A. Emison, EPA, to EPA
Regional Division Directors, ‘‘Revision to Policy on
the Use of PM–10 Measurement Data,’’ November
21, 1988 at 3.
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66761
2008 exceedance is the only exceedance
recorded at the Bakersfield monitor
since 2006 not excluded from regulatory
consideration through notice and
comment rulemaking, the expected
number of exceedances at the
Bakersfield monitor is one. Thus, even
if EPA does not exclude the May 21 and
22, 2008 exceedances from regulatory
consideration, the SJVAB area continues
to attain the PM–10 NAAQS to date
because both Corcoran and Bakersfield
have an expected number of
exceedances of less than or equal to one
per year, averaged over the three year
period 2005–2007 and through 2008 to
date. All other monitors in the SJV area
had an expected number of exceedances
of less than or equal to one per year
during these periods. EPA thus
determines that the SJVAB area has
attained the PM–10 NAAQS as required
by section 107(d)(3)(E)(i).
B. Fully Approved SIP
Comment 2: EJ states that the second
condition for redesignation under
section CAA section 107(d)(3)(E) is that
an area seeking redesignation must have
a fully approved state implementation
plan (SIP) and must satisfy all
requirements that apply to the area and
that the SJV nonattainment area does
not have such a SIP. EJ argues that while
EPA concedes that it has never
approved contingency measures for the
area and has instead suspended this
requirement under the Agency’s Clean
Data Policy, neither the policy nor the
cases EPA cites addresses PM–10
nonattainment areas and therefore do
not square EPA’s action with the
mandate under CAA section 189(c) that
such areas continue to achieve the
milestones for emission reductions in
order to demonstrate reasonable further
progress (RFP) ‘‘until the area is
redesignated to attainment.’’ EJ believes
that because contingency measures are
also necessary to ensure this progress is
achieved, EPA cannot suspend the
requirement for these measures. Citing
Engine Mfrs. Ass’n v. EPA, 88 F.3d
1075, 1089 (D.C. Cir. 1996), EJ asserts
that EPA does not have the authority to
waive statutory requirements and
circumvent redesignation provisions
because it believes compliance with
those requirements is unnecessary.
Response 2: In 2006 EPA approved
the entire nonattainment plan for the
SJV area,4 including the CAA section
189(c)(1) reasonable further progress
milestones, except for the CAA section
172(c)(9) contingency measures, on
4 ‘‘2003 PM10 Plan, San Joaquin Valley Plan to
Attain Federal Standards for Particulate Matter 10
Microns and Smaller’’ (2003 PM–10 Plan).
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which EPA deferred action. 69 FR 30006
(May 26, 2004). EPA subsequently
determined that the contingency
measures requirement for the SJV area
was suspended as a result of its October
2006 determination that the area has
attained the PM–10 standard. 71 FR
63642, 63663. During that rulemaking,
EJ raised the same issues with regard to
EPA’s Clean Data Policy 5 and statutory
construction as it raises here. EPA
responded to EJ’s arguments in the final
rule. See id. at 63643–63647. EJ again
raises these issues in its opening brief in
Latino Issues Forum. EPA again
responds to EJ’s arguments in its brief in
opposition. EJ was required to raise any
issues regarding the suspension of the
contingency measures requirement
during EPA’s 2006 attainment
determination rulemaking and in Latino
Issues Forum. EJ did so and cannot
relitigate the same issues here. Because
EPA has approved SIP provisions
submitted by California for the SJVAB
area that address all applicable CAA
requirements, EPA has concluded that
the CAA section 107(d)(3)(E)
requirement for a fully approved SIP has
been met.
In addition, in the context of
evaluating the area’s eligibility for
redesignation, there is a separate and
additional justification for finding that
the section 172(c)(9) contingency
measures are not an applicable SIP
requirement for purposes of
redesignation. Prior to and
independently of that policy, and
specifically in the context of
redesignations, EPA interpreted the
contingency measure requirement as not
applicable for purposes of
redesignation. In the General Preamble
EPA stated that:
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[t]he section 172(c)(9) requirements are
directed at ensuring RFP and attainment by
5 EPA has long interpreted the CAA to provide
that certain nonattainment area requirements, the
purpose of which are to ensure attainment of the
relevant NAAQS by the applicable deadline, will no
longer apply once an area has attained that NAAQS,
and for as long it continues to do so until it is
redesignated to attainment status. While referred to
as the Clean Data Policy, it is more accurately
described as EPA’s interpretations of the relevant
provisions of Title I, Part D of the CAA. See Sierra
Club v. EPA, 375 F.3d 537, 541–42 (7th Cir. 2004);
Sierra Club v. EPA, 99 F.3d 1551, 1156–57 (10th
Cir. 1996). EPA first set forth this interpretation in
its ‘‘General Preamble for the Interpretation of Title
I of the Clean Air Act Amendments of 1990,’’
(General Preamble) thereafter reiterated it in several
policy memoranda and since codified the policy
with respect to ozone and PM–2.5 nonattainment
areas. 57 FR 13498, 13564 (April 16, 1992), 40 CFR
51.918 (ozone) and 51.1004(c) (PM2.5). EPA has
applied the policy to numerous PM–10
nonattainment areas, including the SJV area. For an
expanded description of the policy and our
application of it, see Respondent EPA’s Merits Brief
in Latino Issues Forum at 7–8, 71 FR 40952, 40954
and 71 FR 63642, 63644.
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18:26 Nov 10, 2008
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the applicable date. These requirements no
longer apply when an area has attained the
standard and is eligible for redesignation.
Furthermore, section 175A for maintenance
plans * * * provides specific requirements
for contingency measures that effectively
supersede the requirements of section
172(c)(9) for these areas.
See also Calcagni memorandum at 6
(‘‘The requirements for reasonable
further progress and other measures
needed for attainment will not apply for
redesignations because they only have
meaning for areas not attaining the
standard.’’). Thus, even if the
contingency measure requirement had
not previously been suspended, it
would not apply for purposes of
evaluating whether an area that has
attained the standard qualifies for
redesignation. EPA has enunciated and
held this position since the General
Preamble was published more than
sixteen years ago and represents the
Agency’s interpretation of what
constitutes applicable requirements
under section 107(d)(3)(E). The Courts
have recognized the scope of EPA’s
authority to interpret ‘‘applicable
requirements’’ in the redesignation
context. See Sierra Club v. EPA, 375
F.3d 537 (7th Cir. 2004).
C. Improvements in Air Quality Must Be
Due to Permanent and Enforceable
Emission Reductions
Comment 3: EJ states that a 1992
guidance memorandum from John
Calcagni lays out the steps that an area
must take to show that the improvement
in air quality is attributable to
permanent and enforceable reductions
in emissions, the third condition for
redesignation to attainment under CAA
section 107(d)(3)(E). EJ claims that this
analysis should include estimating the
percentage reductions achieved from the
federal and state controls implemented
in the area, taking into account
permitted emission rates, production
capacities and other related information.
EJ states that EPA, banking on its waiver
of all the violations during the period of
interest, neglected to perform the proper
analyses in the Calcagni memorandum
and merely repeats the District’s belief,
based on four observations (comments 4
through 7 below), that the area is
attaining the standard.
Response 3: As discussed in our
proposed rule, the Calcagni
memorandum states that the state must
be able to reasonably attribute the
improvement in air quality to emission
reductions which are permanent and
enforceable, and the improvement
should not be a result of temporary
reductions (e.g., economic downturns or
shutdowns) or unusually favorable
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meteorology. The Calcagni
memorandum also states that 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. Our
proposed rule discusses how each of
these factors is addressed by the State in
the ‘‘2007 PM10 Maintenance Plan and
Request for Redesignation,’’ September
20, 2007, SJVAPCD (2007 Plan). 73 FR
22307; 2008, footnote 8; 22311–22312.
In general, the 2007 Plan shows that
there has been a significant
improvement in PM–10 air quality since
1990, noting that there were 33
estimated exceedance days during
1990–1992 and 2.9 exceedance days
during 2002–2004. This decrease in
exceedance days (and emissions)
occurred during a period of rapid
economic growth in the SJVAB area as
indicated by the increases in population
and vehicle miles traveled (VMT). The
2007 Plan did not find any evidence of
significant shutdowns that would cause
the decline in exceedance days. The
2007 Plan analyzed the meteorology in
the SJVAB area during 2003–2006 by
comparing the average annual wind
speeds, precipitation levels and stability
levels to long-term averages and found
that there was no consistent pattern to
show that there was favorable
meteorology leading to the improvement
in PM–10 levels during 2003–2006.
The 2007 Plan states that over 500
new rules and rule amendments have
been adopted, reducing NOX and PM–10
emissions from a wide range of source
categories, and it shows decreases in the
overall emissions of NOX and PM–10
(which include all emissions from area
sources as well as from permitted major
sources) since 2000. A more detailed
discussion of these analyses can be
found in our proposed rule and in the
2007 Plan. EPA’s analysis is based on
the State’s assessment and EPA
continues to believe that the State has
demonstrated that the improvement in
PM–10 air quality in the SJVAB area is
a result of permanent and enforceable
reductions in emissions and has
adequately addressed the provisions of
the Calcagni memorandum.
Finally, as discussed in the response
to comment 1 above, EPA has
determined that the SJV area has
attained the PM–10 standard. 71 FR
63642; 73 FR 14687. These
determinations included EPA’s
concurrence with the State’s and Santa
Rosa Rancheria Tribe’s conclusion that
a number of exceedances were caused
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by exceptional events and thus should
be excluded from regulatory
consideration. Id. EJ seems to suggest
that EPA’s analyses should include
these exceedances even though they
have been properly excluded from
regulatory consideration. EPA disagrees.
Comment 4: EJ claims that the District
provides a chart (2007 Plan at 24, Figure
2) showing a downward trend in air
pollution levels that is completely
misleading because it does not include
EPA-acknowledged exceedances in 2004
and 2005, let alone the many
exceedances EPA has ignored in its
attainment determination.
Response 4: The District’s chart (2007
Plan at 24, Figure 2) shows a long-term
downward PM–10 trend from 1990 to
2006 for the SJVAB area by plotting the
estimated exceedance days over the
NAAQS. The estimated exceedance
days in this chart are based on
exceedances recorded with FRMs and
not FEMs such as continuous beta
attenuation monitors (BAMs). EPA
believes that the District’s chart is not
misleading and provides a general
picture of the long-term trend for PM–
10 and that 1990 is a reasonable year to
begin the analysis because that was the
year the CAA was amended.
EJ’s comment letter (page 4) includes
a chart, ‘‘PM–10 Trend,’’ that appears to
revise the 2007 Plan’s chart by adding
the exceedances from BAMs that
occurred in 2004 and 2005 and by
removing the data for 1990 in order to
show a less precipitous decline in PM–
10 levels. However, even with the
exclusion of the 1990 data and the
addition of the exceedances from the
BAMs, EJ’s ‘‘PM–10 Trend’’ chart still
shows a decline in PM–10 levels.
Moreover, the 2007 Plan provides a
summary in Table 10 of the declining
annual average emissions inventories
from 1990 through 2005 which is
consistent with the District’s trends
chart. Table 10 shows PM–10 emissions
decreasing by 46 tons per day (tpd) and
NOX emissions decreasing by 228 tpd
during this time period.
Finally, as discussed above, EPA has
not ignored any recorded exceedances
but rather has followed its regulations to
exclude from regulatory consideration
any exceedances that are caused by
exceptional events. 73 FR 14687;
response to comment 3 above. EPA also
set forth in its 2006 attainment
determination its conclusions as to prior
monitored data. 71 FR 63642.
Comment 5: EJ claims that while the
District asserts that growth in the SJV
nonattainment area has been rapid since
1990 but that emissions have decreased,
the sources of these claimed reductions
do not support redesignation.
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Response 5: See responses to
comments 1, 3 and 4 above, and 7 and
8 below.
Comment 6: EJ alleges that the District
and EPA conclude without justification
that the District’s meteorological
analysis shows that favorable
meteorology did not lead to the
improvements in air quality. Instead, EJ
argues, the analysis shows that from
2004 to 2006, the SJV nonattainment
area experienced some of the wettest
years on record and that 2003 through
2006 experienced lower than average
stability levels, which EPA and the
District concede would lead to better
dispersion conditions and lower PM–10
levels. As a result, EJ claims the data
provided undercut any claim that the
alleged air quality improvement is likely
to be maintained.
Response 6: Our proposed rule
summarizes the meteorological analysis
provided in the 2007 Plan which
includes an examination of the
precipitation, temperature wind speeds
and atmospheric stability during the
period 2003 through 2006. The
summary was based on data presented
in Appendix C to the 2007 Plan. As EJ
comments, there were some conditions
that favored lower PM–10 levels;
however, there were also conditions that
favored higher PM–10 levels.
Conditions that favored higher PM–10
levels included no variation in annual
average wind speeds (which are
generally quite low for the SJV area),
warmer than average temperatures and
two dry years ranking 98th and 112th in
wetness (with the 1st year being the
wettest year) during a 128 year period.
Since there were conditions that both
favored and did not favor higher PM–10
levels, the conclusion of the 2007 Plan
and EPA’s analysis is that there was no
consistent pattern to show that
attainment was a result of unusually
favorable meteorology. 73 FR 22307,
22312.
Finally we note that the Calcagni
memorandum makes clear that
‘‘[a]ttainment resulting from * * *
unusually favorable meteorology would
not qualify as an air quality
improvement due to permanent and
enforceable emission reductions.’’
Calcagni memorandum at 4. Therefore
EPA disagrees with EJ’s comment that
the meteorological data indicate that the
air quality improvement will not likely
be maintained.
In addition, EPA obtained available
information on precipitation, average
monthly temperatures and wind speeds
for 2007 and compared the 2007 data to
the averages presented in Appendix C to
the 2007 Plan at Tables C–1, C–2 and C–
3. (Atmospheric stability data for 2007
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was not available.) The total
precipitation for 2007 was 7.03 inches
(https://www.wrh.noaa.gov/hnx/fat/
normals/fatrnyr.htm) which is lower
than the average precipitation of 10.13
inches for 1878 through 2006 (2007 Plan
at Table C–1) and would favor higher
PM–10 levels. The average monthly
temperatures in degrees Celcius for 2007
were 4.6 for January, 9.5 for February,
14.3 for March, 15.9 for April, 20.7 for
May, 24 for June, 26.3 for July, 26.3 for
August, 21.7 for September, 16.1 for
October, 11.9 for November and 5.5 for
December. (https://www.weather.gov/
climate/xmacis.php?wfo=hnx) When
compared to the average monthly
temperatures from 1900 through 2005
(2007 Plan at Table C–2), the average
temperatures for the months of March,
May, June and August were higher in
2007 than average and would favor
higher PM–10 levels. Finally, the
average wind speed for 2007 was 3.7
miles per hour (mph) (https://
www.cimis.water.ca.gov) which is
consistent with the average wind speed
of 3.72 mph for 1984 through 2006
(2007 Plan at Table C–3) and would
favor high PM–10 levels. Since the
available 2007 meteorological data favor
higher PM–10 levels, EPA continues to
believe that there is no consistent
pattern that would establish that
attainment has resulted from unusually
favorable meteorology.
Comment 7: EJ disputes EPA’s
conclusion that improvements in air
quality are the result of permanent and
enforceable reductions in emissions
from rules adopted by the District since
1992. EJ claims that most of these rules
were adopted only in the last few years
and therefore any trend in emission
reductions that can be inferred from the
chart provided by the District (2007
Plan at 24, Figure 2) cannot be
attributed to these rules. EJ suggests that
the drop in exceedance days between
1990 and 1992 might be due to a
difference in the methodologies for
measuring exceedances for the TSP and
PM–10 standards. EJ provides its own
chart, ‘‘PM–10 Trend,’’ adjusted to
include the exceedance days that it says
EPA has acknowledged, that purports to
show only minimal changes in the
recurring pattern of PM–10 violations
over the last 15 years.
Response 7: On July 1, 1987, EPA
revised the NAAQS for particulate
matter by replacing the standards for
total suspended particulate matter (TSP)
with new standards applying only to
PM–10. 52 FR 24672. While PM–10
monitoring data have been collected
since 1987 (see 71 FR 63642, 63653), the
District and CARB have not reported
TSP data to EPA’s Air Quality System
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(AQS) database since 1989. Therefore
any difference in measurement
methodologies for the two pollutants
could not be the cause of the drop in
exceedance days between 1990 and
1992.
Since enactment of the 1990 CAA
Amendments, the State has adopted and
submitted several PM–10 plans. These
include a moderate area plan under
CAA section 189(a), a serious area plan
under section 189(b) and a serious area
plan under section 189(d) (i.e., the 2003
PM–10 Plan approved by EPA in 2004
and discussed above). The 2003 PM–10
Plan provides a summary of the many
State, District and EPA rules adopted
from 1990 through 2003. See 2003 PM–
10 Plan at Tables 4–1, 4–2, 4–3 and 4–
4. The 2003 PM–10 Plan also includes
commitments for additional PM–10 and
NOX measures, all of which were
adopted by the District and State after
2003 and most of which have been
approved by EPA. See response to
comment 8 below.
The District’s chart (2007 Plan, Figure
2) shows that PM–10 levels have
declined from 1990 through 2006 while
these PM–10 plans and rules have been
adopted and implemented. We note that
even EJ’s own ‘‘PM–10 Trend’’ chart
shows a general decrease in PM–10
levels since 1992 and since early 2000.
Furthermore, the 2007 Plan shows
that significant reductions in PM–10
and NOX emissions occurred from the
year 2000 to the year 2005, the time
period during which the SJV area
attained the PM–10 standard. NOX
emissions have declined from 673 tpd
in 2000 to 606 tpd in 2005 and PM–10
emissions have declined from 324 tpd
in 2000 to 284 tpd in 2005. 2007 Plan;
Staff Report, Air Resources Board,
‘‘Analysis of the San Joaquin Valley
2007 PM10 Maintenance Plan,’’ (ARB
Staff Report for 2007 Plan) Appendix
B.6
As can be seen from the above
discussion and our responses to
previous comments, PM–10 exceedance
days and PM–10 and NOX emission
levels have declined while at the same
time the SJV area has exhibited
significant growth in population and
vehicle miles traveled. 2007 Plan at 24,
Figure 2 and at 26, Figures 3 and 4.
Thus EPA continues to believe that it is
reasonable to attribute the improvement
in PM–10 air quality to the emission
reductions from adopted rules that are
permanent and enforceable.
Comment 8: EJ argues that the
District’s failure to estimate the tons or
percent reduction from the baseline year
achieved by its PM–10 control measures
makes it difficult to assert that any
improvements in air quality are the
result of such controls. Further, while
EPA claims that the District has adopted
all of its rule commitments in the 2003
PM–10 Plan, only 2 of the 14
commitments have received EPA
approval according to EJ. The
maintenance plan identifies 8 additional
rules, only 3 of which have been
approved by EPA. EJ states that of the
22 rules the District identified during its
PM–10 planning process to help reduce
PM–10 in the SJV nonattainment area,
only 5 are enforceable elements of the
SIP.
Response 8: The 2007 Plan provides
a summary of overall NOX and PM–10
emissions and shows that emissions
have decreased from approximately
1177 tpd in 1990 to approximately 1000
tpd in 2000 to approximately 900 tpd in
2005 and estimates that they will
continue to decrease to approximately
800 tpd in 2010. 2007 Plan at Table 10
and 73 FR 22307, 22312. These
declining emissions levels have
occurred as population and VMT have
increased and are due to the emissions
reductions from rules and control
measures that have been adopted and
implemented since 1990. 2007 Plan at
26 through 27 and 2003 PM–10 Plan at
Tables 4–1, 4–2, 4–3 and 4–9.
The 2003 PM–10 Plan summarizes the
numerous rules and control measures
adopted by the SJVAPCD, the State and
EPA prior to 2003. 2003 PM–10 Plan at
Tables 4–1, 4–2 and 4–3. The 2003 PM–
10 Plan also includes District
commitments to achieve additional
reductions. 2003 PM–10 Plan at Table
4–9. As discussed below, the
commitments have all been converted to
adopted rules. The emissions reductions
from all of the 2003 PM–10 Plan’s rules,
control measures and adopted
commitments are reflected in the 2007
Plan’s emissions inventory. ARB Staff
Report for 2007 Plan at Appendix B.
It is not clear what year EJ considers
to be the baseline year; however, the
2007 Plan provides emissions
inventories for the years 1990, 2000,
2005 and 2010 which include the
estimated tpd of reductions achieved by
the PM–10 rules, control measures and
rules adopted pursuant to commitments.
2007 Plan at Table 10 and ARB Staff
Report for 2007 Plan at Appendix B.
Thus, EPA believes that the State and
District have estimated the tpd
reductions from several baseline years
(1990, 2000 and 2005) achieved by its
PM–10 control measures and have
shown that the improvements in air
quality are the result of such controls.
Regarding EJ’s comment that only five
of the 22 rules the District identified
during its PM–10 planning process are
enforceable elements of the SIP, EPA
notes that this information was updated
in the 2007 Plan. See ‘‘Errata, 2007
PM10 Maintenance Plan and Request for
Redesignation,’’ October 9, 2007,
included in the 2007 Plan submittal to
EPA. Table 1 below summarizes the
EPA-approved rules from the 2003 PM–
10 Plan commitments and provides the
EPA approval dates for these rules as
applicable. EPA has approved all but
three of the submitted rules (Rules 4694,
4401 and 9510).
TABLE 1—SUMMARY OF EPA ACTIONS ON 2003 PM–10 PLAN COMMITMENTS
2003 PM–10 plan commitment 7 (pollutants
covered by commitment)
Adopted rule number and title
Agriculture (Conservation Management
Practice Program) (PM–10, VOC).
B. Cotton Gins (PM–10) ....................................
C. Dryers (NOX) ................................................
D. Fugitive PM–10 (Regulation VIII) (PM–10) ..
4550—Conservation Management Practices ...
Approved 2/14/06, 71 FR 7683.
4204—Cotton Gins ...........................................
4309—Dryers, Dehydrators, and Ovens ..........
8011—General Requirements ..........................
8021—Construction, Demo, Excavation
8031—Bulk Materials.
8041—Carryout and Trackout.
8051—Open Areas.
8061—Paved and Unpaved Roads.
8071—Unpaved Vehicle/Equip Traffic Areas.
Approved 11/9/06, 71 FR 65740.
Approved 5/30/07, 72 FR 29886.
Approved 2/17/06, 71 FR 8461.
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A.
EPA action
6 See footnote 2 of the proposed rule. 73 FR
22307, 22308.
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66765
TABLE 1—SUMMARY OF EPA ACTIONS ON 2003 PM–10 PLAN COMMITMENTS—Continued
2003 PM–10 plan commitment 7 (pollutants
covered by commitment)
Adopted rule number and title
E. Glass-Melting Furnaces (SOX) .....................
F. Gas-Fired Oilfield Steam Generators (SOX)
8081—Agricultural Sources.
4354—Glass Melting Furnaces ........................
4406—Sulfur Compounds From Oilfield Steam
Generators—Kern County.
9510—Indirect Source Review .........................
G. Indirect Source Review, and Indirect Source
Mitigation Fee (NOX, PM–10).
H. Solid Fuel Boilers, Steam Generators, and
Process Heaters (NOX, SOX).
I. Small Boilers, Steam Generators, and Process Heaters (NOX, SOX).
J. Water Heaters (Industrial, Commercial, and
Institutional) (NOX).
K. Wineries (VOC) .............................................
L. Steam Enhanced Crude Oil Production Well
Vents (VOC).
M. Residential Space Heating (NOX) ................
N. Agricultural Internal Combustion Engines
(PM–10, NOX).
Residential Wood Combustion 8 ........................
EPA action
Approved 8/1/07, 72 FR 41894.
Not adopted by District.
Under EPA Review.
4352—Solid Fuel Fired Boilers, Steam Generators, and Process Heaters.
4307—Boilers, Steam Generators, and Process Heaters 2.0 to 5.0 mmBtu.
4308—Boilers, Steam Generators, and Process Heaters 0.075 to 2.0 mmBtu.
4694—Wineries ................................................
4401—Steam Enhanced Crude Oil Production
Well Vents.
4905—Natural Gas Fired, Fan-type, Residential Central Furnaces.
4702—Internal Combustion Engines Phase 2
Approved 5/30/07, 72 FR 29886.
4901—Residential Wood Burning ....................
Approved 9/30/03, 68 FR 56181.
Approved 5/30/07, 72 FR 29886.
Approved 5/30/07, 72 FR 29886.
Under EPA Review.
Under EPA Review.
Approved 5/30/07, 72 FR 29886.
Approved 1/10/08, 73 FR 1819.
7 On May 26, 2004, EPA approved the 2003 PM–10 Plan including commitments for new District rules. See 2003 PM–10 Plan, Table 4–9 List
of New District Commitments. The commitments for PM–10 and NOX reductions were approved as meeting BACM and the commitments for
other pollutants (SOX, VOC) were approved as SIP strengthenings. See 69 FR 30006, 30035 and 69 FR 5412, 5423. The District subsequently
amended the 2003 PM–10 Plan and revised Chapter 4 Control Strategy in May 2005; however, the amendments were not submitted to EPA.
The EPA-approved commitments are those found in the version of the 2003 PM–10 Plan adopted by the District on December 18, 2003.
8 In its comment letter, EJ lists Residential Wood Combustion as a commitment from the 2003 PM–10 Plan; however, it was an adopted measure and not a commitment. We have included it in our Table for completeness in addressing EJ’s comments.
In addition to the rules in Table 1, the
2007 Plan cites reductions from
additional rules that were not included
in the 2003 PM–10 Plan’s commitments.
All of these additional rules have been
adopted and submitted to EPA by the
State and most have been approved by
EPA. Table 2 below provides a summary
of EPA actions on these additional rules
based on the ‘‘Errata, 2007 PM–10
Maintenance Plan and Request for
Redesignation.’’
TABLE 2—SUMMARY OF EPA ACTION ON ADDITIONAL RULES IDENTIFIED BY 2007 PLAN
Rule title
4103 .............................
Open Burning (VOC & NOX) .......................................................................................................
4305 .............................
Boilers, Steam Generators, and Process Heaters (NOX) ...........................................................
4409 .............................
Components Serving Light Crude Oil or Gases at Production Facilities (VOC) ........................
4451 & 4452 ................
4570 .............................
4604 .............................
Components at Petroleum Refineries (VOC).
Confined Animal Feeding Operations (VOC) ..............................................................................
Can and Coil Coating Operations (VOC) ....................................................................................
9310 .............................
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Rule #
School Bus Fleets (NOX) ............................................................................................................
Thus, contrary to EJ’s comment, most
of the rules identified in the 2007 Plan
have been approved by EPA as federally
enforceable elements of the SIP. EPA is
continuing to process the remainder of
the State’s submitted rules.
Comment 9: EJ concludes that because
the air quality improvements are
premised on ignoring multiple
violations of the PM–10 standard and
fewer than one quarter of the rules the
District relies on for reductions are an
enforceable part of the SIP, EPA cannot
reasonably attribute air quality
improvements to permanent and
enforceable emission reductions.
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EPA action
Response 9: See above responses to
comments 1, 3, 4, 6, 7 and 8.
D. Area Has Met All Applicable CAA
Section 110 and Part D Requirements
Comment 10: EJ asserts that the
District fails to comply with CAA
section 107(d)(3)(E) because it has not
met all applicable requirements under
section 110 and part D. EJ says that in
addition to the contingency measure
requirement, the District has not met the
section 189(b)(1)(B) BACM requirement
because BACM were required to be
implemented by January 8, 1993 and
EPA has still not approved most of the
PM–10 rules relied on (as a result of the
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Approved 4/11/06, 71
FR 18216.
Approved 5/18/04, 69
FR 28061.
Approved 3/23/06, 71
FR 14652.
Under EPA Review.
Approved 5/19/06, 70
FR 28826.
Under EPA Review.
2003 PM–10 Plan commitments) as
being BACM-level controls.
Response 10: As noted above, in its
October 30, 2006 attainment
determination EPA suspended the
172(c)(9) contingency measure
requirement and as a result it is no
longer an applicable part D requirement.
71 FR 63642, 63663; 73 FR 22307,
22313. In any event, as set forth above
(see response to comment 2),
independent of its suspension, the
contingency measure requirement is not
an applicable requirement for purposes
of redesignation.
With respect to the section
189(b)(1)(B) BACM requirement, as
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discussed in our proposed rule, EPA
determined that this requirement was
met for the SJV nonattainment area in
our approval of the 2003 PM–10 Plan.
See 69 FR 30006, 30035. (‘‘EPA is
approving the RACM/BACM
demonstration for all significant PM–10
and NOX sources in the SJV as meeting
the requirements of sections 189(a)(1)(C)
and 189(b)(1)(B)’’). In the 2003 PM–10
Plan the District addressed the BACM
requirement by providing enforceable
commitments to implement BACM rules
in the future rather than already
adopted rules. During the rulemaking on
the 2003 PM–10 Plan, EJ argued that
until the relevant BACM requirements
are adopted and no longer subject to
change in the rule development process
for each of these source categories, EPA
could not conclusively determine that
the plan provides for the
implementation of BACM/BACT for all
significant sources of PM–10 and PM–
10 precursors. In rejecting that argument
we stated that:
[s]ection 189(b)(1)(B) requires that serious
area PM–10 plans include ‘[p]rovisions to
assure that the best available control
measures for the control of PM–10 shall be
implemented no later than 4 years after the
date the area is classified (or reclassified) as
a Serious Area.’ Nothing in this language
either requires a state to have adopted
controls in place before a SIP revision can be
approved into its PM–10 plan or forbids the
adoption of an enforceable commitment to
meet the statute’s BACM [footnote omitted]
requirement.
Id. at 30013. We further stated, in fully
approving commitments as meeting the
Act’s BACM requirement that:
[c]onsistent with this statutory language,
EPA has historically determined that an
enforceable commitment to adopt and
implement BACM in a SIP meets this
statutory requirement since it constitutes a
‘provision to assure that BACM is
implemented’ by a fixed deadline. As a
result, the commenters’ complaint that ‘[b]y
definition the plan fails to implement BACM/
BACT for all source categories for which no
developed control measures exist’ has no
merit since the statute itself does not impose
such a requirement. Because the statute does
not define what is a ‘provision to assure
BACM is implemented,’ EPA may adopt an
interpretation reasonably accommodated to
the purpose of the statutory provision.
Chevron U.S.A., Inc. v. Natural Resources
Defense Council, 467 U.S. at 842–44.
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Id. at 30013–30014. In conclusion we
stated that:
In accepting enforceable commitments to
meet the requirements of section 189(b)(1)(B),
however, EPA has required states to
undertake an analysis to ensure that the
regulation ultimately adopted pursuant to the
commitment will represent a BACM level of
control. As we describe in our proposed rule,
a state must determine the technical and
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economic feasibility of potential control
measures for each of the significant source
categories. 69 FR 5412, 5418. Thus the
measure that is the subject of a commitment
must describe generally the type and level of
control to be adopted.
Moreover, once the ultimate control
measure is adopted and submitted to EPA,
the Agency undertakes an additional
evaluation to ensure that that measure meets
the statute’s BACM requirements. See, e.g.,
the Arizona rulemakings in which EPA
initially approved as RACM [footnote
omitted] a requirement in a state statute to
adopt and implement best management
practices for agricultural operations and
subsequently determined that the rules
adopted pursuant to the statute represented
RACM/BACM. 64 FR 34726 (June 29, 1999);
66 FR 51869 (October 11, 2001); 67 FR 48718
(July 25, 2002).
Id. at 30014. EPA’s interpretation and its
full SIP approval of the BACM
requirement was not challenged. EPA
may rely on prior SIP approvals in
approving a redesignation request.
Calcagni memorandum at 3;
Southwestern Pennsylvania Growth
Alliance v. Browner, 144 F.3d. 984. 989–
990 (6th Cir. 1998); and Wall v. EPA,
265 F.3d 526 (6th Cir. 2001). Finally we
note that EPA has approved many of the
rules submitted by the State as meeting
a BACM level of control. See the Federal
Register notices listed in Tables 1 and
2 above in which we approve SJVAPCD
PM–10 and NOX rules.
Comment 11: EJ also claims that the
District has failed to submit to EPA a
demonstration that the quantitative
milestones as required by CAA section
189(c)(1) and (c)(2) and the section
189(d) 5 percent requirement have been
met. EJ also claims that the District has
not met its commitment to update and
improve the 2003 PM–10 Plan by March
2006.
Response 11: CAA section
107(d)(3)(E)(v) requires that a state
seeking redesignation of an area to
attainment must have met all
requirements applicable to the area
under section 110 and part D. In
interpreting this requirement EPA has
stated that ‘‘any requirements that came
due prior to submittal of the
redesignation request must be fully
approved into the plan at or before the
time EPA redesignates the area.’’
Calcagni memorandum at 5. Sierra Club
v. EPA, 375 F.3d 537 (7th Cir. 2004).
EPA has approved the 2003 PM–10
Plan’s RFP demonstration as meeting
the requirements of 172(c)(2) and
189(c)(1) and has approved the plan as
meeting the quantitative milestones
requirement in section 189(c)(1). 69 FR
30006, 30034. Also, as we explained in
our 2006 attainment finding, we believe
that once an area attains the NAAQS the
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requirements of section 189(c)(2) with
respect to milestones no longer applies
under the Agency’s Clean Data Policy.
71 FR 63642, 63646–63647. We also
explained in that rulemaking the
application of the Clean Data Policy to
PM–10. See 71 FR 40952, 40954–40955
and 71 FR 63642, 63643–63645. Apart
from the Clean Data Policy, for an area
that has attained the standard and is
eligible for redesignation, the
requirements for milestone
demonstrations under section 189(c)
have no further meaning or function.
Therefore the District was not required
to submit milestone demonstrations
pursuant to section 189(c).
In addition, EPA approved a
commitment in the 2003 PM–10 Plan by
the State to submit a SIP revision by
March 31, 2006 based on a mid-course
review to determine whether the level of
emission reductions in the plan is
sufficient to attain the PM–10 standards.
69 FR 30006, 30035. EPA approved this
commitment as part of the Plan’s
attainment demonstration. See 69 FR
5412, 5429. While the SJVAPCD
adopted a mid-course review SIP
addressing the quantitative milestone
reporting requirement and mid-course
review SIP commitment and submitted
the SIP to the State, the State has not
submitted the mid-course review SIP to
EPA. Nevertheless, EPA’s full approval
of the attainment demonstration in the
2003 PM–10 Plan fully satisfies the
requirement of CAA section
107(d)(3)(E)(v).
Moreover, EPA has determined that
the SJV area attained the PM–10
standard in 2005, and continues to
attain the standard. The mid-course
review requirement is not a requirement
under section 110 or Part D, and
therefore is not an applicable CAA
requirement for purposes of
redesignation. Furthermore, even if it
were, the requirement for a mid-course
review was approved as part of the
attainment demonstration. Therefore,
because EPA has determined that the
SJV area is attaining the PM–10
standard, a submission under the midcourse review provision would not be
required for purposes of redesignation.
57 FR 13498, 13564; Clean Data Policy.
Comment 12: EJ claims that EPA
misinterprets an October 14, 1994
memorandum from Mary Nichols, EPA,
entitled ‘‘Part D NSR Requirements for
Areas Requesting Redesignation to
Attainment’’ as allowing the District to
replace its new source review (NSR)
program with a prevention of significant
deterioration (PSD) program. EJ quotes
the memorandum as saying that ‘‘the
part D program may be replaced by the
corollary PSD program, if it is shown
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through the maintenance demonstration
that the area will maintain without part
D NSR.’’ EJ asserts that here neither EPA
nor the District has made any such
demonstration and claims that this is
especially worrisome in light of EPA’s
recent proposed approval of revisions to
the District’s NSR program exempting
‘‘so-called minor agricultural sources
such as industrial dairy operations.’’
Response 12: First, the commenter
overlooks the fact, enunciated in our
proposed rule, that EPA has previously
fully approved the NSR program for the
SJV area. We also noted that EPA has
recently proposed approval of some
revisions to the NSR rule. 73 FR 22307,
22313. EJ’s citation to the October 14,
1994 memorandum from Mary Nichols,
EPA, entitled ‘‘Part D NSR
Requirements for Areas Requesting
Redesignation to Attainment’’ (Nichols
memorandum) is misdirected. The
Nichols memorandum’s discussion of
the need to demonstrate maintenance
without fully approved NSR addressed
the situation, not the case here, where
an area’s NSR rule has not been
approved. Moreover, as our proposed
rule explained, even though EPA
previously approved the NSR rule, such
approval is not a prerequisite to
finalizing our approval of the State’s
redesignation request. Id. If an area does
not have a fully approved NSR program,
it can still be redesignated if it shows
maintenance without NSR in effect. The
2003 PM–10 Plan and 2007 Plan do not
rely on reductions from the area’s NSR
program. Nothing in the plans’
inventories or estimated emissions
reductions indicates any reliance on
NSR program reductions. Thus, the
SJVAB area will maintain the NAAQS
without NSR. This is consistent with the
provisions of the Nichols memorandum.
Finally, we note that while the PSD
requirements will apply once the area
has been redesignated to attainment, the
District’s SIP-approved NSR rule will
continue to apply with respect to PM–
10 until EPA approves a revised NSR
rule.
E. Maintenance Plan
Comment 13: EJ maintains that even
if all of the other issues it has raised
with respect to the redesignation were
remedied, EPA cannot approve the
redesignation request because the
maintenance plan is flawed and cannot
be approved. EJ concludes that EPA’s
decision to approve the maintenance
plan without the requisite analysis and
without meeting the basic requirements
laid out in the Calcagni memorandum
leaves little for EJ to comment upon
and, as such, is the very definition of
arbitrary and capricious. EJ believes that
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EPA’s obligation is to provide not just
its legal conclusions but the facts and
rationale that support them.
Response 13: EPA disagrees. Our
proposed rule lays out all of the
requirements for maintenance plans
found under the CAA and the Calcagni
memorandum and sets forth the
Agency’s analysis of how the 2007 Plan
meets each of those requirements. 73 FR
22307, 22313–22315. In addition, the
2007 Plan itself addresses in detail the
requirements in the Calcagni
memorandum. Thus EJ’s contention that
EPA’s discussion of the maintenance
plan left them ‘‘very little’’ to comment
on is without basis.
Comment 14: EJ asserts that the 2005
emissions inventory is insufficient to
identify the level of emissions in the
area because the continuing PM–10
problem is the result of direct PM–10
emissions during the fall rather than
secondary wintertime NOX emissions
and the direct PM–10 inventory is
expected to increase over the next 10
years. EJ states that EPA’s claim that
increasing direct PM–10 emissions are
offset by a larger decrease in the NOX
inventory demonstrates a lack of
understanding of the PM–10 problem in
the SJV nonattainment area because
reducing secondarily formed PM–10
does nothing to reduce the ongoing
direct PM–10 problems. EJ concludes
that since the maintenance
demonstration is based on an inventory
that is insufficient to attain the NAAQS,
EPA cannot find that the plan will
maintain healthful air for 10 years
following redesignation.
In a footnote to its comment above
regarding the emissions inventory for
the maintenance plan, EJ claims that
prior to 2004 the District had never
asked EPA to waive PM–10 data but in
the past 4 years it has been asked to
waive 11 separate events, 10 of them
after the Agency’s original attainment
finding. EJ states that if windy days are
this common EPA and the District must
accept that the SJV nonattainment area
has a windblown dust problem and they
must do more to control it. EJ states that
an event is only exceptional if it is not
expected to recur on a regular basis.
Response 14: As discussed in our
proposed rule, the Calcagni
memorandum provides that a state
should provide an attainment emissions
inventory to identify the level of
emissions in the area sufficient to attain
the NAAQS and, where the state as here
has made an adequate demonstration
that air quality has improved as a result
of the SIP (see above responses to
comments 3 through 4 and 6 through 8),
the attainment inventory will generally
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be an inventory of actual emissions at
the time the area attained.
The 2007 Plan does exactly what the
Calcagni memorandum recommends
and selects the 2005 PM–10 and NOX
inventories as the attainment emission
inventories because the SJV area
attained the standard in 2005. 73 FR
22307, 22314 and 71 FR 63642. The SJV
area relies on reductions of both NOX (a
PM–10 precursor) and directly emitted
PM–10 sources to achieve attainment.
2003 PM–10 Plan at ES–9 through ES–
10, Chapters 2, 4 and 5; 69 FR 5412,
5414 and 69 FR 30006, 30007. Analysis
of ambient air quality data for the SJV
area shows that it experiences the most
frequent and severe exceedances from
October through January during
stagnant weather conditions (i.e., low
wind speeds that are unable to disperse
the PM–10).9 Both direct PM–10 and
secondary PM–10 (formed by reactions
with NOX ) occur during this time.
October and November exceedances are
dominated by direct PM–10 emissions
and December and January are
dominated by secondary PM–10 such as
ammonium nitrate (formed when NOX
reacts with ammonia and other
components); however, the reduction of
both direct PM–10 and NOX is necessary
for reducing ambient PM–10 levels
throughout the year. 2003 PM–10 Plan
at ES–9 through ES–10 and 5–6 through
5–7. Thus, EPA’s belief that the slight
increase in PM–10 emissions of 284 tpd
in 2005 to 290 tpd in 2020 is
insignificant when compared to the
substantial NOX decreases of 606 tpd in
2005 to 328 tpd in 2020 is based on an
understanding that high PM–10 levels
in the SJV area are caused by both direct
PM–10 and precursor NOX emissions. In
addition, consistent with the Calcagni
memorandum, the modeled
maintenance demonstration is primarily
based on modeling similar to the
modeling used for the 2003 PM–10 Plan.
73 FR 22307, 22314. Finally, contrary to
EJ’s comments, there is no ongoing
direct PM–10 problem in the SJVAB as
we have determined that the area has
attained the PM–10 standard. 71 FR
63642 and 73 FR 14687. See also
response to comment 1.
EJ’s comment in footnote 3 of its letter
does not appear to be related to the
inventory or any other provision of the
maintenance plan in the 2007 Plan or
the maintenance plan requirement of
CAA section 107(d)(3)(E)(iv). Rather it
appears to be an expansion of EJ’s
argument that the SJV area has not in
fact attained the PM–10 standard. In this
9 As discussed in our attainment affirmation and
proposed rule, unusually high winds can also cause
exceedances. 73 FR 14687 and 73 FR 22307, 22311.
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regard, see response to comment 1
above. Notwithstanding , EPA notes that
not all of the exceptional event days in
the past five years in the SJV area have
been due to high winds. Of the eleven
exceptional event days, seven were
caused by high wind events and the
remaining four by construction,
improper monitor siting and fireworks.
Comment 15: EJ states that it is not
clear whether the modeling takes into
account the September 2004 and
November 2005 exceedances EPA has
conceded but if it does not then the
modeling for the maintenance plan is
flawed because it fails to include these
higher values in its projections.
Response 15: As discussed in our
proposed rule, 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. 73 FR 22307, 22314–22315.
See also Calcagni memorandum at 9 and
Wall v. EPA, 265 F.3d 426 (6th Cir.
2001). While only required to use one of
these methods, the SJVAPCD showed
both with emissions inventory and
modeling that the area would maintain
the standard for at least ten years after
redesignation, in accordance with
section 175A. For areas such as the SJV
that used modeling for their attainment
demonstrations, the same level of
modeling should be used for the
maintenance demonstrations. The 2007
Plan uses Chemical Mass Balance (CMB)
and rollback to demonstrate
maintenance of the 24-hour PM–10
standard until 2020 which is consistent
with the modeling performed for the
2003 PM–10 Plan. 73 FR 22307, 22314;
2007 Plan at 6–11. The modeling
involves selecting a representative day
for each location, determining the
speciation data for the site based on
analysis of the monitoring filters and
sources in the area and determining the
emissions reductions that are necessary
or that will be achieved due to
emissions reductions from implemented
rules.
The 2007 Plan’s maintenance
demonstration modeling was based on
the highest episodes during the most
recent attainment year at the time, 2006.
The District selected representative peak
winter days for each of the monitors in
the SJVAB for modeling, and used the
observed values from those days as the
basis of its modeling exercise. In
addition, fall episode days were
included for several monitors. Table 2 of
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the 2007 Plan summarizes the episode
values and the 2020 projections.
One of the objectives in determining
appropriate representative episodes is to
choose those days that are
approximately as severe as the design
value for the modeled pollutant. The
design value is based on three years of
monitoring data, or in this case, 2004
through 2006, and depends on the
frequency and completeness of recorded
values. In addition, for PM–10, the
design values are generally based on
FRM data, but FEM data can also be
used; however, as noted in footnote 3
above, data from different monitoring
instruments are not combined.
The representative days selected for
modeling are consistent with the design
values for the Corcoran and Bakersfield
sites where the September 2004 and
November 2005 values were measured.
For the Corcoran FRM, the design value
is 140 µg/m3, based on a calculation that
includes and explicitly accounts for the
217 µg/m3 measured in September
2004.10 This value is very close to, and
supports the selection of, the two
representative high episode values in
the 2007 Plan for Corcoran: A 136 µg/
m3 for the winter episode and a 137 µg/
m3 for the fall episode. The small
differences between the design value of
140 µg/m3 and the selected winter and
fall episode values is not an issue
because the projected maintenance
levels are well below the 24-hour PM–
10 standard of 150 µg/m3. 2007 Plan at
Table 2. The Bakersfield FEM does not
have a complete set of data from 2004
through 2006, and therefore a design
value for this time period cannot be
calculated based on the FEM data.
However, the 2004–2006 PM–10 design
value for Bakersfield using the data
collected with the FRM monitor would
be 154 ug/m3.11 This concentration is
consistent with the values of 153 ug/m3
and 154 µg/m3 measured during the
representative modeled episodes
included in the 2007 Plan for
Bakersfield. Therefore, the September
2004 and November 2005 exceedances
to which EJ refers in its comment were
10 If we assume that the September 2004
exceedance is not flagged, the highest recorded PM–
10 values from 2004 through 2006 are: (1) 217 µg/
m3 on September 3, 2004; (2) 140 µg/m3 on October
26, 2006; and (3) 139 µg/m3 on October 15, 2004.
Since the Corcoran FRM operates on a one-in-three
day schedule, the design value is based on the
second highest recorded PM–10 value, or 140 µg/
m 3.
11 The design value for Bakersfield is calculated
using the FRM data set from 2004–2006. The design
value in this case would be the highest non-flagged
value for the three year period, 154 µg/m3 measured
on December 7, 2006.
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taken into account in the 2007 Plan’s
maintenance demonstration modeling.
Comment 16: While EJ is glad that the
District plans to continue operation of
its PM–10 monitoring network, EJ is
troubled that the District suggests in its
2008 ‘‘Ambient Air Monitoring Network
Plan’’ that it may reduce the frequency
of its monitoring. EJ hopes that the
District will strengthen its network
because EJ continues to believe that the
current network does not adequately
represent the west side communities
and the near-highway areas of high
concentration and that more monitoring
is required.
Response 16: In 2003, EPA evaluated
the adequacy of the monitoring network
for the SJV area and concluded that it
meets all the applicable statutory and
regulatory requirements. See 69 FR
30006, 30033 and ‘‘Evaluation of the
Adequacy of the Monitoring Network
for the San Joaquin Valley, California for
the Annual and 24–Hour PM–10
Standards,’’ Bob Pallarino, EPA,
September 22, 2003. We reaffirmed the
adequacy of the network in our 2006
determination of attainment for the SJV
area. 71 FR 63642, 63648–63658.
With regard specifically to monitoring
frequency, EPA regulations require
minimum frequencies for manual PM–
10 and PM–2.5 samplers at designated
state or local air monitoring stations
(SLAMS) sites. See 40 CFR 58.12. On
October 17, 2006 EPA revised its
monitoring regulations to require air
monitoring agencies to perform an
assessment of their monitoring networks
every five years according to guidance
issued by EPA. See 71 FR 61299 and 40
CFR 58.10(d). The first monitoring
network assessment required by this
regulation must be submitted to EPA by
July 1, 2010. Agencies are directed to
make changes to their monitoring
networks based in part on the results of
these network assessments. Such an
assessment in the SJVAB area may
result in a requirement that the District
increase the sampling frequency of
certain PM–10 monitors sited to record
the maximum concentrations of PM–10
pollution. See 40 CFR 58.12(e).
Most manual PM–10 samplers in the
SJV monitoring network currently
operate at the minimum required
frequency of once every six days, except
for Corcoran which operates manual
PM–10 samplers once every three days.
The District has exceeded this required
sampling frequency by operating
continuous FEM monitors, which
produce a 24-hour average PM–10
concentration every day, at three
locations in the SJVAB area, Tracy,
Corcoran and Bakersfield. According to
the District’s 2008 ‘‘Ambient Air
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Monitoring Network Plan,’’ the
Corcoran and Bakersfield-Golden State
Highway sites are two of the four PM–
10 monitoring sites located to record the
highest PM–10 concentrations in the
SJVAB area.12 Therefore, the District has
already proactively increased the
sampling frequency at two high
concentration sites to the maximum
frequency possible.
Comment 17: EJ believes that the
contingency measure provision in the
maintenance plan is much too weak and
cannot be approved. EJ states that the
provision relies first and foremost on
trying to excuse any future violation
under the EER and then, in the event of
any post-redesignation violations, on
seeing if there are any estimated
reductions achieved that were not
counted towards the attainment
demonstration that can be used to
‘‘cover’’ the violation. EJ does not
believe this approach makes sense
because if an area is violating the
standard, there are no ‘‘extra’’
reductions because all of the reductions
are by definition not working. EJ
believes that while EPA may accept this
gaming in the context of RFP
demonstrations such an approach
would be illegal and arbitrary when real
ambient violations are being monitored.
EJ believes that the District should
adopt the approach suggested in the
Calcagni memorandum which sets
indicators that trigger contingency
provisions before a violation occurs
which would avoid NAAQS violations
and not just come up with on-paper
‘‘covers’’ for those violations.
Response 17: Under CAA section
175A(d), maintenance plans must
contain ‘‘such contingency provisions as
the Administrator deems necessary to
assure that the State will promptly
correct any violation of the standard.’’
The Calcagni memorandum states that
‘‘EPA will review what constitutes a
contingency plan on a case-by-case
basis. At a minimum, it must require
that the State will implement all
measures contained in the Part D
nonattainment plan for the area prior to
redesignation. * * * ’’ Calcagni
memorandum at 12–13. The
memorandum also makes clear that a
monitored violation of the standard is
appropriate to serve as the indicator or
trigger for contingency measures.
Id. at 12.
EJ’s statement that the contingency
provisions of the 2007 Plan ‘‘relies first
and foremost’’ on trying to excuse any
future violation under the EER is
misleading. The 2007 Plan selects an
12 The other two sites are the Fresno-First Street
site and the Stockton-Hazelton site.
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action level or trigger based on an
exceedance of the PM–10 NAAQS of
155 micrograms per cubic meter (µg/
m3).13 2007 Plan at 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. In our proposed rule we
explained why we believe that an
exceedance of 155 µg/m3 is an
appropriate trigger:
The SJVAB has several continuous PM–10
monitors, and a single measurement of 155
µg/m3 at one of these monitors would not
constitute a violation of the PM–10 NAAQS.
Even if a measurement of 155 µg/m3 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.
73 FR 22307, 22315. Thus the
contingency plan makes clear that
determining whether an exceedance of
the PM–10 standard is due to an
exceptional event is part of determining
whether a violation of the standard
actually occurred, which would require
corrective actions. In other words, we
concluded that the 2007 Plan’s action
level or trigger, including the exclusion
of exceedances caused by exceptional
events, meets the statutory mandate that
the contingency provisions ‘‘correct any
violation of the standard.’’ Because it is
clearly part of the action level or trigger,
and not the corrective actions to be
undertaken in the event of a violation,
it is not accurate to conclude, as EJ does,
that the contingency plan relies ‘‘first
and foremost’’ on the use of the EER.
Moreover, since an exceedance, which
is not necessarily a violation, triggers
the contingency measure provision, the
provision may also be used to prevent
violations of the NAAQS, and at a
minimum provides for a violation that
is determined not to be due to an
exceptional event to trigger a measure.
Once the contingency plan is
triggered, the District would determine
the possible causes of the exceedance
and determine if emissions reductions
from adopted measures that are not
needed to maintain the PM–10 NAAQS
are available to serve as contingency
measures. 2007 Plan at 16. EJ objects to
the use of these excess reductions (i.e.,
those not relied on in the maintenance
demonstration) when ambient
concentrations are being monitored.
13 An exceedance is defined as a daily value that
is above the level of the 24-hour standard (150 µg/
m3) after rounding to the nearest 10 µg/m3 (i.e.
values ending in 5 or greater are to be rounded up).
Thus, a recorded value of 154 µg/m3 would not be
an exceedance since it would be rounded to 150 µg/
m3 whereas a recorded value of 155 µg/m3 would
be an exceedance since it would be rounded to 160
µg/m3. See 40 CFR part 50, appendix K, section 1.0.
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Initially we note that EPA has long
approved contingency provisions that
rely on reductions from measures that
are already in place but are over and
above those relied on in the attainment
and RFP demonstrations under CAA
section 172(c)(9). See, e.g., 62 FR 15844
(April 3, 1997); 62 FR 66279 (December
18, 1997); 66 FR 30811 (June 8, 2001);
66 FR 586 and 66 FR 634 (January 3,
2001). We discussed this interpretation
of section 172(c)(9) in our final PM–2.5
implementation rule. See 72 FR 20586,
20642–20643 (April 25, 2007). This
interpretation has also been upheld in
LEAN v. EPA, 382 F.3d 575 (5th Cir.
2004), and the court in that case set
forth in detail the reasoning for
accepting excess reductions from
already adopted measures as
contingency measures.
In addition to being triggered by a
failure to meet RFP, contingency
measures under section 172(c)(9) are
triggered when EPA determines that an
area has failed to attain a NAAQS.
Determinations of whether an area has
attained a NAAQS (see, e.g., section
188(b)(2); 71 FR 40952) are based on
monitored concentrations. Likewise,
here, a determination of whether the
action level has been reached is based
on monitored concentrations. Therefore
our interpretation that excess emission
reductions can appropriately serve as
section 172(c)(9) contingency measures
is equally applicable to section 175A(d)
contingency measures.
Furthermore, section 172(c)(9) is
considerably less flexible than section
175A(d) in that under the former
provision contingency measures are
required to be fully adopted measures
that will take effect without further
action by the state, whereas this is not
a requirement in order for the
maintenance plan to be approved.
Moreover, section 175A(d) grants
considerably more discretion to EPA in
determining whether to accept
contingency provisions in maintenance
plans (maintenance plans must contain
‘‘such contingency provisions as the
Administrator deems necessary to
assure that the State will promptly
correct any violation of the standard.’’
(Emphasis added). In addition, the
Calcagni memorandum at 12–13 states
that a contingency plan under section
175A(d) ‘‘[a]t a minimum must require
that the State will implement all
measures contained in the Part D
nonattainment plan for the area prior to
redesignation. * * * ’’ The 2007 Plan so
provides and goes well beyond this
minimum threshold.
The U.S. Court of Appeals for the
Sixth Circuit addressed the issue of the
adequacy of reductions from already
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adopted measures in the context of
section 175A(d) contingency measures
in a maintenance plan for Cuyahoga
County, Ohio. Greenbaum v. EPA, 370
F.3d 527 (6th Cir. 2004).14 There EPA
had approved section 172(c)(9)
contingency measures into the SIP in
1996 as part of the State’s moderate area
PM–10 nonattainment plan. In
approving these measures EPA found
that they provided for emission
reductions following any prospective
determination that the SIP failed to
provide for timely attainment of the
NAAQS. In 2000, Ohio submitted a
redesignation request with a
maintenance plan that included as
section 175A(d) contingency provisions
the already approved section 172(c)(9)
contingency measures. Among other
things, the petitioners argued that the
CAA does not authorize EPA to use
other measures outside the maintenance
plan to assure correction of a violation.
In upholding EPA’s approval of the
redesignation, the court found that:
[t]he Administrator has been granted broad
discretion by Congress in determining what
is ‘necessary to assure’ prompt correction.
The EPA has approved Ohio’s maintenance
plan, concluding that its contingency
measures provide a means to deal with likely
violations. We do not believe that this
determination is ‘arbitrary, capricious, or
manifestly contrary to the statute.’ Chevron,
467 U.S. at 844.
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The Sixth Circuit in Greenbaum further
noted that Congress contemplated that
contingency measures need not be
sufficient to correct all violations and
that EPA and the state could rely on a
combination of factors to correct
violations. See the extensive discussion
of contingency measures in Greenbaum.
Here, the 2007 Plan looks first to
emission reductions from adopted
measures that are not needed to
maintain the PM–10 NAAQS to serve as
section 175A(d) contingency measures.
If these emission reductions prove to be
insufficient to correct the violation, the
District commits to proceed with
identifying control measures from
feasibility studies such as those found
in its 2007 Ozone Plan and Proposed
2008 PM2.5 Plan 15 (see 2007 Ozone
Plan at Table 6–2 and 2008 PM2.5 Plan
at Table 6–4) and with prioritizing
measures most relevant for reducing
PM–10 emissions. 2007 Plan at 16–17.
14 As early as 1995, EPA approved a maintenance
plan under section 175A that included contingency
provisions that relied in part on measures to be
implemented prior to any post-redesignation
NAAQS violation. See 60 FR 27028, 27029 (May 22,
1995).
15 The 2008 PM2.5 Plan was adopted by the
District on April 30, 2008, approved by the State on
May 22, 2008, and submitted to EPA on June 30,
2008.
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The SJVAPCD has also provided
clarification that if additional control
measures are necessary, the SJVAPCD
will adopt and implement such
measures. Letter from Seyed Sadredin,
SJVAPCD, to Deborah Jordan, EPA,
April 17, 2008. EPA believes that the
2007 Plan’s contingency provisions
which rely in part on emissions
reductions from adopted measures not
needed to maintain the PM–10 NAAQS
to correct any PM–10 violation are
consistent with the Agency’s policies
and with the statute. As the court in
Greenbaum observed, Congress has
expressly delegated to EPA the authority
to determine what contingency
measures are necessary. Here, EPA has
determined that the contingency
measures, which include both the
potential for emission reductions from
already adopted measures and from
measures to be adopted, clearly are
sufficient.
Finally, with respect to EJ’s
preference, suggested in the Calcagni
memorandum, that the contingency
plan for the SJVAB area set indicators
that trigger contingency provisions
before a violation occurs, we note again
that the memorandum provides that
contingency provisions are to be judged
on a case by case basis. See also
Greenbaum. With the exception of the
minimum requirement mentioned
above, the Calcagni memorandum is not
prescriptive and allows for considerable
latitude as to what constitutes an
adequate contingency plan. The
Calcagni memorandum itself provides
that a violation of the standard is an
appropriate trigger for contingency
measures. Calcagni memorandum at 12.
See also Greenbaum. It is a common
practice in maintenance plans to
provide that a violation will trigger the
requirement for a contingency measure
to be implemented. Moreover, as
pointed out above, under the
contingency measure provisions, a
monitored exceedance of the standard
that does not itself constitute a violation
(e.g., at a continuous monitor or a onein-three day FRM monitor) could trigger
a contingency measure prior to a
violation occurring.
F. Revision of Boundary Designation
Comment 18: EJ maintains that the
portion of the San Joaquin Valley that
EPA now proposes to split off was
designated as part of the SJV
nonattainment area because, as
provided in CAA section 107(d)(1)(A), it
was part of the geographic area ‘‘that
does not meet (or that contributes to
ambient air quality in a nearby area that
does not meet) the national primary or
secondary air quality standard for that
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pollutant.’’ EJ states that EPA makes no
attempt to explain how circumstances
have changed to justify the removal of
this portion of the designated
nonattainment area. EJ notes that the
SJV area includes other high-elevation
areas that are located above the
inversion layer and that whether a
community is above or below the
inversion layer is irrelevant because
these areas are part of the Valley and
part of the same air basin polluted by
emissions generated in the Valley.
Response 18: As discussed in our
proposed rule, on January 31, 2008
California requested a boundary
redesignation splitting the SJV
nonattainment area into two separate
nonattainment areas, the SJVAB and
East Kern. Section 107(d)(3)(D) of the
CAA authorizes the State to submit to
EPA a revised designation of any area
and EPA is required to approve or deny
it within 18 months of receipt of a
complete State submittal. The type of
revised designation that the State of
California requested involves a
boundary change only and does not
involve a change in status (e.g., from
‘‘nonattainment’’ to ‘‘attainment’’ or
‘‘unclassifiable’’) of any area. Our
criteria for evaluating the State’s request
are discussed in our proposed rule.
In general, the State has provided a
compelling technical justification for
splitting the nonattainment area which
includes an evaluation of the differences
in jurisdiction, geography, population
and degree of urbanization, employment
and traffic/commuting patterns,
emissions and air quality. 73 FR 22307,
22308–22310. EJ notes that there are
other high elevation areas in the SJV
nonattainment area; however, the State
has not made a request to revise any
other boundaries. In addition, as
discussed in our proposed rule, the
SJVAB and East Kern areas are in
separate air basins and do not have the
same mix of air pollution sources. Id.
EPA continues to believe that it should
grant the State’s request for a revised
designation splitting the SJV
nonattainment area into two PM–10
nonattainment areas, the SJVAB area
and the East Kern area for the reasons
set forth in the proposed rule and in this
response.
Comment 19: A commenter states that
while the proposal to separate the
western portion of the KCAPCD is clear
and compelling, the commenter is
concerned about environmental justice
issues for the East Kern area. The
commenter states that if the purpose of
the separation is to clean-up one area
and ignore the other industrialized area
with the State prison, then EPA is not
following its ethics concerning
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environmental justice. The commenter
states that communities with prisons
serve as a target of environmental
neglect and should not be abandoned
from environmental laws and
attainment requirements and should not
be forgotten by EPA.
Response 19: EPA’s final action to
split the SJV nonattainment area into
two nonattainment areas does not relax
any requirements. EPA is also approving
enforceable commitments for the East
Kern area that will ensure progress in
meeting CAA requirements for the area.
These commitments include the
installation of a FRM/FEM 16 and
submittal of a SIP addressing applicable
CAA requirements if the monitor
violates the PM–10 standard. 73 FR
22307, 22317. In the meantime, the
existing data from the IMPROVE
monitor, although not a FRM or FEM,
do not indicate an air quality problem
in East Kern—rather they show levels
that are consistently significantly below
the standard. See id. at 22310 (‘‘* * *
IMPROVE monitor has, since February
2000, consistently measured PM–10
concentrations far below the PM–10
standard.’’).
With respect to the commenter’s
concerns for fair treatment of the
inhabitants of East Kern, EPA is taking
steps to assure that the East Kern area
will not be forgotten by EPA, and no
community in that area will be
‘‘abandoned from environmental laws
and attainment requirements.’’ EPA is
committed to meeting the goals of
environmental justice and is equally
concerned for the populations of both
the SJVAB and East Kern areas. There is
no basis for concluding that the
population of East Kern is exposed to
ongoing levels above the standard, and
EPA and the State have worked to
provide assurances that the area will be
required to conduct more
comprehensive monitoring and to adopt
additional requirements if needed. Thus
EPA recognizes the role of
environmental justice and is observing
its principles.
Comment 20: A commenter disagrees
with the proposed rule’s statement that
the boundary redesignation makes sense
because of the difference in chemical
composition of PM–10 between the two
areas. The commenter believes this is
not a valid statement because there are
no FRMs or FEMs in the East Kern area.
Furthermore, the commenter states that
the one IMPROVE monitor in the East
Kern area is inadequate and the
chemical composition of the SJVAB and
East Kern should not be compared until
there is an adequate monitoring system
in East Kern. In addition, the
commenter concludes that a reanalysis
of reported data must be performed
before considering attainment for the
SJVAB.
Response 20: We based our
conclusion that the SJVAB and East
Kern should be separate nonattainment
areas on multiple factors, only one of
which relates to the difference in the
types of air pollutants in the two areas.
See 73 FR 22307, 22310. While the
commenter is correct that there is no
FRM or FEM in the East Kern area, as
stated above, the State and the District
have committed to install an FRM/FEM
in the East Kern area. Pending data from
this new monitor, the IMPROVE
monitor does provide useful
information regarding the composition
of PM–10 in the area. See id. and
Attachments B and C to letter from
James N. Goldstene, CARB, to Deborah
Jordan, EPA, January 31, 2008. See also
response to comment 19. The newly
created East Kern area will retain its
nonattainment designation until the
State can demonstrate, following
assessment of data from the new
monitor, that all the applicable CAA
requirements for redesignation of the
East Kern area are met.
EPA does not agree that a reanalysis
of the reported data must be performed
before considering whether the SJVAB
area has attained the PM–10 standard.
As noted above, EPA has found that the
SJVAB area has an adequate monitoring
system on which to base such a
determination. See 69 FR 30006, 30033,
71 FR 63642, 63648 and ‘‘Evaluation of
the Adequacy of the Monitoring
Network for the San Joaquin Valley,
California for the Annual and 24–Hour
PM–10 Standards,’’ Bob Pallarino, EPA,
September 22, 2003. To demonstrate
attainment, an area must show that it
meets the standard over a three-year
period. The SJVAB area has
demonstrated attainment over three
separate 3-year periods—2003–2005,
2004–2006, and 2005–2007, and it
continues to attain the standard.
16 Currently there is no FRM or 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. Pursuant to its commitment,
CARB has purchased the new monitor and has
secured permission from the Bureau of Land
Management to install it next to the existing
IMPROVE monitor.
G. Miscellaneous Comments
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Comment 21: A commenter states that
there are several gaps in evaluating the
PM–10 data for the SJVAB from 1990 to
2004 and that given the cyclical nature
of PM–10 the downward trend should
be considered inconclusive until all
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66771
yearly averages are taken into account as
well as seasonally weighted averages.
The commenter also states that in the
proposed rule’s discussion of
meteorological conditions a lower
stability level would more likely lead to
less dispersion and higher PM–10
values. The commenter believes the
lower stability means the PM–10 levels
were overestimated and provides
information as to the unequal
distribution in the surrounding
community and who is bearing the
brunt of the higher exposures.
Response 21: In our proposed rule we
reference the expected PM–10
exceedances from 1990–1992, 1998–
2000 and 2002–2004 to show that there
has been a significant decline in
NAAQS exceedances over the past 17
years, i.e., from 1990 through 2006.
There are no data gaps; the 2007 Plan
includes data for each year. 2007 Plan
at 23–24, Figure 2. EPA believes that a
17 year period is sufficient to establish
a trend that accounts for any cyclical
changes in PM–10 data. In addition, an
evaluation of the seasonal conditions
causing PM–10 is provided in the 2003
PM–10 Plan. 2003 PM–10 Plan at ES–4
to ES–10 and Chapter 2.
EPA examined meteorological data,
including information about
atmospheric stability, wind speeds,
precipitation and temperature in order
to determine if there were any
unusually favorable meteorological
conditions that would cause PM–10
exceedances. EPA determined that
overall there was no consistent pattern
of favorable meteorology. 73 FR 22307,
22312; responses to comments 3 and 6
above.
For the SJVAB area, it has been
determined that on an annual average
basis, unstable conditions (or low
stability) result in dispersion of
pollutants and lower PM–10 levels and
stable conditions (or high stability)
result in a temperature inversion which
keeps emissions at the surface and leads
to higher PM–10 levels. 2007 Plan at
Appendix C. During the attainment
period of 2003 through 2006, the SJVAB
area experienced somewhat low
stability which allowed for dispersion of
pollutants and lower PM–10 levels;
however, as discussed in response to
comment 6 above, based on the analysis
of all the meteorological parameters,
EPA determined that there was no
overall pattern which favored improved
PM–10 levels.
It is not completely clear to EPA what
point the commenter is trying to make
regarding stability. EPA acknowledges,
however, that unstable conditions
combined with other factors (e.g.,
emissions) in the SJV area can lead to
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high PM–10 levels on a daily basis, as
has been seen with exceedances that
occur during high wind events. Such
exceedances however have been
excluded from regulatory consideration
under EPA’s Exceptional Events Rule.
73 FR 22307, 22310–22311 and 73 FR
14687.
Comment 22: The SJVAPCD provided
comments supporting EPA’s proposed
actions and also notes a minor
typographical error for the proposed
transportation conformity budgets found
in Table 4 for Merced County for 2005.
The SJVAPCD states that the budget
should read 39.4 tons per day and not
39.2 tons per day.
Response 22: EPA appreciates the
comments and has made the correction
in today’s final action.
redesignations and section 175A for
maintenance plans have been met for
the SJVAB area, EPA is approving the
State’s request to redesignate the newly
created serious SJVAB nonattainment
area to attainment for the PM–10
NAAQS and approving the 2007
maintenance plan for the area.
EPA is also approving the conformity
trading mechanism for the SJVAB area
and the motor vehicle emissions subarea
budgets for the attainment year, 2005,
and the maintenance year, 2020, found
in Table 3 below. The 2005 attainment
year budget replaces the current
attainment budgets from the approved
2003 PM–10 Plan. These budgets are
approved as of November 12, 2008
pursuant to section 93.118(f)(2)(iii).17
III. Final Actions
For the reasons set forth in the
proposed rule and in the responses to
comments above, EPA is taking the final
actions summarized below:
Having concluded that the State has
addressed all the necessary
requirements for a revised boundary
designation, EPA is approving the
State’s request under section
107(d)(3)(D) to revise the boundary
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.
Having concluded that the CAA
requirements of section 107(d)(3)(E) for
TABLE 3—MOTOR VEHICLE EMISSIONS SUBAREA BUDGETS 2007 PLAN *
[Tons per day]
2005
2020
County
PM–10
NOX
PM–10
NOX
Fresno ..............................................................................................................................
Kern ** ..............................................................................................................................
Kings ................................................................................................................................
Madera .............................................................................................................................
Merced *** ........................................................................................................................
San Joaquin .....................................................................................................................
Stanislaus ........................................................................................................................
Tulare ...............................................................................................................................
13.5
12.1
3.1
3.6
6.2
9.1
5.6
7.3
59.2
88.3
16.7
13.9
39.4
42.6
29.7
25.1
16.1
14.7
3.6
4.7
6.4
10.6
6.7
9.4
23.2
39.5
6.8
6.5
12.9
17.0
10.8
10.9
Total ..........................................................................................................................
60.5
314.9
72.2
127.6
* The budgets are based on attainment and maintenance of the 24-hour PM–10 NAAQS. The annual standard was revoked on December 18,
2006. See 71 FR 61144.
** MVEBs in Table 3 are only for the SJVAB portion of Kern County.
*** EPA’s April 25 and May 23, 2008 proposed rules (73 FR 22307 and 73 FR 30029) incorrectly include 39.2 tons per day for the Merced
2005 NOX subarea budget. This was a typographical error. The number provided in the State’s submittal of the 2007 Plan is 39.4 tons per day,
which is reflected in Table 3 above.
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EPA is excluding from use in
determining that the SJVAB area 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, and is
determining that the SJVAB area
continues to attain the PM–10 standard.
Finally, EPA is approving
commitments from KCAPCD and CARB
to install a FRM or FEM in the newly
created East Kern serious PM–10
nonattainment area and to address
section 189(d) CAA requirements for the
area in a SIP revision in the event the
FRM or FEM records a violation of the
PM–10 standard.
IV. Statutory and Executive Order
Reviews
17 40 CFR 93.118(f)(2) applies when EPA reviews
the adequacy of an implementation plan
simultaneously with EPA’s approval or disapproval
of the implementation plan, as is the case here.
Subsection (f)(2)(iii) provides that ‘‘[i]f EPA makes
an adequacy finding through a final rulemaking that
approves the implementation plan submission,
such a finding will become effective upon the
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Under Executive Order 12866 (58 FR
51735, October 4, 1993), this 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 approves
a revised boundary designation, a
redesignation to attainment for the
SJVAB, a maintenance plan for the
SJVAB area, motor vehicle emissions
budgets and conformity trading
mechanism for the area and
commitments for the East Kern area, all
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of which were either requested or
submitted by the State. Accordingly, the
Administrator certifies that this rule
will not have a significant economic
impact on a substantial number of small
entities under the Regulatory Flexibility
Act (5 U.S.C. 601 et seq.). Because this
rule does not impose any additional
enforceable duty, it does not contain
any unfunded mandate or significantly
or uniquely affect small governments, as
described in the Unfunded Mandates
Reform Act of 1995 (Pub. L. 104–4).
Executive Order 13175 (65 FR 67249,
November 9, 2000) requires EPA to
develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’ Seven Indian tribes have
publication date of EPA’s approval in the Federal
Register.’’
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reservations located within the
boundaries of the SJVAB. EPA has
consulted with representatives of the
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
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 action merely
approves requests or submittals from the
State and does not alter the relationship
or the distribution of power and
responsibilities established in the Clean
Air Act.
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
approvals of a revised boundary
designation, a redesignation to
attainment for the SJVAB area, a
maintenance plan for the SJVAB area,
motor vehicle emissions budgets and
conformity trading mechanism for the
area and commitments for the East Kern
area. It will not have disproportionately
high and adverse effects on any
communities in the area, including
minority and low-income communities.
This 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 because it would
be inconsistent with applicable law for
EPA, when determining the attainment
status of an area, to use voluntary
consensus standards in place of
promulgated air quality standards and
monitoring procedures that otherwise
satisfy the provisions of the Clean Air.
This 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.).
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
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Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A major rule
cannot take effect until 60 days after it
is published in the Federal Register.
This action is not a ‘‘major rule’’ as
defined by 5 U.S.C. 804(2).
Under section 307(b)(1) of the Clean
Air Act, petitions for judicial review of
this action must be filed in the United
States Court of Appeals for the
appropriate circuit by January 12, 2009.
Filing a petition for reconsideration by
the Administrator of this final rule does
not affect the finality of this rule for the
purposes of judicial review nor does it
extend the time within which a petition
for judicial review may be filed, and
shall not postpone the effectiveness of
such rule or action. This action may not
be challenged later in proceedings to
enforce its requirements. (See section
307(b)(2)).
List of Subjects
40 CFR Part 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: September 24, 2008.
Wayne Nastri,
Regional Administrator, Region IX.
Parts 52 and 81 of Chapter I, Title 40
of the Code of Federal Regulations are
amended as follows:
■
PART 52—[AMENDED]
1. The authority citation for Part 52
continues to read as follows:
§ 52.220
Subpart F—California
2. Section 52.220 is amended by
adding paragraphs (c)(356) and (357) to
read as follows:
■
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Identification of plan.
*
*
*
*
*
(c) * * *
(356) The following plan was
submitted on November 16, 2007, by the
Governor’s Designee.
(i) Incorporation by reference.
(A) San Joaquin Valley Air Pollution
Control District.
(1) 2007 PM10 Maintenance Plan and
Request for Redesignation, adopted by
the San Joaquin Valley Air Pollution
Control District on September 20, 2007,
section 6. Contingency Plan on pages 16
to 17.
(ii) Additional materials.
(A) San Joaquin Valley Air Pollution
Control District.
(1) 2007 PM10 Maintenance Plan and
Request for Redesignation, adopted by
the San Joaquin Valley Air Pollution
Control District on September 20, 2007,
except for Appendices A through F.
(2) State of California, Air Resources
Board, Staff Report, Analysis of the San
Joaquin Valley 2007 PM10 Maintenance
Plan, Release Date: October 12, 2007,
Appendix B Emission Inventory.
(3) Letter dated May 13, 2008, from
James N. Goldstene, California Air
Resources Board, to Wayne Nastri, EPA,
providing revised motor vehicle
emission budgets for the 2007 San
Joaquin Valley PM10 Maintenance Plan.
(357) The following commitments
were submitted on February 29, 2008,
by the Governor’s Designee:
(i) Incorporation by reference.
(A) Commitments for the installation
and operation of a FRM or FEM PM–10
monitor and SIP development and
submittal.
(1 ) Resolution No. 2008–001–02,
adopted by the Air Pollution Control
Board, Kern County Air Pollution
Control District on February 27, 2008.
(2 ) Executive Order S–08–004,
adopted by the California Air Resources
Board on March 3, 2008.
*
*
*
*
*
PART 81—[AMENDED]
3. The authority citation for Part 81
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
■
Authority: 42 U.S.C. 7401 et seq.
66773
4. In § 81.305 the ‘‘California—PM–
10’’ table is amended under Fresno,
Kern, Kings, Madera, Merced, San
Joaquin, Stanislaus, Tulare Counties by
revising the entry for the ‘‘San Joaquin
Valley planning area’’ to read as follows:
■
§ 81.305
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CALIFORNIA—PM–10
Designation
Classification
Designated Area
Date
*
*
*
*
Fresno, Kern, Kings, Madera, Merced, San Joaquin, Stanislaus, Tulare
Counties:
mstockstill on PROD1PC66 with RULES
*
*
*
*
East Kern; that portion of Kern County which lies between the following
two lines (with the exception of that portion in Hydrologic Unit Number
18090205—the Indian Wells Valley):
(1) West and north of a line described as follows: Beginning at the
southwest corner of section 31, T. 10 N. 16 W. and running east to
the northwest boundary of the Rancho La Liebre Land Grant; then
running north and east along the northwest boundary of the Rancho
La Liebre Land Grant to the point of intersection with the range line
common to R. 15 W. and R. 16 W., San Bernardino Base and Meridian; then north along the range line to the northwest corner of
section 2, T. 32 S., R. 32 E., Mount Diablo Base and Meridian; then
east along the township line common to T. 32 S. and T. 31 S.; then
north along the range line common to R. 35 E. and R. 34 E.; then
east along the township line common to T. 29 S. and T. 28 S.; then
north along the range line common to R. 36 E. and R. 35 E.; then
east along the township line common to T. 28 S. and T. 27 S.; then
north along the range line common to R. 37 E. and R. 36 E. to the
Kern-Tulare County boundary.
(2) East and south of a line of a line described as follows: Beginning
at the southwest corner of section 31, T. 10 N. 16 W. and running
north along the range line common to R. 16 W. and R. 17 W., San
Bernardino Base and Meridian; north along the range line to the
point of intersection with the Rancho El Tejon Land Grant boundary;
then southeast, northeast, and northwest along the boundary of the
Rancho El Tejon Land Grant to the northwest corner of S. 3, T. 11
N., R. 17 W.; then west 1.2 miles; then north to the Rancho El
Tejon Land Grant boundary; then northwest along the Rancho El
Tejon line to the southeast corner of S. 34, T. 32 S., R. 30 E.,
Mount Diablo Base and Meridian; then north to the northwest corner
of S. 35, T. 31 S., R. 30 E.; then northeast along the boundary of
the Rancho El Tejon Land Grant to the southwest corner of S. 18,
T. 31 S., R. 31 E.; then east to the southeast corner of S. 13, T. 31
S., R. 31 E.; then north along the range line common to R. 31 E.
and R. 32 E., Mount Diablo Base and Meridian, to the northwest
corner of S. 6, T. 29 S., R. 32 E.; then east to the southwest corner
of S. 31, T. 28 S., R. 32 E.; then north along the range line common to R. 31 E. and R. 32 E. to the northwest corner of S. 6, T. 28
S., R. 32 E., then west to the southeast corner of S. 36, T. 27 S., R.
31 E., then north along the range line common to R. 31 E. and R.
32 E. to the Kern-Tulare County boundary.
VerDate Aug<31>2005
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11/15/1990
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*
Serious.
Federal Register / Vol. 73, No. 219 / Wednesday, November 12, 2008 / Rules and Regulations
66775
CALIFORNIA—PM–10—Continued
Designation
Classification
Designated Area
Date
San Joaquin Valley Air Basin; Fresno County, Kings County, Madera
County, Merced County, San Joaquin County, Stanislaus County, Tulare
County, and that portion of Kern County which lies west and north of a
line described as follows: Beginning at the Kern-Los Angeles County
boundary and running north and east along the northwest boundary of
the Rancho La Libre Land Grant to the point of intersection with the
range line common to R. 16 W. and R. 17 W., San Bernardino Base and
Meridian; north along the range line to the point of intersection with the
Rancho El Tejon Land Grant boundary; then southeast, northeast, and
northwest along the boundary of the Rancho El Tejon Land Grant to the
northwest corner of S. 3, T. 11 N., R. 17 W.; then west 1.2 miles; then
north to the Rancho El Tejon Land Grant boundary; then northwest
along the Rancho El Tejon line to the southeast corner of S. 34, T. 32
S., R. 30 E., Mount Diablo Base and Meridian; then north to the northwest corner of S. 35, T. 31 S., R. 30 E.; then northeast along the
boundary of the Rancho El Tejon Land Grant to the southwest corner of
S. 18, T. 31 S., R. 31 E.; then east to the southeast corner of S. 13, T.
31 S., R. 31 E.; then north along the range line common to R. 31 E. and
R. 32 E., Mount Diablo Base and Meridian, to the northwest corner of S.
6, T. 29 S., R. 32 E.; then east to the southwest corner of S. 31, T. 28
S., R. 32 E.; then north along the range line common to R. 31 E. and R.
32 E. to the northwest corner of S. 6, T. 28 S., R. 32 E., then west to
the southeast corner of S. 36, T. 27 S., R. 31 E., then north along the
range line common to R. 31 E. and R. 32 E. to the Kern-Tulare County
boundary.
*
*
*
[FR Doc. E8–26500 Filed 11–10–08; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 180
[EPA–HQ–OPP–2008–0175; FRL–8387–8]
Avermectin; Pesticide Tolerances for
Emergency Exemptions
Environmental Protection
Agency (EPA).
ACTION: Final rule.
mstockstill on PROD1PC66 with RULES
AGENCY:
SUMMARY: This regulation establishes a
time-limited tolerance for combined
residues of the insecticide avermectin
B1 and its delta-8,9-isomer in or on
bean, lima, seed. This action is in
response to EPA’s granting of an
emergency exemption under section 18
of the Federal Insecticide, Fungicide,
and Rodenticide Act (FIFRA)
authorizing use of the pesticide on large
lima beans. This regulation establishes a
maximum permissible level for residues
of avermectin in this food commodity.
The time-limited tolerance expires and
is revoked on December 31, 2010.
DATES: This regulation is effective
November 12, 2008. Objections and
requests for hearings must be received
on or before January 12, 2009, and must
be filed in accordance with the
VerDate Aug<31>2005
18:26 Nov 10, 2008
Jkt 217001
December 12,
2008.
*
Frm 00061
Fmt 4700
Sfmt 4700
Date
Type
Attainment.
*
instructions provided in 40 CFR part
178 (see also Unit I.C. of the
SUPPLEMENTARY INFORMATION.
ADDRESSES: EPA has established a
docket for this action under docket
identification (ID) number EPA–HQ–
OPP–2008–0175. All documents in the
docket are listed in the docket index
available in https://www.regulations.gov.
Although listed in the index, some
information is not publicly available,
e.g., Confidential Business Information
(CBI) or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available in the electronic docket at
https://www.regulations.gov, or, if only
available in hard copy, at the OPP
Regulatory Public Docket in Rm. S–
4400, One Potomac Yard (South Bldg.),
2777 S. Crystal Dr., Arlington, VA. The
Docket Facility is open from 8:30 a.m.
to 4 p.m., Monday through Friday,
excluding legal holidays. The Docket
Facility telephone number is (703) 305–
5805.
FOR FURTHER INFORMATION CONTACT:
Andrew Ertman, Registration Division
(7505P), Office of Pesticide Programs,
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460–0001; telephone number:
PO 00000
Type
*
*
(703) 308–9367; e-mail address:
ertman.andrew@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does this Action Apply to Me?
You may be potentially affected by
this action if you are an agricultural
producer, food manufacturer, or
pesticide manufacturer. Potentially
affected entities may include, but are
not limited to:
• Crop production (NAICS code 111).
• Animal production (NAICS code
112).
• Food manufacturing (NAICS code
311).
• Pesticide manufacturing (NAICS
code 32532).
This listing is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
affected by this action. Other types of
entities not listed in this unit could also
be affected. The North American
Industrial Classification System
(NAICS) codes have been provided to
assist you and others in determining
whether this action might apply to
certain entities. If you have any
questions regarding the applicability of
this action to a particular entity, consult
the person listed under FOR FURTHER
INFORMATION CONTACT.
E:\FR\FM\12NOR1.SGM
12NOR1
Agencies
[Federal Register Volume 73, Number 219 (Wednesday, November 12, 2008)]
[Rules and Regulations]
[Pages 66759-66775]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E8-26500]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 52 and 81
[EPA-R09-OAR-2008-0306; FRL-8724-7]
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: Final rule.
-----------------------------------------------------------------------
SUMMARY: EPA is approving the State of California's request under the
Clean Air Act (CAA or the Act) 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
[[Page 66760]]
Valley Air Basin (SJVAB) serious PM-10 nonattainment area and the East
Kern serious PM-10 nonattainment area. EPA is also redesignating the
SJVAB nonattainment area to attainment for the PM-10 national ambient
air quality standard (NAAQS) and approving the PM-10 maintenance plan,
motor vehicle emissions budgets and conformity trading mechanism for
the area. EPA is also excluding from use in determining that the area
has attained the standard exceedances on July 4, 2007, and January 4,
2008, that EPA has concluded were caused by exceptional events.
Finally, EPA is approving 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 CAA requirements under section 189(d) as necessary for the
area.
DATE: This rule is effective on December 12, 2008. The motor vehicle
emission budgets are applicable as of November 12, 2008.
ADDRESSES: EPA has established docket number EPA-R09-OAR-2008-0306 for
this action. The docket is available electronically at
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. Public Comments and EPA Responses
A. Area Has Attained
B. Fully Approved SIP
C. Improvements in Air Quality are Due to Permanent and
Enforceable Emission Reductions
D. Area Has Met All Applicable CAA Section 110 and Part D
Requirements
E. Maintenance Plan
F. Revision of Boundary Designation
G. Miscellaneous Comments
III. Final Actions
IV. Statutory and Executive Order Reviews
I. Background
On April 25, 2008 (73 FR 22307), EPA proposed the following
actions:
Approval of the State of California's request to revise
the designation for the SJV serious PM-10 nonattainment area by
splitting the area into two separate nonattainment areas, the SJVAB
serious PM-10 nonattainment area and the East Kern serious PM-10
nonattainment area.
Redesignation of the SJVAB nonattainment area to
attainment for the PM-10 NAAQS and approval of the maintenance plan,
motor vehicle emissions budgets and conformity trading mechanism for
the SJVAB area.
Exclusion from use in determining that the SJVAB 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.
Approval of enforceable commitments by the Kern County Air
Pollution Control District (KCAPCD) and the California Air Resources
Board (CARB) to install a PM-10 monitor in the East Kern nonattainment
area and to address CAA requirements under section 189(d) as necessary
for the East Kern area.
Subsequently, On May 23, 2008, EPA extended the public comment
period for two weeks, until June 10, 2008. 73 FR 30029. EPA issued the
extension in order to notify the public of a minor change in the motor
vehicle emissions budgets and to provide the public with the
opportunity to consider these technical corrections.
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.\1\ EPA is required to
approve or deny the revised designation within 18 months of receipt. On
January 31, 2008, the State submitted to EPA a revised designation that
involves a boundary change only and not a change in status (e.g., from
``nonattainment,'' to ``attainment'' or ``unclassifiable'') of any
area.
---------------------------------------------------------------------------
\1\ 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).
---------------------------------------------------------------------------
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 memorandum).
The proposed rule provides a more detailed discussion of the
background pertinent to this final action.
II. Public Comments and EPA Responses
EPA received one letter in support of EPA's proposed actions from
the San Joaquin Valley Air Pollution Control District (SJVAPCD or the
District) and two letters with adverse comments. As EPA sets forth in
detail in its responses to comments below, in taking final action EPA
has fully considered all data pertinent for regulatory use in
determining attainment in the SJVAB area and EPA continues to believe
that the area has attained the PM-10 standard. EPA has also determined
that the State's request for redesignation and the maintenance plan for
the SJVAB area meet the applicable requirements of the CAA. In
addition, EPA is granting the State's request for a boundary revision
for the area based on a multiplicity of factors. The available
monitoring data for the East Kern area, while limited, also indicate
that concentrations are well below the NAAQS. Thus, for the reasons set
forth in the responses to comments below, as well as in the proposed
rule, EPA is finalizing its proposed determinations as fully meeting
the requirements of the CAA.
A. Area Has Attained
Comment 1: Earthjustice (EJ) states that the first condition that a
nonattainment area must meet in order to be redesignated to attainment
under CAA section 107(d)(3)(E) is that EPA has determined that the area
has actually attained the NAAQS. EJ alleges that the SJV nonattainment
area has recorded multiple exceedances of the standard during the
period that EPA is relying on to demonstrate attainment and that EPA is
thus ignoring a serious air quality problem and the health impacts
associated with it. EJ incorporates by reference and attaches its
previous comments on EPA's attainment determination that claim the
problem EPA is ignoring has existed for
[[Page 66761]]
many years, is part of what led EPA to designate the SJV area
nonattainment in the first place and is caused by ongoing human
activity that is not reasonably controlled.
Response 1: The previous comments to which EJ refers in its June
10, 2008 comment letter on the proposed rule are contained in its
August 18, 2006 comment letter with attachments A-H, October 26, 2007
comment letter, December 29, 2006 Petition for Reconsideration and
March 21, 2007 Petition for Withdrawal, with attached declarations from
Sarah Jackson and Jan Null. EJ raised the same issues as it raises here
during EPA's rulemakings regarding the 2006 determination of attainment
for the SJV nonattainment area and 2008 affirmation of that
determination. EPA fully responded to EJ's comments at that time. See
the final rules at 71 FR 63642 (October 30, 2006) and 73 FR 14687
(March 19, 2008). See also the proposed rules for these actions at 71
FR 40952 (July 19, 2006) and 72 FR 49046 (August 27, 2007). As we
explained in our responses to EJ's comments in the final rules, EPA
believes that the SJV area has attained the PM-10 NAAQS and that the
exceedances noted by EJ were properly excluded from consideration under
the Agency's Exceptional Events Rule (EER)(72 FR 13560; March 22,
2007).
EJ subsequently filed petitions for review of the October 2006 and
March 2008 final rules in the U.S. Court of Appeals for the Ninth
Circuit. Latino Issues Forum, et al. v. EPA, Nos. 06-75831 and 08-
71238.\2\ In its opening brief in these cases, filed on June 16, 2008,
EJ again raises these issues. In its brief in opposition, filed on
September 3, 2008, EPA again responds to EJ's arguments. EJ was
required to raise any issues regarding the 2006 attainment
determination and 2008 affirmation of that determination during those
rulemakings and in the Ninth Circuit in Latino Issues Forum and cannot
relitigate the same issues here.
---------------------------------------------------------------------------
\2\ The Ninth Circuit has consolidated the two petitions for
review.
---------------------------------------------------------------------------
Moreover, in the proposed rule for today's final action we proposed
to exclude under the EER data showing exceedances in the SJV
nonattainment area on July 4, 2007 and January 8, 2008, and concluded
that the area continued to attain the PM-10 standard through February
2008. We did not receive any adverse comments on this aspect of our
proposed rule. In this final action, for the reasons set forth in the
proposed rule and in EPA's concurrence letters to which it refers, we
are concurring with the State's flagging of those data as caused by
fireworks and high wind exceptional events, and excluding those data
from consideration in determining that the SJVAB area continues to
attain the standard.
Finally, EPA is aware of PM-10 exceedances recorded on May 21, 2008
at the Corcoran and Bakersfield Federal Equivalent Method (FEM)
monitors and the Corcoran Federal Reference Method (FRM) monitor, and
on May 22, 2008 at the Corcoran FEM. On June 24, 2008, the District
posted on its website documentation that these exceedances were caused
by a natural event, i.e., high winds. The comment period ended on July
24, 2008 and no public comments were received. The documentation was
submitted to EPA on August 12, 2008 and EPA has concurred that these
exceedances should be flagged as exceptional events. Letter from Wayne
Nastri, EPA to Mary D. Nichols, CARB, September 24, 2008.
EPA is not taking comment on whether the May 2008 exceedances
should be excluded from the determination in this final rule that the
SJVAB area continues to attain the PM-10 standard. The determination of
whether an area has attained the PM-10 standard is based on the most
recent three consecutive calendar years of data. As mentioned above and
in other EPA actions, the SJVAB area has attained the PM-10 standard
based on data for the three-year period from 2003 through 2005 and the
three-year period from 2005 through 2007. See 71 FR 63642 and 73 FR
14687. Because 2008 has not ended, EPA cannot determine whether the
area has attained the standard based on the three-year period from 2006
through 2008. We can, however, determine with less than three years of
data whether the SJVAB area has failed to attain in the period from
2006 to date. See 40 CFR part 50, appendix K, section 2.3(c) and 71 FR
63642, footnote 26.
Because the May 21 and 22, 2008 exceedances are the only
exceedances at the Corcoran monitors since 2006 not excluded through
notice and comment rulemaking from regulatory consideration, the
expected number of exceedances recorded at the FRM monitor, based on
the May 21 exceedance, is three and the expected number of exceedances
recorded at the FEM monitor on May 21 and May 22 is two.\3\ Similarly,
because the May 21, 2008 exceedance is the only exceedance recorded at
the Bakersfield monitor since 2006 not excluded from regulatory
consideration through notice and comment rulemaking, the expected
number of exceedances at the Bakersfield monitor is one. Thus, even if
EPA does not exclude the May 21 and 22, 2008 exceedances from
regulatory consideration, the SJVAB area continues to attain the PM-10
NAAQS to date because both Corcoran and Bakersfield have an expected
number of exceedances of less than or equal to one per year, averaged
over the three year period 2005-2007 and through 2008 to date. All
other monitors in the SJV area had an expected number of exceedances of
less than or equal to one per year during these periods. EPA thus
determines that the SJVAB area has attained the PM-10 NAAQS as required
by section 107(d)(3)(E)(i).
---------------------------------------------------------------------------
\3\ Note that the Corcoran FRM operates on a one-in-three day
schedule and that EPA does not combine PM-10 data collected with
different monitoring methods, i.e., FRMs and FEMs. See Memorandum
from Gerald A. Emison, EPA, to EPA Regional Division Directors,
``Revision to Policy on the Use of PM-10 Measurement Data,''
November 21, 1988 at 3.
---------------------------------------------------------------------------
B. Fully Approved SIP
Comment 2: EJ states that the second condition for redesignation
under section CAA section 107(d)(3)(E) is that an area seeking
redesignation must have a fully approved state implementation plan
(SIP) and must satisfy all requirements that apply to the area and that
the SJV nonattainment area does not have such a SIP. EJ argues that
while EPA concedes that it has never approved contingency measures for
the area and has instead suspended this requirement under the Agency's
Clean Data Policy, neither the policy nor the cases EPA cites addresses
PM-10 nonattainment areas and therefore do not square EPA's action with
the mandate under CAA section 189(c) that such areas continue to
achieve the milestones for emission reductions in order to demonstrate
reasonable further progress (RFP) ``until the area is redesignated to
attainment.'' EJ believes that because contingency measures are also
necessary to ensure this progress is achieved, EPA cannot suspend the
requirement for these measures. Citing Engine Mfrs. Ass'n v. EPA, 88
F.3d 1075, 1089 (D.C. Cir. 1996), EJ asserts that EPA does not have the
authority to waive statutory requirements and circumvent redesignation
provisions because it believes compliance with those requirements is
unnecessary.
Response 2: In 2006 EPA approved the entire nonattainment plan for
the SJV area,\4\ including the CAA section 189(c)(1) reasonable further
progress milestones, except for the CAA section 172(c)(9) contingency
measures, on
[[Page 66762]]
which EPA deferred action. 69 FR 30006 (May 26, 2004). EPA subsequently
determined that the contingency measures requirement for the SJV area
was suspended as a result of its October 2006 determination that the
area has attained the PM-10 standard. 71 FR 63642, 63663. During that
rulemaking, EJ raised the same issues with regard to EPA's Clean Data
Policy \5\ and statutory construction as it raises here. EPA responded
to EJ's arguments in the final rule. See id. at 63643-63647. EJ again
raises these issues in its opening brief in Latino Issues Forum. EPA
again responds to EJ's arguments in its brief in opposition. EJ was
required to raise any issues regarding the suspension of the
contingency measures requirement during EPA's 2006 attainment
determination rulemaking and in Latino Issues Forum. EJ did so and
cannot relitigate the same issues here. Because EPA has approved SIP
provisions submitted by California for the SJVAB area that address all
applicable CAA requirements, EPA has concluded that the CAA section
107(d)(3)(E) requirement for a fully approved SIP has been met.
---------------------------------------------------------------------------
\4\ ``2003 PM10 Plan, San Joaquin Valley Plan to Attain Federal
Standards for Particulate Matter 10 Microns and Smaller'' (2003 PM-
10 Plan).
\5\ EPA has long interpreted the CAA to provide that certain
nonattainment area requirements, the purpose of which are to ensure
attainment of the relevant NAAQS by the applicable deadline, will no
longer apply once an area has attained that NAAQS, and for as long
it continues to do so until it is redesignated to attainment status.
While referred to as the Clean Data Policy, it is more accurately
described as EPA's interpretations of the relevant provisions of
Title I, Part D of the CAA. See Sierra Club v. EPA, 375 F.3d 537,
541-42 (7th Cir. 2004); Sierra Club v. EPA, 99 F.3d 1551, 1156-57
(10th Cir. 1996). EPA first set forth this interpretation in its
``General Preamble for the Interpretation of Title I of the Clean
Air Act Amendments of 1990,'' (General Preamble) thereafter
reiterated it in several policy memoranda and since codified the
policy with respect to ozone and PM-2.5 nonattainment areas. 57 FR
13498, 13564 (April 16, 1992), 40 CFR 51.918 (ozone) and 51.1004(c)
(PM2.5). EPA has applied the policy to numerous PM-10
nonattainment areas, including the SJV area. For an expanded
description of the policy and our application of it, see Respondent
EPA's Merits Brief in Latino Issues Forum at 7-8, 71 FR 40952, 40954
and 71 FR 63642, 63644.
---------------------------------------------------------------------------
In addition, in the context of evaluating the area's eligibility
for redesignation, there is a separate and additional justification for
finding that the section 172(c)(9) contingency measures are not an
applicable SIP requirement for purposes of redesignation. Prior to and
independently of that policy, and specifically in the context of
redesignations, EPA interpreted the contingency measure requirement as
not applicable for purposes of redesignation. In the General Preamble
EPA stated that:
[t]he section 172(c)(9) requirements are directed at ensuring
RFP and attainment by the applicable date. These requirements no
longer apply when an area has attained the standard and is eligible
for redesignation. Furthermore, section 175A for maintenance plans *
* * provides specific requirements for contingency measures that
effectively supersede the requirements of section 172(c)(9) for
these areas.
See also Calcagni memorandum at 6 (``The requirements for reasonable
further progress and other measures needed for attainment will not
apply for redesignations because they only have meaning for areas not
attaining the standard.''). Thus, even if the contingency measure
requirement had not previously been suspended, it would not apply for
purposes of evaluating whether an area that has attained the standard
qualifies for redesignation. EPA has enunciated and held this position
since the General Preamble was published more than sixteen years ago
and represents the Agency's interpretation of what constitutes
applicable requirements under section 107(d)(3)(E). The Courts have
recognized the scope of EPA's authority to interpret ``applicable
requirements'' in the redesignation context. See Sierra Club v. EPA,
375 F.3d 537 (7th Cir. 2004).
C. Improvements in Air Quality Must Be Due to Permanent and Enforceable
Emission Reductions
Comment 3: EJ states that a 1992 guidance memorandum from John
Calcagni lays out the steps that an area must take to show that the
improvement in air quality is attributable to permanent and enforceable
reductions in emissions, the third condition for redesignation to
attainment under CAA section 107(d)(3)(E). EJ claims that this analysis
should include estimating the percentage reductions achieved from the
federal and state controls implemented in the area, taking into account
permitted emission rates, production capacities and other related
information. EJ states that EPA, banking on its waiver of all the
violations during the period of interest, neglected to perform the
proper analyses in the Calcagni memorandum and merely repeats the
District's belief, based on four observations (comments 4 through 7
below), that the area is attaining the standard.
Response 3: As discussed in our proposed rule, the Calcagni
memorandum states that the state must be able to reasonably attribute
the improvement in air quality to emission reductions which are
permanent and enforceable, and the improvement should not be a result
of temporary reductions (e.g., economic downturns or shutdowns) or
unusually favorable meteorology. The Calcagni memorandum also states
that 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. Our proposed rule
discusses how each of these factors is addressed by the State in the
``2007 PM10 Maintenance Plan and Request for Redesignation,'' September
20, 2007, SJVAPCD (2007 Plan). 73 FR 22307; 2008, footnote 8; 22311-
22312.
In general, the 2007 Plan shows that there has been a significant
improvement in PM-10 air quality since 1990, noting that there were 33
estimated exceedance days during 1990-1992 and 2.9 exceedance days
during 2002-2004. This decrease in exceedance days (and emissions)
occurred during a period of rapid economic growth in the SJVAB area as
indicated by the increases in population and vehicle miles traveled
(VMT). The 2007 Plan did not find any evidence of significant shutdowns
that would cause the decline in exceedance days. The 2007 Plan analyzed
the meteorology in the SJVAB area during 2003-2006 by comparing the
average annual wind speeds, precipitation levels and stability levels
to long-term averages and found that there was no consistent pattern to
show that there was favorable meteorology leading to the improvement in
PM-10 levels during 2003-2006.
The 2007 Plan states that over 500 new rules and rule amendments
have been adopted, reducing NOX and PM-10 emissions from a
wide range of source categories, and it shows decreases in the overall
emissions of NOX and PM-10 (which include all emissions from
area sources as well as from permitted major sources) since 2000. A
more detailed discussion of these analyses can be found in our proposed
rule and in the 2007 Plan. EPA's analysis is based on the State's
assessment and EPA continues to believe that the State has demonstrated
that the improvement in PM-10 air quality in the SJVAB area is a result
of permanent and enforceable reductions in emissions and has adequately
addressed the provisions of the Calcagni memorandum.
Finally, as discussed in the response to comment 1 above, EPA has
determined that the SJV area has attained the PM-10 standard. 71 FR
63642; 73 FR 14687. These determinations included EPA's concurrence
with the State's and Santa Rosa Rancheria Tribe's conclusion that a
number of exceedances were caused
[[Page 66763]]
by exceptional events and thus should be excluded from regulatory
consideration. Id. EJ seems to suggest that EPA's analyses should
include these exceedances even though they have been properly excluded
from regulatory consideration. EPA disagrees.
Comment 4: EJ claims that the District provides a chart (2007 Plan
at 24, Figure 2) showing a downward trend in air pollution levels that
is completely misleading because it does not include EPA-acknowledged
exceedances in 2004 and 2005, let alone the many exceedances EPA has
ignored in its attainment determination.
Response 4: The District's chart (2007 Plan at 24, Figure 2) shows
a long-term downward PM-10 trend from 1990 to 2006 for the SJVAB area
by plotting the estimated exceedance days over the NAAQS. The estimated
exceedance days in this chart are based on exceedances recorded with
FRMs and not FEMs such as continuous beta attenuation monitors (BAMs).
EPA believes that the District's chart is not misleading and provides a
general picture of the long-term trend for PM-10 and that 1990 is a
reasonable year to begin the analysis because that was the year the CAA
was amended.
EJ's comment letter (page 4) includes a chart, ``PM-10 Trend,''
that appears to revise the 2007 Plan's chart by adding the exceedances
from BAMs that occurred in 2004 and 2005 and by removing the data for
1990 in order to show a less precipitous decline in PM-10 levels.
However, even with the exclusion of the 1990 data and the addition of
the exceedances from the BAMs, EJ's ``PM-10 Trend'' chart still shows a
decline in PM-10 levels.
Moreover, the 2007 Plan provides a summary in Table 10 of the
declining annual average emissions inventories from 1990 through 2005
which is consistent with the District's trends chart. Table 10 shows
PM-10 emissions decreasing by 46 tons per day (tpd) and NOX
emissions decreasing by 228 tpd during this time period.
Finally, as discussed above, EPA has not ignored any recorded
exceedances but rather has followed its regulations to exclude from
regulatory consideration any exceedances that are caused by exceptional
events. 73 FR 14687; response to comment 3 above. EPA also set forth in
its 2006 attainment determination its conclusions as to prior monitored
data. 71 FR 63642.
Comment 5: EJ claims that while the District asserts that growth in
the SJV nonattainment area has been rapid since 1990 but that emissions
have decreased, the sources of these claimed reductions do not support
redesignation.
Response 5: See responses to comments 1, 3 and 4 above, and 7 and 8
below.
Comment 6: EJ alleges that the District and EPA conclude without
justification that the District's meteorological analysis shows that
favorable meteorology did not lead to the improvements in air quality.
Instead, EJ argues, the analysis shows that from 2004 to 2006, the SJV
nonattainment area experienced some of the wettest years on record and
that 2003 through 2006 experienced lower than average stability levels,
which EPA and the District concede would lead to better dispersion
conditions and lower PM-10 levels. As a result, EJ claims the data
provided undercut any claim that the alleged air quality improvement is
likely to be maintained.
Response 6: Our proposed rule summarizes the meteorological
analysis provided in the 2007 Plan which includes an examination of the
precipitation, temperature wind speeds and atmospheric stability during
the period 2003 through 2006. The summary was based on data presented
in Appendix C to the 2007 Plan. As EJ comments, there were some
conditions that favored lower PM-10 levels; however, there were also
conditions that favored higher PM-10 levels. Conditions that favored
higher PM-10 levels included no variation in annual average wind speeds
(which are generally quite low for the SJV area), warmer than average
temperatures and two dry years ranking 98th and 112th in wetness (with
the 1st year being the wettest year) during a 128 year period. Since
there were conditions that both favored and did not favor higher PM-10
levels, the conclusion of the 2007 Plan and EPA's analysis is that
there was no consistent pattern to show that attainment was a result of
unusually favorable meteorology. 73 FR 22307, 22312.
Finally we note that the Calcagni memorandum makes clear that
``[a]ttainment resulting from * * * unusually favorable meteorology
would not qualify as an air quality improvement due to permanent and
enforceable emission reductions.'' Calcagni memorandum at 4. Therefore
EPA disagrees with EJ's comment that the meteorological data indicate
that the air quality improvement will not likely be maintained.
In addition, EPA obtained available information on precipitation,
average monthly temperatures and wind speeds for 2007 and compared the
2007 data to the averages presented in Appendix C to the 2007 Plan at
Tables C-1, C-2 and C-3. (Atmospheric stability data for 2007 was not
available.) The total precipitation for 2007 was 7.03 inches (https://
www.wrh.noaa.gov/hnx/fat/normals/fatrnyr.htm) which is lower than the
average precipitation of 10.13 inches for 1878 through 2006 (2007 Plan
at Table C-1) and would favor higher PM-10 levels. The average monthly
temperatures in degrees Celcius for 2007 were 4.6 for January, 9.5 for
February, 14.3 for March, 15.9 for April, 20.7 for May, 24 for June,
26.3 for July, 26.3 for August, 21.7 for September, 16.1 for October,
11.9 for November and 5.5 for December. (https://www.weather.gov/
climate/xmacis.php?wfo=hnx) When compared to the average monthly
temperatures from 1900 through 2005 (2007 Plan at Table C-2), the
average temperatures for the months of March, May, June and August were
higher in 2007 than average and would favor higher PM-10 levels.
Finally, the average wind speed for 2007 was 3.7 miles per hour (mph)
(https://www.cimis.water.ca.gov) which is consistent with the average
wind speed of 3.72 mph for 1984 through 2006 (2007 Plan at Table C-3)
and would favor high PM-10 levels. Since the available 2007
meteorological data favor higher PM-10 levels, EPA continues to believe
that there is no consistent pattern that would establish that
attainment has resulted from unusually favorable meteorology.
Comment 7: EJ disputes EPA's conclusion that improvements in air
quality are the result of permanent and enforceable reductions in
emissions from rules adopted by the District since 1992. EJ claims that
most of these rules were adopted only in the last few years and
therefore any trend in emission reductions that can be inferred from
the chart provided by the District (2007 Plan at 24, Figure 2) cannot
be attributed to these rules. EJ suggests that the drop in exceedance
days between 1990 and 1992 might be due to a difference in the
methodologies for measuring exceedances for the TSP and PM-10
standards. EJ provides its own chart, ``PM-10 Trend,'' adjusted to
include the exceedance days that it says EPA has acknowledged, that
purports to show only minimal changes in the recurring pattern of PM-10
violations over the last 15 years.
Response 7: On July 1, 1987, EPA revised the NAAQS for particulate
matter by replacing the standards for total suspended particulate
matter (TSP) with new standards applying only to PM-10. 52 FR 24672.
While PM-10 monitoring data have been collected since 1987 (see 71 FR
63642, 63653), the District and CARB have not reported TSP data to
EPA's Air Quality System
[[Page 66764]]
(AQS) database since 1989. Therefore any difference in measurement
methodologies for the two pollutants could not be the cause of the drop
in exceedance days between 1990 and 1992.
Since enactment of the 1990 CAA Amendments, the State has adopted
and submitted several PM-10 plans. These include a moderate area plan
under CAA section 189(a), a serious area plan under section 189(b) and
a serious area plan under section 189(d) (i.e., the 2003 PM-10 Plan
approved by EPA in 2004 and discussed above). The 2003 PM-10 Plan
provides a summary of the many State, District and EPA rules adopted
from 1990 through 2003. See 2003 PM-10 Plan at Tables 4-1, 4-2, 4-3 and
4-4. The 2003 PM-10 Plan also includes commitments for additional PM-10
and NOX measures, all of which were adopted by the District
and State after 2003 and most of which have been approved by EPA. See
response to comment 8 below.
The District's chart (2007 Plan, Figure 2) shows that PM-10 levels
have declined from 1990 through 2006 while these PM-10 plans and rules
have been adopted and implemented. We note that even EJ's own ``PM-10
Trend'' chart shows a general decrease in PM-10 levels since 1992 and
since early 2000.
Furthermore, the 2007 Plan shows that significant reductions in PM-
10 and NOX emissions occurred from the year 2000 to the year
2005, the time period during which the SJV area attained the PM-10
standard. NOX emissions have declined from 673 tpd in 2000
to 606 tpd in 2005 and PM-10 emissions have declined from 324 tpd in
2000 to 284 tpd in 2005. 2007 Plan; Staff Report, Air Resources Board,
``Analysis of the San Joaquin Valley 2007 PM10 Maintenance Plan,'' (ARB
Staff Report for 2007 Plan) Appendix B.\6\
---------------------------------------------------------------------------
\6\ See footnote 2 of the proposed rule. 73 FR 22307, 22308.
---------------------------------------------------------------------------
As can be seen from the above discussion and our responses to
previous comments, PM-10 exceedance days and PM-10 and NOX
emission levels have declined while at the same time the SJV area has
exhibited significant growth in population and vehicle miles traveled.
2007 Plan at 24, Figure 2 and at 26, Figures 3 and 4. Thus EPA
continues to believe that it is reasonable to attribute the improvement
in PM-10 air quality to the emission reductions from adopted rules that
are permanent and enforceable.
Comment 8: EJ argues that the District's failure to estimate the
tons or percent reduction from the baseline year achieved by its PM-10
control measures makes it difficult to assert that any improvements in
air quality are the result of such controls. Further, while EPA claims
that the District has adopted all of its rule commitments in the 2003
PM-10 Plan, only 2 of the 14 commitments have received EPA approval
according to EJ. The maintenance plan identifies 8 additional rules,
only 3 of which have been approved by EPA. EJ states that of the 22
rules the District identified during its PM-10 planning process to help
reduce PM-10 in the SJV nonattainment area, only 5 are enforceable
elements of the SIP.
Response 8: The 2007 Plan provides a summary of overall
NOX and PM-10 emissions and shows that emissions have
decreased from approximately 1177 tpd in 1990 to approximately 1000 tpd
in 2000 to approximately 900 tpd in 2005 and estimates that they will
continue to decrease to approximately 800 tpd in 2010. 2007 Plan at
Table 10 and 73 FR 22307, 22312. These declining emissions levels have
occurred as population and VMT have increased and are due to the
emissions reductions from rules and control measures that have been
adopted and implemented since 1990. 2007 Plan at 26 through 27 and 2003
PM-10 Plan at Tables 4-1, 4-2, 4-3 and 4-9.
The 2003 PM-10 Plan summarizes the numerous rules and control
measures adopted by the SJVAPCD, the State and EPA prior to 2003. 2003
PM-10 Plan at Tables 4-1, 4-2 and 4-3. The 2003 PM-10 Plan also
includes District commitments to achieve additional reductions. 2003
PM-10 Plan at Table 4-9. As discussed below, the commitments have all
been converted to adopted rules. The emissions reductions from all of
the 2003 PM-10 Plan's rules, control measures and adopted commitments
are reflected in the 2007 Plan's emissions inventory. ARB Staff Report
for 2007 Plan at Appendix B.
It is not clear what year EJ considers to be the baseline year;
however, the 2007 Plan provides emissions inventories for the years
1990, 2000, 2005 and 2010 which include the estimated tpd of reductions
achieved by the PM-10 rules, control measures and rules adopted
pursuant to commitments. 2007 Plan at Table 10 and ARB Staff Report for
2007 Plan at Appendix B. Thus, EPA believes that the State and District
have estimated the tpd reductions from several baseline years (1990,
2000 and 2005) achieved by its PM-10 control measures and have shown
that the improvements in air quality are the result of such controls.
Regarding EJ's comment that only five of the 22 rules the District
identified during its PM-10 planning process are enforceable elements
of the SIP, EPA notes that this information was updated in the 2007
Plan. See ``Errata, 2007 PM10 Maintenance Plan and Request for
Redesignation,'' October 9, 2007, included in the 2007 Plan submittal
to EPA. Table 1 below summarizes the EPA-approved rules from the 2003
PM-10 Plan commitments and provides the EPA approval dates for these
rules as applicable. EPA has approved all but three of the submitted
rules (Rules 4694, 4401 and 9510).
Table 1--Summary of EPA Actions on 2003 PM-10 Plan Commitments
------------------------------------------------------------------------
2003 PM-10 plan commitment 7
(pollutants covered by Adopted rule EPA action
commitment) number and title
------------------------------------------------------------------------
A. Agriculture (Conservation 4550--Conservation Approved 2/14/06,
Management Practice Program) Management 71 FR 7683.
(PM-10, VOC). Practices.
B. Cotton Gins (PM-10).......... 4204--Cotton Gins. Approved 11/9/06,
71 FR 65740.
C. Dryers (NOX)................. 4309--Dryers, Approved 5/30/07,
Dehydrators, and 72 FR 29886.
Ovens.
D. Fugitive PM-10 (Regulation 8011--General Approved 2/17/06,
VIII) (PM-10). Requirements. 71 FR 8461.
8021--Construction
, Demo,
Excavation.
8031--Bulk
Materials..
8041--Carryout and
Trackout..
8051--Open Areas..
8061--Paved and
Unpaved Roads.
8071--Unpaved
Vehicle/Equip
Traffic Areas.
[[Page 66765]]
8081--Agricultural
Sources.
E. Glass-Melting Furnaces (SOX). 4354--Glass Approved 8/1/07,
Melting Furnaces. 72 FR 41894.
F. Gas-Fired Oilfield Steam 4406--Sulfur Not adopted by
Generators (SOX). Compounds From District.
Oilfield Steam
Generators--Kern
County.
G. Indirect Source Review, and 9510--Indirect Under EPA Review.
Indirect Source Mitigation Fee Source Review.
(NOX, PM-10).
H. Solid Fuel Boilers, Steam 4352--Solid Fuel Approved 5/30/07,
Generators, and Process Heaters Fired Boilers, 72 FR 29886.
(NOX, SOX). Steam Generators,
and Process
Heaters.
I. Small Boilers, Steam 4307--Boilers, Approved 5/30/07,
Generators, and Process Heaters Steam Generators, 72 FR 29886.
(NOX, SOX). and Process
Heaters 2.0 to
5.0 mmBtu.
J. Water Heaters (Industrial, 4308--Boilers, Approved 5/30/07,
Commercial, and Institutional) Steam Generators, 72 FR 29886.
(NOX). and Process
Heaters 0.075 to
2.0 mmBtu.
K. Wineries (VOC)............... 4694--Wineries.... Under EPA Review.
L. Steam Enhanced Crude Oil 4401--Steam Under EPA Review.
Production Well Vents (VOC). Enhanced Crude
Oil Production
Well Vents.
M. Residential Space Heating 4905--Natural Gas Approved 5/30/07,
(NOX). Fired, Fan-type, 72 FR 29886.
Residential
Central Furnaces.
N. Agricultural Internal 4702--Internal Approved 1/10/08,
Combustion Engines (PM-10, NOX). Combustion 73 FR 1819.
Engines Phase 2.
Residential Wood Combustion \8\. 4901--Residential Approved 9/30/03,
Wood Burning. 68 FR 56181.
------------------------------------------------------------------------
7 On May 26, 2004, EPA approved the 2003 PM-10 Plan including
commitments for new District rules. See 2003 PM-10 Plan, Table 4-9
List of New District Commitments. The commitments for PM-10 and NOX
reductions were approved as meeting BACM and the commitments for other
pollutants (SOX, VOC) were approved as SIP strengthenings. See 69 FR
30006, 30035 and 69 FR 5412, 5423. The District subsequently amended
the 2003 PM-10 Plan and revised Chapter 4 Control Strategy in May
2005; however, the amendments were not submitted to EPA. The EPA-
approved commitments are those found in the version of the 2003 PM-10
Plan adopted by the District on December 18, 2003.
8 In its comment letter, EJ lists Residential Wood Combustion as a
commitment from the 2003 PM-10 Plan; however, it was an adopted
measure and not a commitment. We have included it in our Table for
completeness in addressing EJ's comments.
In addition to the rules in Table 1, the 2007 Plan cites reductions
from additional rules that were not included in the 2003 PM-10 Plan's
commitments. All of these additional rules have been adopted and
submitted to EPA by the State and most have been approved by EPA. Table
2 below provides a summary of EPA actions on these additional rules
based on the ``Errata, 2007 PM-10 Maintenance Plan and Request for
Redesignation.''
Table 2--Summary of EPA Action on Additional Rules Identified by 2007
Plan
------------------------------------------------------------------------
Rule Rule title EPA action
------------------------------------------------------------------------
4103.......................... Open Burning (VOC & Approved 4/11/
NOX). 06, 71 FR
18216.
4305.......................... Boilers, Steam Approved 5/18/
Generators, and 04, 69 FR
Process Heaters (NOX). 28061.
4409.......................... Components Serving Approved 3/23/
Light Crude Oil or 06, 71 FR
Gases at Production 14652.
Facilities (VOC).
4451 & 4452................... Components at
Petroleum Refineries
(VOC).
4570.......................... Confined Animal Under EPA
Feeding Operations Review.
(VOC).
4604.......................... Can and Coil Coating Approved 5/19/
Operations (VOC). 06, 70 FR
28826.
9310.......................... School Bus Fleets Under EPA
(NOX). Review.
------------------------------------------------------------------------
Thus, contrary to EJ's comment, most of the rules identified in the
2007 Plan have been approved by EPA as federally enforceable elements
of the SIP. EPA is continuing to process the remainder of the State's
submitted rules.
Comment 9: EJ concludes that because the air quality improvements
are premised on ignoring multiple violations of the PM-10 standard and
fewer than one quarter of the rules the District relies on for
reductions are an enforceable part of the SIP, EPA cannot reasonably
attribute air quality improvements to permanent and enforceable
emission reductions.
Response 9: See above responses to comments 1, 3, 4, 6, 7 and 8.
D. Area Has Met All Applicable CAA Section 110 and Part D Requirements
Comment 10: EJ asserts that the District fails to comply with CAA
section 107(d)(3)(E) because it has not met all applicable requirements
under section 110 and part D. EJ says that in addition to the
contingency measure requirement, the District has not met the section
189(b)(1)(B) BACM requirement because BACM were required to be
implemented by January 8, 1993 and EPA has still not approved most of
the PM-10 rules relied on (as a result of the 2003 PM-10 Plan
commitments) as being BACM-level controls.
Response 10: As noted above, in its October 30, 2006 attainment
determination EPA suspended the 172(c)(9) contingency measure
requirement and as a result it is no longer an applicable part D
requirement. 71 FR 63642, 63663; 73 FR 22307, 22313. In any event, as
set forth above (see response to comment 2), independent of its
suspension, the contingency measure requirement is not an applicable
requirement for purposes of redesignation.
With respect to the section 189(b)(1)(B) BACM requirement, as
[[Page 66766]]
discussed in our proposed rule, EPA determined that this requirement
was met for the SJV nonattainment area in our approval of the 2003 PM-
10 Plan. See 69 FR 30006, 30035. (``EPA is approving the RACM/BACM
demonstration for all significant PM-10 and NOX sources in
the SJV as meeting the requirements of sections 189(a)(1)(C) and
189(b)(1)(B)''). In the 2003 PM-10 Plan the District addressed the BACM
requirement by providing enforceable commitments to implement BACM
rules in the future rather than already adopted rules. During the
rulemaking on the 2003 PM-10 Plan, EJ argued that until the relevant
BACM requirements are adopted and no longer subject to change in the
rule development process for each of these source categories, EPA could
not conclusively determine that the plan provides for the
implementation of BACM/BACT for all significant sources of PM-10 and
PM-10 precursors. In rejecting that argument we stated that:
[s]ection 189(b)(1)(B) requires that serious area PM-10 plans
include `[p]rovisions to assure that the best available control
measures for the control of PM-10 shall be implemented no later than
4 years after the date the area is classified (or reclassified) as a
Serious Area.' Nothing in this language either requires a state to
have adopted controls in place before a SIP revision can be approved
into its PM-10 plan or forbids the adoption of an enforceable
commitment to meet the statute's BACM [footnote omitted]
requirement.
Id. at 30013. We further stated, in fully approving commitments as
meeting the Act's BACM requirement that:
[c]onsistent with this statutory language, EPA has historically
determined that an enforceable commitment to adopt and implement
BACM in a SIP meets this statutory requirement since it constitutes
a `provision to assure that BACM is implemented' by a fixed
deadline. As a result, the commenters' complaint that `[b]y
definition the plan fails to implement BACM/BACT for all source
categories for which no developed control measures exist' has no
merit since the statute itself does not impose such a requirement.
Because the statute does not define what is a `provision to assure
BACM is implemented,' EPA may adopt an interpretation reasonably
accommodated to the purpose of the statutory provision. Chevron
U.S.A., Inc. v. Natural Resources Defense Council, 467 U.S. at 842-
44.
Id. at 30013-30014. In conclusion we stated that:
In accepting enforceable commitments to meet the requirements of
section 189(b)(1)(B), however, EPA has required states to undertake
an analysis to ensure that the regulation ultimately adopted
pursuant to the commitment will represent a BACM level of control.
As we describe in our proposed rule, a state must determine the
technical and economic feasibility of potential control measures for
each of the significant source categories. 69 FR 5412, 5418. Thus
the measure that is the subject of a commitment must describe
generally the type and level of control to be adopted.
Moreover, once the ultimate control measure is adopted and
submitted to EPA, the Agency undertakes an additional evaluation to
ensure that that measure meets the statute's BACM requirements. See,
e.g., the Arizona rulemakings in which EPA initially approved as
RACM [footnote omitted] a requirement in a state statute to adopt
and implement best management practices for agricultural operations
and subsequently determined that the rules adopted pursuant to the
statute represented RACM/BACM. 64 FR 34726 (June 29, 1999); 66 FR
51869 (October 11, 2001); 67 FR 48718 (July 25, 2002).
Id. at 30014. EPA's interpretation and its full SIP approval of the
BACM requirement was not challenged. EPA may rely on prior SIP
approvals in approving a redesignation request. Calcagni memorandum at
3; Southwestern Pennsylvania Growth Alliance v. Browner, 144 F.3d. 984.
989-990 (6th Cir. 1998); and Wall v. EPA, 265 F.3d 526 (6th Cir. 2001).
Finally we note that EPA has approved many of the rules submitted by
the State as meeting a BACM level of control. See the Federal Register
notices listed in Tables 1 and 2 above in which we approve SJVAPCD PM-
10 and NOX rules.
Comment 11: EJ also claims that the District has failed to submit
to EPA a demonstration that the quantitative milestones as required by
CAA section 189(c)(1) and (c)(2) and the section 189(d) 5 percent
requirement have been met. EJ also claims that the District has not met
its commitment to update and improve the 2003 PM-10 Plan by March 2006.
Response 11: CAA section 107(d)(3)(E)(v) requires that a state
seeking redesignation of an area to attainment must have met all
requirements applicable to the area under section 110 and part D. In
interpreting this requirement EPA has stated that ``any requirements
that came due prior to submittal of the redesignation request must be
fully approved into the plan at or before the time EPA redesignates the
area.'' Calcagni memorandum at 5. Sierra Club v. EPA, 375 F.3d 537 (7th
Cir. 2004). EPA has approved the 2003 PM-10 Plan's RFP demonstration as
meeting the requirements of 172(c)(2) and 189(c)(1) and has approved
the plan as meeting the quantitative milestones requirement in section
189(c)(1). 69 FR 30006, 30034. Also, as we explained in our 2006
attainment finding, we believe that once an area attains the NAAQS the
requirements of section 189(c)(2) with respect to milestones no longer
applies under the Agency's Clean Data Policy. 71 FR 63642, 63646-63647.
We also explained in that rulemaking the application of the Clean Data
Policy to PM-10. See 71 FR 40952, 40954-40955 and 71 FR 63642, 63643-
63645. Apart from the Clean Data Policy, for an area that has attained
the standard and is eligible for redesignation, the requirements for
milestone demonstrations under section 189(c) have no further meaning
or function. Therefore the District was not required to submit
milestone demonstrations pursuant to section 189(c).
In addition, EPA approved a commitment in the 2003 PM-10 Plan by
the State to submit a SIP revision by March 31, 2006 based on a mid-
course review to determine whether the level of emission reductions in
the plan is sufficient to attain the PM-10 standards. 69 FR 30006,
30035. EPA approved this commitment as part of the Plan's attainment
demonstration. See 69 FR 5412, 5429. While the SJVAPCD adopted a mid-
course review SIP addressing the quantitative milestone reporting
requirement and mid-course review SIP commitment and submitted the SIP
to the State, the State has not submitted the mid-course review SIP to
EPA. Nevertheless, EPA's full approval of the attainment demonstration
in the 2003 PM-10 Plan fully satisfies the requirement of CAA section
107(d)(3)(E)(v).
Moreover, EPA has determined that the SJV area attained the PM-10
standard in 2005, and continues to attain the standard. The mid-course
review requirement is not a requirement under section 110 or Part D,
and therefore is not an applicable CAA requirement for purposes of
redesignation. Furthermore, even if it were, the requirement for a mid-
course review was approved as part of the attainment demonstration.
Therefore, because EPA has determined that the SJV area is attaining
the PM-10 standard, a submission under the mid-course review provision
would not be required for purposes of redesignation. 57 FR 13498,
13564; Clean Data Policy.
Comment 12: EJ claims that EPA misinterprets an October 14, 1994
memorandum from Mary Nichols, EPA, entitled ``Part D NSR Requirements
for Areas Requesting Redesignation to Attainment'' as allowing the
District to replace its new source review (NSR) program with a
prevention of significant deterioration (PSD) program. EJ quotes the
memorandum as saying that ``the part D program may be replaced by the
corollary PSD program, if it is shown
[[Page 66767]]
through the maintenance demonstration that the area will maintain
without part D NSR.'' EJ asserts that here neither EPA nor the District
has made any such demonstration and claims that this is especially
worrisome in light of EPA's recent proposed approval of revisions to
the District's NSR program exempting ``so-called minor agricultural
sources such as industrial dairy operations.''
Response 12: First, the commenter overlooks the fact, enunciated in
our proposed rule, that EPA has previously fully approved the NSR
program for the SJV area. We also noted that EPA has recently proposed
approval of some revisions to the NSR rule. 73 FR 22307, 22313. EJ's
citation to the October 14, 1994 memorandum from Mary Nichols, EPA,
entitled ``Part D NSR Requirements for Areas Requesting Redesignation
to Attainment'' (Nichols memorandum) is misdirected. The Nichols
memorandum's discussion of the need to demonstrate maintenance without
fully approved NSR addressed the situation, not the case here, where an
area's NSR rule has not been approved. Moreover, as our proposed rule
explained, even though EPA previously approved the NSR rule, such
approval is not a prerequisite to finalizing our approval of the
State's redesignation request. Id. If an area does not have a fully
approved NSR program, it can still be redesignated if it shows
maintenance without NSR in effect. The 2003 PM-10 Plan and 2007 Plan do
not rely on reductions from the area's NSR program. Nothing in the
plans' inventories or estimated emissions reductions indicates any
reliance on NSR program reductions. Thus, the SJVAB area will maintain
the NAAQS without NSR. This is consistent with the provisions of the
Nichols memorandum. Finally, we note that while the PSD requirements
will apply once the area has been redesignated to attainment, the
District's SIP-approved NSR rule will continue to apply with respect to
PM-10 until EPA approves a revised NSR rule.
E. Maintenance Plan
Comment 13: EJ maintains that even if all of the other issues it
has raised with respect to the redesignation were remedied, EPA cannot
approve the redesignation request because the maintenance plan is
flawed and cannot be approved. EJ concludes that EPA's decision to
approve the maintenance plan without the requisite analysis and without
meeting the basic requirements laid out in the Calcagni memorandum
leaves little for EJ to comment upon and, as such, is the very
definition of arbitrary and capricious. EJ believes that EPA's
obligation is to provide not just its legal conclusions but the facts
and rationale that support them.
Response 13: EPA disagrees. Our proposed rule lays out all of the
requirements for maintenance plans found under the CAA and the Calcagni
memorandum and sets forth the Agency's analysis of how the 2007 Plan
meets each of those requirements. 73 FR 22307, 22313-22315. In
addition, the 2007 Plan itself addresses in detail the requirements in
the Calcagni memorandum. Thus EJ's contention that EPA's discussion of
the maintenance plan left them ``very little'' to comment on is without
basis.
Comment 14: EJ asserts that the 2005 emissions inventory is
insufficient to identify the level of emissions in the area because the
continuing PM-10 problem is the result of direct PM-10 emissions during
the fall rather than secondary wintertime NOX emissions and
the direct PM-10 inventory is expected to increase over the next 10
years. EJ states that EPA's claim that increasing direct PM-10
emissions are offset by a larger decrease in the NOX
inventory demonstrates a lack of understanding of the PM-10 problem in
the SJV nonattainment area because reducing secondarily formed PM-10
does nothing to reduce the ongoing direct PM-10 problems. EJ concludes
that since the maintenance demonstration is based on an inventory that
is insufficient to attain the NAAQS, EPA cannot find that the plan will
maintain healthful air for 10 years following redesignation.
In a footnote to its comment above regarding the emissions
inventory for the maintenance plan, EJ claims that prior to 2004 the
District had never asked EPA to waive PM-10 data but in the past 4
years it has been asked to waive 11 separate events, 10 of them after
the Agency's original attainment finding. EJ states that if windy days
are this common EPA and the District must accept that the SJV
nonattainment area has a windblown dust problem and they must do more
to control it. EJ states that an event is only exceptional if it is not
expected to recur on a regular basis.
Response 14: As discussed in our proposed rule, the Calcagni
memorandum provides that a state should provide an attainment emissions
inventory to identify the level of emissions in the area sufficient to
attain the NAAQS and, where the state as here has made an adequate
demonstration that air quality has improved as a result of the SIP (see
above responses to comments 3 through 4 and 6 through 8), the
attainment inventory will generally be an inventory of actual emissions
at the time the area attained.
The 2007 Plan does exactly what the Calcagni memorandum recommends
and selects the 2005 PM-10 and NOX inventories as the
attainment emission inventories because the SJV area attained the
standard in 2005. 73 FR 22307, 22314 and 71 FR 63642. The SJV area
relies on reductions of both NOX (a PM-10 precursor) and
directly emitted PM-10 sources to achieve attainment. 2003 PM-10 Plan
at ES-9 through ES-10, Chapters 2, 4 and 5; 69 FR 5412, 5414 and 69 FR
30006, 30007. Analysis of ambient air quality data for the SJV area
shows that it experiences the most frequent and severe exceedances from
October through January during stagnant weather conditions (i.e., low
wind speeds that are unable to disperse the PM-10).\9\ Both direct PM-
10 and secondary PM-10 (formed by reactions with NOX ) occur
during this time. October and November exceedances are dominated by
direct PM-10 emissions and December and January are dominated by
secondary PM-10 such as ammonium nitrate (formed when NOX
reacts with ammonia and other components); however, the reduction of
both direct PM-10 and NOX is necessary for reducing ambient
PM-10 levels throughout the year. 2003 PM-10 Plan at ES-9 through ES-10
and 5-6 through 5-7. Thus, EPA's belief that the slight increase in PM-
10 emissions of 284 tpd in 2005 to 290 tpd in 2020 is insignificant
when compared to the substantial NOX decreases of 606 tpd in
2005 to 328 tpd in 2020 is based on an understanding that high PM-10
levels in the SJV area are caused by both direct PM-10 and precursor
NOX emissions. In addition, consistent with the Calcagni
memorandum, the modeled maintenance demonstration is primarily based on
modeling similar to the modeling used for the 2003 PM-10 Plan. 73 FR
22307, 22314. Finally, contrary to EJ's comments, there is no ongoing
direct PM-10 problem in the SJVAB as we have determined that the area
has attained the PM-10 standard. 71 FR 63642 and 73 FR 14687. See also
response to comment 1.
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\9\ As discussed in our attainment affirmation and proposed
rule, unusually high winds can also cause exceedances. 73 FR 14687
and 73 FR 22307, 22311.
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EJ's comment in footnote 3 of its letter does not appear to be
related to the inventory or any other provision of the maintenance plan
in the 2007 Plan or the maintenance plan requirement of CAA section
107(d)(3)(E)(iv). Rather it appears to be an expansion of EJ's argument
that the SJV area has not in fact attained the PM-10 standard. In this
[[Page 66768]]
regard, see response to comment 1 above. Notwithstanding , EPA notes
that not all of the exceptional event days in the past five years in
the SJV area have been due to high winds. Of the eleven exceptional
event days, seven were caused by high wind events and the remaining
four by construction, improper monitor siting and fireworks.
Comment 15: EJ states that it is not clear whether the modeling
takes into account the September 2004 and November 2005 exceedances EPA
has conceded but if it does not then the modeling for the maintenance
plan is flawed because it fails to include these higher values in its
projections.
Response 15: As discussed in our proposed rule, 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. 73 FR 22307, 22314-22315. See also Calcagni
memorandum at 9 and Wall v. EPA, 265 F.3d 426 (6th Cir. 2001). While
only required to use one of these methods, the SJVAPCD showed both with
emissions inventory and modeling that the area would maintain the
standard for at least ten years after redesignation, in accordance with
section 175A. For areas such as the SJV that used modeling for their
attainment demonstrations, the same level of modeling should be used
for the maintenance demonstrations. The 2007 Plan uses Chemical Mass
Balance (CMB) and rollback to demonstrate maintenance of the 24-hour
PM-10 standard until 2020 which is consistent with the modeling
performed for the 2003 PM-10 Plan. 73 FR 22307, 22314; 2007 Plan at 6-
11. The modeling involves selecting a representative day for each
location, determining the speciation data for the site based on
analysis of the monitoring filters and sources in the area and
determining the emissions reductions that are necessary or that will be