Approval and Promulgation of State Implementation Plans for Air Quality Planning Purposes; California-South Coast and Coachella, 43663-43673 [05-14931]
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Federal Register / Vol. 70, No. 144 / Thursday, July 28, 2005 / Proposed Rules
(3) From subsections (d)(1), (2), (3),
and (4) because these provisions
concern individual access to and
amendment of records contained in this
system, which consists of
counterterrorism, investigatory and
intelligence records. Compliance with
these provisions could alert the subject
of an investigation pertaining to
terrorism of the fact and nature of the
investigation, and/or the investigative
interest of the FBI and/or other
intelligence or law enforcement
agencies; compromise sensitive
information classified in the interest of
national security; interfere with the
overall law enforcement process by
leading to the destruction of evidence,
improper influencing of witnesses,
fabrication of testimony, and/or flight of
the subject; could identify a confidential
source or disclose information which
would constitute an unwarranted
invasion of another’s personal privacy;
reveal a sensitive investigative or
intelligence technique; or constitute a
potential danger to the health or safety
of law enforcement personnel,
confidential informants, and witnesses.
Amendment of these records would
interfere with ongoing counterterrorism
investigations and analysis activities
and impose an impossible
administrative burden by requiring
investigations, analyses, and reports to
be continuously reinvestigated and
revised.
(4) From subsection (e)(1) because it
is not always possible for TSC to know
in advance what information is relevant
and necessary for it to complete an
identity comparison between the
individual being screened and a known
or suspected terrorist. Also, because
TSC and the FBI may not always know
what information about an encounter
with a known or suspected terrorist will
be relevant to law enforcement for the
purpose of conducting an operational
response.
(5) From subsection (e)(2) because
application of this provision could
present a serious impediment to
counterterrorism efforts in that it would
put the subject of an investigation, study
or analysis on notice of that fact, thereby
permitting the subject to engage in
conduct designed to frustrate or impede
that activity. The nature of
counterterrorism investigations is such
that vital information about an
individual frequently can be obtained
only from other persons who are
familiar with such individual and his/
her activities. In such investigations it is
not feasible to rely upon information
furnished by the individual concerning
his own activities.
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(6) From subsection (e)(3), to the
extent that this subsection is interpreted
to require TSC to provide notice to an
individual if TSC receives information
about that individual from a third party.
Should the subsection be so interpreted,
exemption from this provision is
necessary to avoid impeding
counterterrorism efforts by putting the
subject of an investigation, study or
analysis on notice of that fact, thereby
permitting the subject to engage in
conduct intended to frustrate or impede
that activity.
(7) From subsection (e)(5) because
many of the records in this system are
derived from other domestic and foreign
agency record systems and therefore it
is not possible for the FBI and the TSC
to vouch for their compliance with this
provision, however, the TSC has
implemented internal quality assurance
procedures to ensure that TSC terrorist
screening data is as thorough, accurate,
and current as possible. In addition,
TSC supports but does not conduct
investigations; therefore, it must be able
to collect information related to terrorist
identities and encounters for
distribution to law enforcement and
intelligence agencies that do conduct
terrorism investigations. In the
collection of information for law
enforcement, counterterrorism, and
intelligence purposes, it is impossible to
determine in advance what information
is accurate, relevant, timely, and
complete. With the passage of time,
seemingly irrelevant or untimely
information may acquire new
significance as further investigation
brings new details to light. The
restrictions imposed by (e)(5) would
limit the ability of those agencies’
trained investigators and intelligence
analysts to exercise their judgment in
conducting investigations and impede
the development of intelligence
necessary for effective law enforcement
and counterterrorism efforts. The TSC
has, however, implemented internal
quality assurance procedures to ensure
that TSC terrorist screening data is as
thorough, accurate, and current as
possible.
(8) From subsection (e)(8) because to
require individual notice of disclosure
of information due to compulsory legal
process would pose an impossible
administrative burden on the FBI and
the TSC and could alert the subjects of
counterterrorism, law enforcement, or
intelligence investigations to the fact of
those investigations when not
previously known.
(9) From subsection (g) to the extent
that the system is exempt from other
specific subsections of the Privacy Act.
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43663
Dated: July 22, 2005.
Paul R. Corts,
Assistant Attorney General for
Administration.
[FR Doc. 05–14850 Filed 7–27–05; 8:45 am]
BILLING CODE 4410–02–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 52
[CA–314–0483; FRL–7945–4]
Approval and Promulgation of State
Implementation Plans for Air Quality
Planning Purposes; California—South
Coast and Coachella
Environmental Protection
Agency (EPA).
ACTION: Proposed rule.
AGENCY:
SUMMARY: EPA is proposing to approve
state implementation plan (SIP)
revisions submitted by the State of
California to provide for attainment of
the particulate matter (PM–10) national
ambient air quality standards (NAAQS)
in the Los Angeles-South Coast Air
Basin and the Coachella Valley Area,
and to establish emissions budgets for
these areas for purposes of
transportation conformity. EPA is also
proposing to approve revisions to
fugitive dust regulations and ordinances
for the areas. EPA is proposing to
approve these SIP revisions under
provisions of the Clean Air Act (CAA)
regarding EPA action on SIP submittals,
SIPs for national primary and secondary
ambient air quality standards, and plan
requirements for nonattainment areas.
DATES: Written comments on this
proposal must be received by August 29,
2005.
ADDRESSES: Please mail comments to:
Dave Jesson (AIR–2), EPA Region IX, 75
Hawthorne Street, San Francisco, CA
94105–3901, or e-mail to
jesson.david@epa.gov. The rulemaking
docket for this proposal is available for
public inspection during normal
business hours at EPA’s Region IX
office. A reasonable fee may be charged
for copying parts of the docket.
Copies of the SIP materials are also
available for inspection at the following
locations:
California Air Resources Board, 1001 I
Street, Sacramento, California 95812.
South Coast Air Quality Management
District, 21865 E. Copley Drive,
Diamond Bar, California 91765.
The 2003 Air Quality Management
Plan, which includes the South Coast
PM10 plan, is electronically available at:
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https://www.aqmd.gov/aqmp/
AQMD03AQMP.htm.
The 2003 Coachella Valley PM10
State Implementation Plan is at: https://
www.aqmd.gov/aqmp/docs/
f2003cvsip.pdf.
The fugitive dust rules are
electronically available at: https://
www.aqmd.gov/rules/rulesreg.html.
FOR FURTHER INFORMATION CONTACT:
Dave Jesson, EPA Region IX, at (415)
972–3957, or jesson.david@epa.gov.
SUPPLEMENTARY INFORMATION:
Throughout this document, ‘‘we,’’ ‘‘us,’’
and ‘‘our’’ refer to EPA.
Table of Contents
I. Background
A. Summary
B. PM–10 Problem in the South Coast and
Coachella Valley
C. CAA Planning Provisions
D. Designation and Classification
E. Adoption and Submittal of these
Revisions
II. Evaluation of the SIP Submittals
A. Emission Inventories
B. Control Measures
1. Applicable Requirements
2. Description of South Coast Control
Measure Commitments
3. Proposed Action on South Coast Control
Measures
C. Regulations and Ordinances
1. Description of Regulations and
Ordinances
a. SCAQMD Rule 403—Fugitive Dust
b. SCAQMD Rule 403.1—Supplemental
Fugitive Dust Control Requirements for
Coachella Valley
c. SCAQMD Rule 1186—PM10 Emissions
from Paved and Unpaved Roads, and
Livestock Operations
d. Coachella Valley Local Ordinances
2. Proposed Action on Regulations and
Ordinances
D. Contingency Measures
E. Reasonable Further Progress (RFP) and
Milestones
1. South Coast
2. Coachella Valley
F. Attainment Demonstrations
1. South Coast
2. Coachella Valley
G. Motor Vehicle Emission Budgets
1. South Coast
2. Coachella Valley
III. Summary of EPA’s Proposed Action
IV. Administrative Requirements
I. Background
A. Summary
We are proposing to approve 2003
plan amendments for the South Coast
Air Basin (or ‘‘South Coast’’), as the plan
amendments pertain to attainment of
the 24-hour and annual PM–10
NAAQS.1 We are proposing to approve
1 The nonattainment area includes all of Orange
County and the more populated portions of Los
Angeles, San Bernardino, and Riverside Counties.
For a description of the boundaries of the Los
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revisions to the PM–10 plan for the
Coachella Valley Planning Area
(‘‘Coachella Valley’’).2 We are also
proposing to approve the plans’ PM–10
motor vehicle emissions budgets for
purposes of transportation conformity.
Finally, we are proposing to approve
revisions to Rules 403, 403.1, and 1186
of the South Coast Air Quality
Management District (SCAQMD)
regulating fugitive dust emissions, and
revisions to fugitive dust ordinances for
Coachella Valley jurisdictions. These
revisions update, improve, strengthen,
and supplement the approved SIP
provisions for control of PM–10 and
PM–10 precursors in the two areas.
B. PM–10 Problem in the South Coast
and Coachella Valley
Although great progress has been
made in reducing PM–10
concentrations, the South Coast and
Coachella Valley continue to violate the
PM–10 NAAQS, and the State must
therefore adopt, submit, and implement
measures and other provisions sufficient
to make expeditious progress and attain
the NAAQS by the applicable deadline.3
The SCAQMD has adopted and the
State has submitted PM–10 attainment
Angeles-South Coast Air Basin Area, see 40 CFR
81.305.
2 The Coachella Valley Planning Area is in central
Riverside County in the Salton Sea Basin. The
boundary is defined at 40 CFR 81.305.
3 The health effects from elevated PM–10
concentrations include lung damage, respiratory
and cardio-vascular disease, and premature death.
Children, the elderly, and people suffering from
heart and lung diseases, such as asthma, are
especially at risk.
EPA revised the NAAQS for particulate matter on
July 1, 1987 (52 FR 24672), replacing standards for
total suspended particulates with new standards
applying only to particulate matter up to 10
microns in diameter (PM–10). At that time, EPA
established two PM–10 standards. The annual PM–
10 standard is attained when the expected annual
arithmetic mean of the 24-hour samples averaged
over a 3-year period does not exceed 50 micrograms
per cubic meter (µg/m3). The 24-hour PM–10
standard of 150 µg/m3 is attained if samples taken
for 24-hour periods have no more than one
expected exceedance per year, averaged over 3
years. See 40 CFR 50.6 and 40 CFR part 50,
appendix K.
On July 18, 1997, EPA reaffirmed the annual PM–
10 standard, and slightly revised the 24-hour PM–
10 standard (652 FR 38651). In the same action,
EPA also established two new standards for PM,
both applying only to particulate matter up to 2.5
microns in diameter (PM–2.5).
This SIP submittal addresses the 24-hour and
annual PM–10 standards as originally promulgated.
An opinion issued by the U.S. Court of Appeals for
the D.C. Circuit in American Trucking Assoc., Inc.,
et al. v. USEPA, No. 97–1440 (May 14, 1999), among
other things, vacated the 1997 standards for PM–10.
However, the PM–10 standards promulgated on July
1, 1987 were not an issue in this litigation, and the
Court’s decision does not affect the applicability of
those standards in the South Coast and Coachella
Valley areas. Codification of those standards
continues to be recorded at 40 CFR 50.6. See also
69 FR 45592, July 30, 2004.
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plans and regulations for these two
areas in past years. In 2003, we fully
approved PM–10 progress and
attainment plans for the South Coast
and Coachella Valley as meeting all
CAA requirements for serious PM–10
areas, and as part of those actions we
also granted attainment date extensions
for the areas for both the 24-hour and
annual PM–10 NAAQS, from December
31, 2001 to December 31, 2006,
pursuant to CAA section 188(e). For
more information on the currently
approved South Coast and Coachella
Valley PM–10 plans (‘‘2002 SIPs’’),
please see our proposed and final
rulemaking notices. The proposals were
issued on December 17, 2002 (67 FR
77212 and 67 FR 77204) and the final
approvals were issued on April 18, 2003
(68 FR 19316 and 68 FR 19318). We
have also previously approved
SCAQMD fugitive dust regulations and
Coachella Valley local ordinances for
the control of fugitive dust. See
approvals of SCAQMD Rules 403, 403.1,
and 1186, and 10 Coachella Valley
ordinances published on December 9,
1998 (63 FR 67784), and again on
February 17, 2000 (65 FR 8057),
following SCAQMD adoption of
amendments strengthening Rules 403
and 1186. This proposed action simply
addresses updates and improvements to
the 2002 SIPs for the South Coast and
Coachella Valley, the SCAQMD fugitive
dust regulations, and the Coachella
Valley ordinances, adopted as part of
the attainment plans for the South Coast
and Coachella Valley.
C. CAA Planning Provisions
The Federal CAA was substantially
amended in 1990 to establish new
planning requirements and attainment
deadlines for the NAAQS. The most
fundamental of these nonattainment
area provisions applicable to the South
Coast and Coachella Valley is the
requirement that the State submit a SIP
demonstrating attainment of the PM–10
NAAQS. This demonstration must be
based upon enforceable measures to
achieve emission reductions leading to
emissions at or below the level
predicted to result in attainment of the
NAAQS throughout the nonattainment
area. The measures must meet the
standard for Best Available Control
Measures (BACM), and the measures
must be implemented expeditiously and
ensure attainment no later than the
applicable CAA deadline. CAA section
189(b). Because the State requested an
extension of the attainment date for the
South Coast and Coachella Valley
beyond the applicable deadline of
December 31, 2001, under CAA section
188(e) the State must demonstrate that
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the plans include the most stringent
measures (MSM) that are included in
any implementation plan or are
achieved in practice, and can feasibly be
implemented in the area.
EPA has issued a ‘‘General Preamble’’
describing the Agency’s preliminary
views on how EPA intends to act on
SIPs submitted under Title I of the Act.
See 57 FR 13498 (April 16, 1992), 57 FR
18070 (April 28, 1992). EPA later issued
an Addendum to the General Preamble
providing guidance on SIP requirements
for serious PM–10 areas. 59 FR 41998
(August 16, 1994). The reader should
refer to these documents for a more
detailed discussion of EPA’s
preliminary interpretations of Title I
requirements. In this proposed
rulemaking action, EPA applies these
policies to the South Coast and
Coachella Valley PM–10 SIP submittals,
taking into consideration the specific
factual issues presented.
D. Designation and Classification
On the date of enactment of the 1990
CAA Amendments, PM–10 areas,
including the South Coast and
Coachella Valley, meeting the
qualifications of section 107(d)(4)(B) of
the amended Act, were designated
nonattainment by operation of law. See
56 FR 11101 (March 15, 1991).
Once an area is designated
nonattainment, section 188 of the CAA
outlines the process for classification of
the area and establishes the area’s
attainment date. In accordance with
section 188(a), at the time of
designation, all PM–10 nonattainment
areas, including the South Coast and
Coachella Valley, were initially
classified as moderate by operation of
law. Section 188(b)(1) of the Act further
provides that moderate areas can
subsequently be reclassified as serious
before the applicable moderate area
attainment date if at any time EPA
determines that the area cannot
‘‘practicably’’ attain the PM–10 NAAQS
by this attainment date.
EPA determined on January 8, 1993,
that the South Coast and Coachella
Valley could not practicably attain the
PM–10 NAAQS by the applicable
attainment deadline for moderate areas
(December 31, 1994, per section
188(c)(1) of the Act), and reclassified the
area as serious (58 FR 3334). In
accordance with section 189(b)(2) of the
Act, the State was required to make the
following SIP submittals. First, the State
had to submit by August 8, 1994, a SIP
to ensure the implementation of BACM
no later than 4 years after
reclassification, as required by CAA
section 189(b)(1)(B). Second, the State
had to submit a SIP by February 8, 1997,
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providing for progress and expeditious
attainment, as required by CAA section
189(b)(1)(A).
E. Adoption and Submittal of These
Revisions
For a description of the history and
content of the 2002 SIPs, rules, and
ordinances for the South Coast and
Coachella Valley, please see our
proposed and final rules cited above. On
August 1, 2003, the SCAQMD adopted
the 2003 South Coast Air Quality
Management Plan (‘‘2003 South Coast
AQMP’’) and the 2003 Coachella Valley
PM10 State Implementation Plan (‘‘2003
Coachella Valley Plan’’), including the
motor vehicle emissions budgets for the
areas.4 The California Air Resources
Board (CARB) approved the plans on
October 23, 2003, and submitted the
plans to us on January 9, 2004. We
determined that these submittals were
complete on February 18, 2004,
pursuant to CAA section 110(k)(1)(B)
and 40 CFR part 51, Appendix V.
On April 2, 2004, the SCAQMD
adopted revisions to Rules 403, 403.1,
and 1186, and CARB submitted the
revisions on July 29, 2004. On August
10, 2004, we determined the submittal
to be complete. On November 16, 2004,
CARB submitted revised Coachella
Valley ordinances, which were adopted
by the local jurisdictions on various
dates in 2003 and 2004, and the
implementation handbooks for Rules
403 and 403.1, which were
inadvertently omitted from the April 2,
2004 SIP submittal. On April 6, 2005,
we determined the submittal to be
complete.
Both the SCAQMD and CARB
satisfied applicable statutory and
regulatory requirements for reasonable
public notice and hearing prior to
adoption of the SIP revisions. The
SCAQMD conducted numerous public
workshops, and properly noticed the
public hearings at which the plans and
rules were adopted. The SIP submittals
include proof of publication for notices
of the public hearings. The local
Coachella Valley jurisdictions properly
noticed and adopted the fugitive dust
ordinances. Therefore, we conclude that
the SIP submittals have met the public
notice and involvement requirements of
section 110(a)(1) of the CAA.
4 In addition to PM–10, the 2003 South Coast
AQMP addressed the NAAQS for carbon monoxide
(CO), ozone, and nitrogen dioxide (NO2). We will
take separate action on the plan with respect to
these standards.
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II. Evaluation of the SIP Submittals
A. Emission Inventories
CAA section 172(c)(3) requires that all
nonattainment area plan submittals
include a comprehensive, accurate, and
current inventory of actual emissions
from all sources in the area.
The emission inventories in the 2003
South Coast AQMP and the 2003
Coachella Valley Plan supersede those
in the 2002 SIPs for these areas. The
revised 2003 South Coast AQMP
includes summary emission inventories
for major source categories in tons per
annual average day for VOC, NOX, CO,
SOX, TSP, PM–10, and PM–2.5 for the
1997 base year (Table 3–1A) and the
2006 attainment year (Table 3–3A).
Appendix III (Base and Future Year
Emission Inventories) to the 2003 South
Coast AQMP provides more detailed
emissions inventories for 1995, 1997,
2000, 2002, 2003, 2005, 2006, and
various later years. Appendix IV–A also
includes additional emissions data,
including control category baseline
emissions for 1997, 2006, and 2010, and
estimates of baseline emissions and
emission reductions from each of the
2003 South Coast AQMP control
measures for 2006 and 2010 for primary
PM–10 or PM–10 precursors (NOX, SOX,
VOC, and ammonia), as applicable to
the measure. Appendix III documents
the source of the data and references
SCAQMD and CARB reports that
provide detailed information on the
methodologies used to estimate
emissions from area sources. Finally,
Appendix V (Modeling and Attainment
Demonstrations) includes estimated
average annual day emission reductions
by control measure for PM–10, VOC,
NOX, and SOX in 2006 in the South
Coast.
The 2003 Coachella Valley Plan
includes annual average and maximum
24-hour emission inventories for 1995
(Table 2–2), 2000 (Table 2–3), 2003
(Table 2–4), and 2006 (Table 2–5).
The principal emissions inventory
enhancements of the revised plans are
the use of more accurate emissions
factors and models and updated activity
levels for emissions associated with
mobile sources, including: (1) The use
of the latest EPA-approved California
motor vehicle emissions factor model
(EMFAC2002) 5 and the most recent
motor vehicle activity data from the
Southern California Association of
Governments (SCAG); (2) an improved
methodology for estimating paved road
5 We approved use of EMFAC2002 on April 1,
2003 (68 FR 15722) for use in SIPs and conformity
analyses. EMFAC2002 produces California-specific
emissions for the full range of motor vehicles.
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dust emissions 6; and (3) CARB’s new
nonroad mobile source model (the
OFFROAD model). The emission
inventories for the South Coast Air
Basin also use the results of special
studies of aircraft, marine vessels,
composting, and ammonia emissions
(see Appendix III of the 2003 South
Coast AQMP, pages III–1–13 to III–1–
14), and more accurate emissions factors
for the windblown dust category, based
on use of climate, wind speed, and soil
data representative of Southern
California.
The emission inventories in the 2003
South Coast AQMP and 2003 Coachella
Valley Plan are complete with respect to
sources that have been found to
contribute to PM–10 violations. The
inventories employ activity levels,
emission factors, and growth projections
that are current and reflective of the best
available emissions information.
Because they are current, accurate,
and complete, we propose to approve as
meeting the provisions of CAA section
172(c)(3) the South Coast emission
inventories in Chapter 3 (Tables 3–1A
and 3–3A), Appendix III (Tables A–1,
A–2, A–3, A–5, and A–7), and
Appendix V of the 2003 South Coast
AQMP (Attachment 4), and the
Coachella Valley emission inventories
in Tables 2–2, 2–3, 2–4, and 2–5 of the
2003 Coachella Valley Plan.
B. Control Measures
We recently approved the control
measure portions of the 2002 SIPs for
the South Coast and Coachella Valley.
The 2003 South Coast AQMP makes
minor modifications to the previously
approved SCAQMD commitments to
adopt control measures. Although the
2003 South Coast AQMP includes
changes to the control measure
commitments by CARB and SCAG,
these new and amended commitments
apply only to the ozone portion of the
plan, and therefore are not part of this
proposed action. The 2003 Coachella
Valley Plan includes no changes to the
control measure commitments in the
2002 SIP.
1. Applicable Requirements
Because the South Coast Air Basin
and Coachella Valley are classified as
serious for PM–10, the nonattainment
plans for these areas must include
measures that reflect a BACM level of
control for each source category that
6 We recently approved this methodology as part
of our adequacy determination for the motor vehicle
emissions budgets in the revised South Coast and
Coachella Valley PM–10 plans. See 58 FR 15326,
March 25, 2004. The methodologies are discussed
on page III–1–12 of Appendix III of the 2003 South
Coast AQMP.
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contributes significantly to a violation of
the 24-hour or annual PM–10 NAAQS.7
For a discussion of the BACM and MSM
provisions applicable to these areas and
our determination that the 2002 SIPs for
the South Coast and Coachella Valley
fully met these requirements, see the
discussion in the proposed approval of
the plans at 67 FR 77215 and 67 FR
77207 (December 17, 2002).8
In the 2002 SIPs for the South Coast
and Coachella Valley, SCAQMD
determined which source categories are
‘‘significant,’’ as part of the BACM
analysis.9 Please refer to 67 FR 77215–
6 and 67 FR 77207–9 (December 17,
2002) for a summary of the BACM
determinations of significant categories
in the 2002 SIPs for South Coast and
Coachella Valley. Updates to the
emissions inventories in the 2003 South
Coast AQMP and the 2003 Coachella
Valley Plan did not change the
7 The plans must also satisfy lesser control
measure provisions applicable to moderate areas,
Reasonably Available Control Measures (RACM) for
areas sources such as fugitive dust, and Reasonably
Available Control Technology (RACT) for stationary
sources such as commercial and industrial
operations. In approving the 2002 SIPs, we did not
make an independent assessment of the plans’
control measures against the RACM and RACT
requirements, since the plans would meet RACM
and RACT requirements if they were found to meet
the BACM requirement.
8 Our final rules on the 2002 SIPs included our
determination that the CAA provisions relating to
BACM (section 189(b)(1)(B)) and MSM (section
188(e)) were fully met by the South Coast and
Coachella Valley control measures, which consisted
of: (1) Enforceable commitments to adopt and
implement regulations; and (2) fully adopted
regulations and ordinances, including those fugitive
dust rules and ordinances we had previously
approved (SCAQMD Rules 403, 403.1, and 1186,
and Coachella Valley fugitive dust ordinances). See
68 FR 19316 and 68 FR 19318 in the final rules.
9 By analogy to Title I Part C of the Clean Air Act
relating to Prevention of Significant Deterioration
(PSD), EPA interprets BACM for serious PM–10
areas as generally similar to the definition of Best
Available Control Technology (BACT) for the PSD
program. PM–10 BACM is therefore defined as ‘‘the
maximum degree of emissions reduction of PM–10
and PM–10 precursors from a source * * * which
is determined on a case-by-case basis, taking into
account energy, environmental, and economic
impacts and other costs, to be achievable for such
source through application of production processes
and available methods, systems, and techniques for
control of each such pollutant.’’ General Preamble
Addendum, 59 FR 42010 (August 16, 1994).
EPA exempts from the BACM requirement de
minimis source categories, which do not contribute
significantly to nonattainment. EPA has generally
relied on the criteria applied under the new source
permit programs (40 CFR 51.165(b)) and has
therefore presumed that a source category
contributes significantly to a violation of the 24hour NAAQS if its impact at the location of
expected violation would exceed 5 µg/m3, and
would contribute significantly to a violation of the
annual NAAQS if its impact at the time and
location of the expected violation would exceed 1
µg/m3. 59 FR 42011. However, states must also
review the potential to attain earlier through
application of controls on anthropogenic sources
below these general levels.
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determinations of significant source
categories in the 2002 SIPs. As a result,
the revised plans continue the prior
determinations of applicable BACM,
which we approved in our April 18,
2003 final rule (see 68 FR 19316, and 68
FR 19318). The revised plans, rules, and
ordinances strengthen the 2002 SIPs’
control requirements for primary PM
and (in the case of the South Coast) the
applicable secondary precursors.
Therefore, these plan updates also do
not recreate the 2002 SIPs’
demonstrations, pursuant to CAA
section 188(e), that the plans include
the most stringent measures.10
Finally, the control measures in the
serious area plans must be sufficient to
achieve expeditious attainment by the
applicable deadline. As discussed
below, the revised SIPs update and
improve the progress and attainment
provisions in the 2002 SIPs, and we
propose to conclude that the plans, as
revised, continue to meet the
requirements of CAA sections 189(c)
and 189(b)(1)(A) for reasonable further
progress and expeditious attainment of
the PM–10 NAAQS.
2. Description of South Coast Control
Measure Commitments
The South Coast 2003 AQMP relies
heavily on existing, fully adopted
SCAQMD regulations to reduce primary
PM–10 and secondary precursors as
needed to bring the area into attainment
of the 24-hour and annual PM–10
NAAQS. The secondary precursors in
the South Coast are NOX and, to a lesser
extent, SOX, VOC, and ammonia (NH3).
The majority of these control measures
have been approved in prior actions on
SCAQMD regulations submitted over
the years.11
Although existing controls on primary
PM–10 and secondary PM–10
precursors achieve the overwhelming
majority of reductions necessary for
attainment, it is still necessary to adopt
new regulations or strengthen existing
regulations in order to deliver the small
additional amount of reductions needed
for attainment of the PM–10 NAAQS in
10 SCAQMD did, as part of the plan update,
review control measures to confirm that the
District’s measures and commitments continue to
reflect the best and most stringent control level. See
discussions of each control measure in Appendix
IV–A, which summarizes the results of the District’s
survey of available control technologies and
techniques, and provides extensive documentation
and references to support the proposed control.
11 See, for example, our approval of the 1997
ozone plan and that plan’s NOX and VOC control
measure commitments, as amended in 1999 (65 FR
6091, February 8, 2000; 65 FR 18903, April 10,
2000). We have approved the District’s NOX and
VOC regulations in separate rulemaking over the
years. You may see copies of the approved rules at:
https://www.epa.gov/region09/air/sips/.
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the South Coast. The SCAQMD’s
commitment to adopt new or
strengthened regulations in the 2003
South Coast AQMP is described at
length in Chapter 4 and in Appendix
IV–A (District’s Stationary and Mobile
Source Control Measures).
Table 1 below, entitled ‘‘South Coast
PM–10 Control Measures,’’ lists the
target primary PM–10, NH3, VOC, and
SOX emission reductions from each
including evolution of the measures
over time and progress on the measures
since the 2002 SIP. Appendix IV–A also
documents the costs of implementation,
discusses technological feasibility
issues, explains the schedule for
expeditious implementation, and
examines other factors as part of a
comprehensive rationale for the
measures.12
control measure commitment included
in the plan. Certain new SCAQMD
control measures in the South Coast
2003 AQMP are intended to reduce NOX
emissions, but the NOX emission
reductions from these measures by 2006
are relatively small and therefore the
new NOX measures and reductions are
not included in Table 1.
Appendix IV–A provides extensive
history of the control measures,
TABLE 1.—SOUTH COAST PM–10 CONTROL MEASURES
[Source: South Coast 2003 AQMP, Appendix IV–A]
Control measure
number
2006
reduction
target
in tons
per day
Control measure title
Remaining 2002 SIP Control Measures
CMB–07 ............
CMB–09 1 ..........
WST–01 1 ..........
WST–02 1 ..........
PRC–03 (P2) .....
Emission Reductions from Petroleum Refinery Flares (SOX) ................................................................................
Petroleum Refinery Fluid Catalytic Cracking Units (PM–10, NH3) ........................................................................
Emission Reductions from Livestock Waste (VOC, NH3) ......................................................................................
Emission Reductions from Composting (VOC, NH3) .............................................................................................
Emission Reductions from Restaurant Operations (PM–10) ..................................................................................
2.1
0.1, 0
4.2, 8.7
1.2, 1.9
0.2
New Control Measures
BCM–07 1 ..........
BCM–08 1 ..........
MSC–04 ............
MSC–06 ............
TCB–01 2 ...........
Further PM10 Reductions from Fugitive Dust Sources (PM–10) ...........................................................................
Further Emission Reductions from Aggregate and Cement Manufacturing Operations (PM–10) .........................
Miscellaneous Ammonia Sources (NH3) ................................................................................................................
Wood-Burning Fireplaces and Wood Stoves (PM–10) ...........................................................................................
Transportation Conformity Backstop Measure (PM–10) .........................................................................................
TBD
0.6
TBD
TBD
0
1 These measures have already been adopted by SCAQMD. Revisions to Rules 403 and 1186 fulfill BCM–07; new Rule 1127 (Emission Reductions from Livestock Waste, adopted 8/6/04) addresses WST–01; new Rule 1133.2 (Emission Reductions from Co-Composting Operations,
adopted 1/10/03) responds to WST–02 commitments; new Rule 1105.1 (Reduction of PM10 and Ammonia Emissions from Fluid Catalytic Cracking Units, adopted 11/7/03) meets the CMB–09 commitment; and new Rule 1157 (PM10 Emissions Reductions from Aggregate and Related Operations, adopted 1/07/05) fulfills the BCM-08 commitment.
2 This measure, which is intended to achieve reductions in PM–10 after the 2006 attainment date, is discussed below and in Section II.G.,
Motor Vehicle Emission Budgets.
Table 2 below, entitled ‘‘South Coast
Emission Reduction Commitments,’’
presents the enforceable SCAQMD
commitments to adopt and implement
measures by specific dates to achieve
particular emission reductions. This
table is derived from Table 4–8A in the
South Coast 2003 AQMP, and includes
the commitments for the remaining 3
years of the South Coast PM–10
attainment demonstration.
TABLE 2.—SOUTH COAST EMISSION REDUCTION COMMITMENTS COMMITMENTS TO ADOPT AND IMPLEMENT NEW
MEASURES TO ACHIEVE EMISSION REDUCTIONS IN TONS PER DAY FROM 2010 PLANNING INVENTORY
[Source: South Coast 2003 AQMP, Table 4–8A]
VOC
PM–10
NOX
SOX
Year
Adopt
2004 .................................
2005 .................................
2006 .................................
Impl
2.0
2.0
0
0
0
4.8
12 Although the 2003 South Coast AQMP includes
new and revised State control measures in
Appendix IV–B (Proposed 2003 State and Federal
Strategy for the California State Implementation
Plan) and new regional transportation strategies in
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Adopt
Impl
1.7
0
0
Adopt
0
0.16
0.86
Appendix IV–C (Regional Transportation Strategy &
Control Measures), these control measures are not
part of the revised PM–10 portion of the plan since
they are primarily designed to contribute emission
reductions needed for attainment of the 1-hour
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Impl
3.0
2.1
0
Adopt
0
0
0
Impl
2.1
0
0
0
2.1
0
ozone NAAQS by 2010. We intend to rule on these
measures when we act on the ozone portion of the
South Coast 2003 AQMP.
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The emission reduction targets shown
in Table 1 and the emission reduction
commitments shown in Table 2 are
intended to update and replace those in
the 2002 SIP, reflecting recent progress
in the development of the measures.13
The 2003 South Coast AQMP includes
one measure applicable to the post-2006
period. In order to ensure that growth in
transportation related emissions in
future years does not jeopardize
continued attainment of the PM–10
NAAQS, SCAQMD adopted TCB–01—
Transportation Conformity Budget
Backstop Measure. This measure
consists of a commitment to adopt
further PM–10 controls no later than
2019 to achieve as much as 9 tons per
day of additional PM–10 emission
reductions by 2020, and to adopt still
more PM–10 controls no later than 2029
to achieve as much as 16 tons per day
of additional PM–10 emission
reductions by 2030. Under the measure,
SCAQMD will be responsible for
implementing further fugitive dust rules
and SCAG will be responsible for
developing and achieving additional
emission reductions from the Regional
Transportation Plan and Transportation
Control Measures. Further details on
this committal measure may be found in
Appendix IV–A, pages IV–119 through
IV–121.
3. Proposed Action on South Coast
Control Measures
Inasmuch as the South Coast 2003
AQMP presents minor updates,
refinements, and enhancements of the
South Coast control measures in the
2002 SIP, we propose to approve them
under CAA section 110(k)(3), as meeting
the requirements of CAA sections
110(a), 188(e), and 189(b)(1)(B), and
remaining consistent with attainment as
expeditiously as practicable. We are
proposing to approve each of the control
measure commitments in Table 1 and
the overall SCAQMD commitment in
Table 2 to adopt and implement rules by
specified dates to achieve particular
emission reductions. We propose that
these updated commitments supersede
and replace the commitments for the
same measures in the 2002 SIP for the
South Coast.14
13 SCAQMD has now adopted regulations
fulfilling the following commitments in the 2002
SIP: BCM–01, BCM–03, BCM–04, BCM–06, BCM–
08, CMB–09, PRC–01, WST–01, and WST–02. It
should be noted that the NOX reductions from the
committal measures in the South Coast 2003
AQMP, as displayed in Table 2, are not relied on
for progress or attainment, but will contribute to
maintenance of the PM–10 NAAQS in the period
after 2006.
14 The previously approved commitments for
these measures are shown in Table 1 of our
proposed action on the 2002 SIP for PM–10 (67 FR
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As noted above, the 2003 Coachella
Valley Plan contains no new control
measure commitments, but relies on the
adopted revisions to Rules 403 and
403.1 and the local ordinances.
C. Regulations and Ordinances
The principal fugitive dust
regulations in the South Coast and
Coachella Valley are two SCAQMD
rules: Rule 403—‘‘Fugitive Dust’’ and
Rule 1186—‘‘PM10 Emissions from
Paved and Unpaved Roads and
Livestock Operations.’’ Attainment of
the PM–10 NAAQS in Coachella Valley
also depends on emission reductions
from SCAQMD Rule 403.1—
‘‘Supplemental Fugitive Dust Control
Requirements for Coachella Valley
Sources’’ and fugitive dust control
77216, December 17, 2002) and, for secondary
precursors to PM–10, in Table 2 of our proposed
action on the ozone SIP (65 FR 6096, February 8,
2000; final rule 65 FR 18903, April 10, 2000). It
should be noted that the 2003 South Coast AQMP
uses updated baseline and projected emissions
inventories and control factors, and so the emission
reductions targets in this new plan are calculated
using different currencies from the approved ozone
and PM–10 SIPs. Moreover, the 2003 South Coast
AQMP committal measures reflect in the baseline
and projected emissions inventories all reductions
that have already been accomplished by SCAQMD
regulations adopted subsequent to the submittal of
the earlier SIPs.
Commitments approved by EPA under CAA
section 110(k)(3) are enforceable by EPA and
citizens under CAA sections 113 and 304,
respectively. In the past, we have approved
enforceable commitments and courts have enforced
those actions against states that failed to comply
with their commitments. For further discussion and
citation, please see 69 FR 5427 (February 4, 2004)
and 69 FR 30029 (May 26, 2004).
We consider 3 factors in determining whether to
approve enforceable commitments: (a) Whether the
commitment addresses a limited portion of the
statutorily-required program; (b) whether the state
is capable of fulfilling its commitment; and (c)
whether the commitment is for a reasonable and
appropriate period of time. In the case of this
update to the 2002 SIP for the South Coast, the
number of commitments and the associated
emission reductions are considerably reduced,
because of continued successful SCAQMD rule
adoption, leaving relatively few reductions to be
accomplished in future, as shown in Table 2. The
commitments represent a small percent of the
required emission reductions from the 1997 base
year. For example, the NOX commitments are not
required for attainment but rather contribute toward
post-2006 maintenance of the PM–10 NAAQS, and
the VOC commitments are 1.0% of the VOC
emission reductions achieved from the 1997 base
year through the 2006 attainment year. The
SCAQMD has demonstrated its diligence in
fulfilling commitments generally and, in the case of
the commitments in this plan, the SCAQMD had
adopted in regulatory form 5 of the 10 commitments
by August 2004, including all the most significant
PM–10 measures. We believe that the schedule for
adopting and implementing the measures is for a
reasonable and appropriate period of time, given
the complex and challenging nature of the control
measures. Finally, the adoption and
implementation schedule in the commitments is
consistent with the SCAQMD’s ability to make
expeditious progress toward attainment of the
standards.
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ordinances adopted by Riverside County
and 9 cities within the Coachella Valley.
Attainment of the PM–10 NAAQS in the
South Coast also requires NH3 and VOC
reductions from livestock waste
operations, and SCAQMD adopted on
August 6, 2004, a new SCAQMD Rule
1127—‘‘Emission Reductions from
Livestock Waste’’ to accomplish these
reductions.15
In this action, we are proposing to
approve recently adopted amendments
strengthening Rules 403, 403.1, and
1186, and more stringent fugitive dust
control ordinances adopted by the 10
Coachella Valley jurisdictions. These
regulations and ordinances were
adopted in fulfillment of emission
reduction commitments in the 2002
SIPs for the South Coast and Coachella,
and in the 2003 South Coast AQMP.
The docket for this rulemaking
includes the complete SIP submittal
package, including the current rule text,
strike-out/underline rule text
highlighting rule amendments, and the
SCAQMD Staff Report, which provides
information on the regulatory
background, rule purpose and
applicability, affected sources, legal
authority, changes in the rules and
implementation handbooks, estimation
of emissions and emission reductions,
cost and cost-effectiveness estimates,
and summary of public comments and
SCAQMD response. The Staff Report
and supplementary materials on revised
Rules 403, 403.1, and 1186 may also be
found at: https://www.aqmd.gov/hb/
2004/040438a.html.
1. Description of Regulations and
Ordinances
a. SCAQMD Rule 403—Fugitive Dust
Rule 403 applies to any land use or
activity that has the potential to
generate fugitive dust, including
construction and agricultural activities.
SCAQMD originally adopted Rule 403
in 1976, and amended the rule in 1992,
1993, 1997, and 1998. On February 17,
2000 (65 FR 8057), we approved Rule
403, including its two handbooks (‘‘Rule
403 Implementation Handbook’’ and
‘‘Rule 403 Agricultural Handbook’’), as
the rule was last amended in 1998.
On April 2, 2004, the SCAQMD again
adopted strengthening and clarifying
amendments to the rule and handbooks,
and adopted an additional handbook—
‘‘Rule 403 Coachella Valley Agricultural
15 On July 21, 2004 (69 FR 43518), we approved
new SCAQMD Rules 1133, 1133.1, and 1133.2,
adopted on January 10, 2003, establishing VOC and
NH3 controls on composting operations. We intend
to act on Rule 1127 in separate rulemaking, once
the rule is submitted. These rules contribute
reductions required as part of the South Coast PM–
10 NAAQS attainment demonstration.
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Handbook.’’ The more significant
changes include: Lowering the
threshold for construction projects
subject to additional requirements for
large operations and strengthening those
notification and control requirements;
requiring construction sites greater than
5 acres to install track-out control
devices; identifying conservation
practices for Coachella Valley crop
producers seeking a Rule 403
exemption; tightening provisions
relating to weed abatement; and adding
numerous provisions to clarify the rule
and improve its enforceability.
CARB and SCAQMD requested that
we not approve into the SIP the revised
rule provision (h), relating to Ambient
Air Analysis Fees.16 In the same
correspondence, CARB and SCAQMD
asked that we approve only the
following sections of the revised 403
Implementation Handbook, which is
incorporated into the rule: (1) Chapter
5—Guidance for Large Operations; (2)
Chapter 7—Test Methods; and (3)
Chapter 8—On-Site Monitoring.
SCAQMD asked that we approve the
entire Rule 403 Coachella Valley
Agricultural Handbook, just as we have
previously approved the entire 403
Agricultural Handbook applicable to the
South Coast area (65 FR 8057).17
b. SCAQMD Rule 403.1—Supplemental
Fugitive Dust Control Requirements for
Coachella Valley
SCAQMD Rule 403.1 applies to any
land use or activity within the Coachella
Valley that has the potential to generate
fugitive dust, including construction
activities.18 The rule includes especially
stringent provisions for implementation
when wind speeds exceed 25 miles per
hour, and the rule also serves as a
backstop for local jurisdictions’
enforcement of their fugitive dust
ordinances. SCAQMD originally
adopted Rule 403.1 in 1993, and
amended the rule in 2000. On December
9, 1998 (63 FR 67784), we approved
Rule 403.1, including the ‘‘403.1
Implementation Handbook,’’ as
originally adopted in 1993.
On April 2, 2004, the SCAQMD
adopted strengthening and clarifying
amendments to the rule and ‘‘Rule 403.1
Implementation Handbook.’’ The more
significant changes include: more
16 Letter from Michael Scheible, CARB, to Wayne
Nastri, USEPA, dated November 16, 2004, and letter
from Elaine Chang, SCAQMD, to Dave Jesson,
USEPA, dated September 17, 2004.
17 Letter from Elaine Chang, SCAQMD, to Bob
Fletcher, ARB, dated August 18, 2004.
18 Rule 403.1 was originally titled ‘‘Wind
Entrainment of Fugitive Dust.’’ The amendment
adopted this year includes a change in the rule’s
title to ‘‘Supplemental Fugitive Dust Control
Requirements for Coachella Valley.’’
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stringent soil stabilization requirements
for inactive construction sites; addition
of a requirement that sources not subject
to a local dust control ordinance submit
a fugitive dust control plan to SCAQMD;
and numerous provisions clarifying the
rule and improving its enforceability.
CARB and SCAQMD requested that
we not approve into the SIP the revised
rule provision (j), relating to Fees.19
SCAQMD also asked that we approve
only the following sections of the
revised ‘‘Rule 403.1 Implementation
Handbook,’’ which is incorporated into
the rule: (1) Chapter 2—Coachella
Valley Wind Monitoring; (2) Chapter
3—On-Site Wind Monitoring
Equipment; (3) Chapter 4—Fugitive
Dust Control Plan Guidance; and (4)
Chapter 7—Test Methods.20
c. SCAQMD Rule 1186—PM10
Emissions From Paved and Unpaved
Roads, and Livestock Operations
SCAQMD Rule 1186 establishes
controls to reduce dust from traffic on
paved and unpaved roads, from hay
grinding activities, and from access
connections and feed lane at livestock
operations. The rule includes
requirements for purchase of PM10
efficient street sweepers; removal of
material on roadways; curbing;
treatment of medians; and paving,
stabilization, and/or speed restrictions
for unpaved roads. SCAQMD originally
adopted Rule 1186 in 1997, and
amended the rule in 1998, and 1999. On
February 17, 2000 (65 FR 8057), we
approved Rule 1186 as it was last
amended in 1998.
On April 2, 2004, the SCAQMD
adopted strengthening and clarifying
amendments to the rule. The more
significant changes include: extending
street cleaning requirements to
Coachella Valley and implementing
requirements for improved road
shoulders.
d. Coachella Valley Local Ordinances
On February 16, 1995, the State
submitted for SIP approval the
following fugitive dust ordinances
adopted by the following Coachella
Valley jurisdictions on the dates shown
in parentheses: City of Cathedral City
Ordinance No. 377 (2/18/93), City of
Coachella Ordinance No. 715 (10/6/93),
City of Desert Hot Springs Ordinance
No. 93–2 (5/18/93), City of Indian Wells
Ordinance No. 313 (2/4/93), City of
Indio Ordinance No. 1138 (3/17/93),
19 Letter from Michael Scheible, CARB, to Wayne
Nastri, USEPA, dated November 16, 2004, and letter
from Elaine Chang, SCAQMD, to Dave Jesson,
USEPA, dated September 17, 2004.
20 Letter from Elaine Chang, SCAQMD, to Bob
Fletcher, ARB, dated August 18, 2004.
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43669
City of La Quinta Ordinance No. 219
(12/15/92), City of Palm Desert
Ordinance No. 701 (1/14/93), City of
Palm Springs Ordinance No. 1439 (4/21/
93), City of Rancho Mirage Ordinance
No. 575 (8/5/93), and County of
Riverside Ordinance No. 742 (1/4/94).
On December 9, 1998 (63 FR 67784), we
approved all of these ordinances.
These ordinances were based on a
model fugitive dust control ordinance
developed by the Coachella Valley
Association of Governments (CVAG),
local governments, and the SCAQMD.
The ordinances typically require: (1)
Dust control plans for each construction
project needing a grading permit; (2)
plans to pave or chemically treat
unpaved surfaces if daily vehicle trips
exceed 150; (3) imposition of 15 mph
speed limits for unpaved surfaces if
daily vehicle trips do not exceed 150;
(4) paving or chemical treatment of
unpaved parking lots; and (5) actions to
discourage use of unimproved property
by off-highway vehicles.
Again working in cooperation with
CVAG and SCAQMD, all of the
jurisdictions recently developed a more
stringent model ordinance and then
adopted new replacement ordinances
based on the model. The revised
ordinances improve in numerous ways
the effectiveness of controls on
construction emissions and enhance the
jurisdictions’ various programs for
reducing reentrained dust emissions.
On November 16, 2004, CARB
submitted the following new and
improved ordinances as replacements
for the previously approved SIP
provisions: City of Cathedral City
Ordinance No. 583 (adopted 1/14/04),
City of Coachella Ordinance No. 896
(10/8/03), City of Desert Hot Springs
Ordinance No. 2003–16 (10/7/03), City
of Indian Wells Ordinance No. 545 (11/
6/03), City of Indio Ordinance No. 1357
(12/3/03), City of La Quinta Ordinance
No. 391 (12/2/03), City of Palm Desert
Ordinance No. 1056 (11/13/03), City of
Palm Springs Ordinance No. 1639 (11/
5/03), City of Rancho Mirage
Ordinances No. 855 (12/18/03) and No.
863 (4/29/04), and County of Riverside
Ordinance No. 742.1 (1/13/04).
2. Proposed Action on Regulations and
Ordinances
The revisions to Rules 403, 403.1, and
1186 and the Coachella Valley fugitive
dust ordinances strengthen the SIPapproved rules and ordinances. The
rules and ordinances continue to
contain adequate enforcement
provisions for ensuring compliance by
regulated facilities and the rules deliver
emission reductions consistent with the
South Coast and Coachella Valley
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progress and attainment requirements.
Prior versions of these rules and
ordinances were previously determined
to meet the BACM and MSM provisions,
and the rules and ordinances, as now
strengthened, continue to meet
applicable CAA subpart 2 provisions.
As noted above, the SCAQMD has
requested that we not approve certain
provisions of the rules and
accompanying handbooks. With these
exceptions, we are proposing to approve
SCAQMD Rules 403, 403.1, and 1186,
including the rule handbooks (Rule 403
Implementation Handbook, Rule 403
Coachella Valley Agricultural
Handbook, and Rule 403.1
Implementation Handbook), as amended
on April 2, 2004, and the Coachella
Valley fugitive dust ordinances under
CAA section 110(k)(3), as submitted on
November 16, 2004, as meeting the
provisions of CAA sections 110(a),
188(e), and 189(b)(1)(B).
Finally, we are proposing to conclude
that the 2003 South Coast AQMP and
the 2003 Coachella Valley Plan continue
to meet BACM and MSM control
measure requirements under CAA
sections 188(e) and 189(b)(1)(B),
through fully adopted regulations and
ordinances and (in the case of the South
Coast) a very limited number of nearterm commitments to adopt additional
measures.
D. Contingency Measures
The CAA requires that the SIP include
contingency measures to be
implemented if the area fails to meet
progress requirements or to attain the
NAAQS by the applicable deadline. In
response to this provision, the 2003
South Coast AQMP includes two
updated contingency measures: CTY–
01—Accelerated Implementation of
Control Measures, and CTY–14—
Emission Reductions from
Miscellaneous Sources (Weed
Abatement). These measures are
discussed at length in Appendix IV–A,
Section 2, pages IV–122 through IV–133.
CTY–01 includes Table 4 (page IV–126)
displaying the scheduled control
measures whose implementation could
be accelerated as part of the contingency
measure implementation. Both
measures have the potential to achieve
significant further reductions in PM–10
and its precursors and may be
implemented quickly to cure a SIP
shortfall. Upon final federal approval,
these contingency measures would
supersede and replace the contingency
measures in the 2002 SIP for the South
Coast.
In addition to these contingency
measures, the 2003 South Coast AQMP
projects a level of excess control for
years beyond 2006 for NOX and VOC,
two of the major secondary precursors
to PM–10 in the South Coast. This safety
margin is due to the future year benefits
of measures already adopted in
regulatory form by October 31, 2002, the
cutoff date for the inventories in
Appendix III, Attachment A. The extent
of this cushion, which is primarily the
result of fleet turnover to meet the
State’s stringent mobile source emission
standards, is shown below in Table 3—
‘‘Emissions of PM–10 Precursors in the
South Coast.’’
TABLE 3.—EMISSIONS OF PM–10 PRECURSORS IN THE SOUTH COAST
[Emissions are shown in average annual tons per day]
2006
Table A–7
Precursor
NOX ..................................................................................................................
VOC .................................................................................................................
2007
Table A–8
950
698
2008
Table A–9
912
672
2010
Table A–10
873
658
780
630
Source: 2003 South Coast AQMP, Appendix III, Attachment A.
Assuming that the 2006 levels are
consistent with attainment of the PM–10
NAAQS, the declining total basinwide
inventory of NOX and VOC show
additional reductions beyond those
needed to maintain the NAAQS. Thus,
for the year 2008, projected emissions of
NOX are 77 tpd below the attainment
level, and projected emissions of VOC
are 40 tpd below the attainment level.
We propose to approve the
SCAQMD’s contingency measure
provisions under CAA section 110(k)(3)
as meeting the requirements of CAA
section 172(c)(9). Specifically, we are
proposing to approve contingency
measures CTY–01—Accelerated
Implementation of Control Measures,
and CTY–04—Control of Emissions
from Miscellaneous Sources (Weed
Abatement), as set forth in Section 2 of
Appendix IV–A to the 2003 South Coast
AQMP.
There are no new contingency
measures in the 2003 Coachella Valley
Plan. Therefore, the contingency
provisions in the 2002 SIP for Coachella
Valley (see 67 FR 77209) remain
applicable.
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E. Reasonable Further Progress (RFP)
and Milestones
The plans must include quantitative
milestones which are to be achieved
every 3 years until the areas are
redesignated to attainment, and which
demonstrate RFP, as defined in CAA
section 171(1), until the area reaches
attainment. CAA sections 172(c)(2) and
189(c).
1. South Coast
Frm 00025
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[Emissions are shown in average annual tons
per day]
Pollutant
PM–10 ..............
NOX ..................
SOX ...................
VOC ..................
2003
292
1,048
58
804
2006
292
935
57
673
Source: 2003 South Coast AQMP, Table 6–
The 2003 South Coast AQMP includes
projected levels of controlled emissions,
based on fully adopted regulations and
enforceable schedules for
implementation of the control measure
commitments. The resulting emissions
levels are shown in Table 4—‘‘South
Coast PM–10 Reasonable Further
Progress Milestones.’’ Using the
approaches discussed in Section II.F.1
below, the SCAQMD modeled the
emissions levels for 2006 to demonstrate
that both the 24-hour and annual PM–
10 NAAQS will be attained when
emissions are reduced to the levels
shown for 2006.
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TABLE 4.—SOUTH COAST PM–10
REASONABLE FURTHER PROGRESS
MILESTONES
Sfmt 4702
1.
We propose to approve this milestone
schedule as meeting the requirements of
CAA section 189(c), since the schedule
reflects expeditious implementation of
BACM and expeditious attainment of
the 24-hour and annual PM–10 NAAQS.
These triennial progress milestones are
the principal progress component, but
the 2003 South Coast AQMP also
provides additional information
regarding interim year reductions. See,
for example, Table 2 above, Table A–6
of Appendix III, and the 2005 milestone
year reduction schedule for the 1-hour
ozone component of the plan (Table 6–
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3b). We therefore propose to conclude
that the 2003 South Coast AQMP also
meets the RFP provision of CAA section
172(c)(2).
2. Coachella Valley
The 2003 Coachella Valley Plan
includes projected levels of controlled
emissions, based on fully adopted
regulations and enforceable schedules
for implementation of the 2002 SIP’s
control measure commitment. The
resulting emissions levels are shown in
Table 5—‘‘Coachella Valley PM–10
Reasonable Further Progress
Milestones.’’ Using the approaches
discussed in Section II.F.2 below, the
SCAQMD modeled the emissions levels
for 2006 to demonstrate that both the
24-hour and annual PM–10 NAAQS will
be attained when emissions are reduced
to the levels shown for 2006.
TABLE 5.—COACHELLA VALLEY PM–
10
REASONABLE
FURTHER
PROGRESS MILESTONES
[PM–10 emissions are shown in average
annual tons per day]
2003
2006
30.32 .........................................
29.09
Source: 2003 Coachella Valley Plan, Tables
2–9 and 2–7.
We propose to approve this schedule
as meeting the RFP and milestone
requirements of CAA section 189(c)(1),
since the schedule reflects expeditious
implementation of BACM and
expeditious attainment of the 24-hour
and annual PM–10 NAAQS.
Specifically, we are proposing to
approve the milestone provisions in
Tables 2–9 and 2–7 of the 2003
Coachella Valley Plan. Because the
reductions needed for attainment
between the 2003 and 2006 milestones
are small (1.23 tons per day), we believe
that interim year reduction estimates are
not necessary or meaningful, and we
conclude that the plan meets the
requirements of CAA section 172(c)(2)
relating to RFP.
F. Attainment Demonstration
The plans must provide detailed
demonstrations (including air quality
modeling) that the specified control
strategy will reduce PM–10 emissions so
that the standards will be attained as
soon as practicable but no later than
December 31, 2006. CAA section
189(b)(1)(A). In the case of the South
Coast and Coachella Valley, the
attainment demonstration must analyze
both the 24-hour and annual NAAQS,
since the areas have historically violated
both NAAQS.
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1. South Coast
In the 2003 South Coast AQMP,
SCAQMD primarily relied on
UAMAERO–LT modeling approach to
assess control scenarios and to
determine attainment of the PM–10
NAAQS. The 2003 South Coast AQMP
also employed linear rollback of
speciated particulate at 5 representative
sites in the basin.21 Finally, a weight-ofevidence (WOE) assessment was used
for basin grids where high
concentrations were predicted. The
inputs and application of the models
and the WOE analyses are described in
Chapter 2 of Appendix V (Modeling and
Attainment Demonstrations) of the 2003
South Coast AQMP.
The modeling results for 1995, 2006,
and 2010 are presented in Chapter 5
(Figure 5–1 shows maximum annual
concentrations and Figure 5–2 shows
maximum 24-hour concentrations), and
on pages V–2–49 to V–2–58 of
Appendix V. The modeling predicts that
the peak annual concentration in 2006
with implementation of controls will be
50 µg/m3, compared to the 50 µg/m3
annual PM–10 NAAQS. The modeling
predicts that the peak 24-hour
concentration in 2006 with controls will
be 150 µg/m3, compared to the 150 µg/
m3 24-hour PM–10 NAAQS.
In contrast to other pollutants, we
have not issued detailed modeling
guidelines for PM–10, nor have we
established minimum performance
requirements for PM–10 modeling.22 We
have reviewed the SCAQMD’s modeling
approaches for both primary PM–10 and
secondary PM–10, using both receptor
modeling and dispersion modeling. We
believe that the modeling in the 2003
South Coast AQMP provides a
reasonable basis for linking emissions
with air quality, for identifying an
appropriate control strategy, and for
determining whether the strategy
21 Under the District’s PM10 Technical
Enhancement Program (PTEP), SCAQMD has been
measuring speciated particulate matter at the
following sites: Anaheim, Diamond Bar, Fontana,
Los Angeles, and Rubidoux. Information about the
PTEP program may be found in Appendix V to the
1997 South Coast AQMP and 2003 South Coast
AQMP.
22 Over the years, EPA has issued some
recommendations on PM–10 modeling, including
those codified at 40 CFR part 51, appendix W, 7.2.1
and 7.2.2, and those set forth in the PM–10 SIP
Development Guideline (USEPA 450/2–860001, 6/
87). Although we do not set minimum performance
goals or require model performance evaluation for
PM–10 modeling, SCAQMD included a
performance evaluation for the UAMAERO–LT by
grid cell and monitoring site and also a performance
evaluation at each of the 5 PTEP sites for sulfate,
nitrate, ammonium, organic carbon, elemental
carbon, and primary PM–10 (Appendix V, pages V–
2–31 to V–2–47).
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43671
delivers attainment for both the 24-hour
and annual PM–10 NAAQS.
The SCAQMD’s modeling shows that
the level of emissions after
implementation of the proposed set of
control strategies would result in 2006
ambient concentrations within the
South Coast in attainment of both the
24-hour and annual PM–10 NAAQS. We
therefore conclude that the air quality
modeling and attainment demonstration
contained in the 2003 South Coast
AQMP, Chapter 5 and Appendix V,
Chapter 2, are consistent with existing
EPA guidance, and we propose to
approve the attainment demonstration
under CAA section 189(b)(1)(A).
2. Coachella Valley
In the 2003 Coachella Valley Plan as
with the 2003 South Coast AQMP,
SCAQMD primarily relied on
UAMAERO–LT modeling approach to
assess control scenarios and to
determine attainment of the annual PM–
10 NAAQS. The 2003 Coachella Valley
Plan also employed linear rollback of
each of the significant primary source
categories as part of the demonstration
of attainment of the 24-hour PM–10
NAAQS. The attainment demonstration
is presented in Chapter 3. The predicted
peak concentration is 49.6 µg/m3 for the
annual NAAQS and 141.6 µg/m3 for the
24-hour NAAQS.23
The modeling thus shows that the
level of emissions after implementation
of the proposed set of control strategies
would result in 2006 ambient
concentrations within the Coachella
Valley in attainment of both the 24-hour
and annual PM–10 NAAQS. We
therefore conclude that the air quality
modeling and attainment demonstration
contained in the 2003 Coachella Valley
Plan, Chapter 3, are consistent with
existing EPA guidance, and we propose
to approve the attainment
demonstration under CAA section
189(b)(1)(A).
G. Motor Vehicle Emission Budgets
Rate of progress and attainment
demonstration submittals must specify
the maximum emissions of
transportation-related precursors of PM–
10 allowed in each milestone year and
the attainment year and demonstrate
that these emissions levels, when
considered with emissions from all
other sources, are consistent with RFP
and attainment. In order for us to find
these emissions levels or ‘‘budgets’’
23 The SCAQMD excercised its option to increase
the estimated 2006 paved road dust emissions in
the attainment demonstration to provide a safety
margin in the motor vehicle emissions budget,
resulting in predicted maximum concentrations of
50.4 µg/m3 and 144.3 µg/m3 (Table 3–3).
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adequate and approvable, the submittal
must meet the conformity adequacy
provisions of 40 CFR 93.118(e)(4) and be
approvable under all pertinent SIP
requirements.
The budgets defined by this and other
plans when they are approved into the
SIP or, in some cases, when the budgets
are found to be adequate, are then used
to determine the conformity of
transportation plans, programs, and
projects to the SIP, as described by CAA
section 176(c)(3)(A). For more detail on
this part of the conformity requirements,
see 40 CFR 93.118. For transportation
conformity purposes, the cap on
emissions of transportation-related PM–
10 precursors is known as the motor
vehicle emissions budget. The budget
must reflect all of the motor vehicle
control measures contained in the
attainment demonstration (40 CFR
93.118(e)(4)(v)), and must include PM–
10 and PM–10 precursor emissions from
the following sources: Motor vehicles,
reentrained dust from traffic on paved
and unpaved roads, and emissions
during construction of highway and rail
projects.24
The motor vehicle emissions budgets
for the South Coast are presented in
Table 6 below, entitled ‘‘South Coast
PM–10 Plan Motor Vehicle Emissions
Budgets,’’ which is taken from ‘‘2003
South Coast AQMP On-Road Motor
Vehicle Emissions Budgets,’’ an
attachment to CARB’s SIP submittal.
The motor vehicle emissions budgets for
the Coachella Valley are presented in
Table 7 below, entitled ‘‘Coachella
Valley PM–10 Plan Motor Vehicle
Emissions Budgets,’’ which is taken
from ‘‘2003 Coachella Valley PM–10 SIP
24 The conformity regulations provide that, for
purposes of budgets and conformity determinations,
the applicable pollutants are bOC, NOx, and PM–
10 if the applicable implementation plan
establishes a budget for such emissions as part of
the RFP, attainment, or maintenance strategy, or
EPA has made such a finding. 40 CFR
91.102(b)(2)(111). Thus, although the SCAMQD has
set RFP and attainment reductions for SOx, the
conformity regulations do not allow for SOx
budgets. The conformity regulations require that, in
PM–10 areas with SIPs which identify constructionrelated fugitive PM—10 as a contributor to the
nonattainment problem, the PM–10 budget and
conformity analysis must include fugitive, PM–10
emissions associated with the construction of
highway and transit projects. 40 CFR 93.122(d)(2)
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On-Road Motor Vehicle Emissions
Budgets,’’ an attachment to CARB’s SIP
submittal.
EPA has previously determined that
these budgets are adequate (see 69 FR
15325, March 25, 2004), following
posting of the budgets on EPA’s
conformity Web site: https://
www.epa.gov/otaq/transp/conform/
reg9sips.htm.
We propose to approve the motor
vehicle emission budgets shown in
Tables 6 and 7 as consistent with CAA
section 176(c)(2)(A) and the adequacy
criteria of 40 CFR 93.118(e)(4),
including consistency with the baseline
emissions inventories, the motor vehicle
control measure emission reductions
used in the progress and attainment
demonstration, and the reductions
needed for continued attainment of the
standard after the attainment deadline.
TABLE 6.—SOUTH COAST PM–10
PLAN MOTOR VEHICLE EMISSIONS III. Summary of EPA’s Proposed Action
BUDGETS
We are proposing to approve revisions
[Emissions are shown in annual average tons
per day]
to SCAQMD Rules 403 (except for
subdivision h), 403.1 (except for
subdivision j), and 1186 regulating
Year
PM–10
NOX
VOC
fugitive dust emissions; revisions to the
2003 ............
168
635
311 implementation handbooks for the rules
2006 ............
166
549
251 (Rule 403 Implementation Handbook,
Chapters 5, 7, and 8; Rule 403 Coachella
Valley Agricultural Handbook; Rule
TABLE 7.—COACHELLA VALLEY PM– 403.1 Implementation Handbook,
10 PLAN MOTOR VEHICLE EMIS- Chapters 2, 3, 4, and 7); and revisions
SIONS BUDGETS
to the fugitive dust ordinances for 10
[Emissions are shown in annual average tons Coachella Valley jurisdictions. These
per day]
revisions update, improve, strengthen,
and supplement the SIP provisions for
Year
PM–10
control of PM–10 and PM–10 precursors
in the two areas.
2003 ..........................................
12.3
We are proposing to approve 2003
2006 ..........................................
10.9
plan amendments to the 2002 SIPs for
the South Coast and Coachella Valley
The 2003 Coachella Valley Plan
serious nonattainment areas, as the plan
provides additional information on the
amendments pertain to CAA provisions
budgets in Chapter 2 (pages 2–9 through applicable to attainment SIPs for the 242–12) and Chapter 3 (pages 3–3 through hour and annual PM–10 NAAQS.
3–4), where the safety margin in the
Specifically, we are proposing to
2006 budgets is explained. In Section
approve under section 110(k)(3) the
II.B.2., we propose to approve committal PM–10 portions of the 2003 South Coast
measure TCB–01—Transportation
AQMP and the 2003 Coachella Valley
Conformity Budget Backstop Measure,
Plan with respect to the CAA
which is designed to ensure that motor
requirements for emissions inventories
vehicle emissions remain consistent
under section 172(c)(3); control
with the South Coast PM–10 budget and measures, as meeting the requirements
continued attainment of the PM–10
of sections 110(a), 188(e), and
NAAQS in the South Coast through the
189(b)(1)(B); RFP under section
years 2020 and 2030.
189(c)(1); contingency measures under
As discussed above in Section II.A.,
section 172(c)(9); demonstration of
Emission Inventories, the motor vehicle attainment under section 189(b)(1)(A);
emissions portions of these budgets (i.e., and motor vehicle emissions budgets
the evaporative and tailpipe emissions)
under section 176(c)(2)(A).
were developed using the EMFAC2002
We show the proposed plan approvals
motor vehicle emissions factors, along
in Table 8—‘‘Proposed Approvals of
with activity levels reflecting current
South Coast and Coachella Valley PM–
information provided by SCAG.
10 Attainment Plan Submittals.’’
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43673
TABLE 8.—PROPOSED APPROVALS OF SOUTH COAST AND COACHELLA VALLEY PM–10 ATTAINMENT PLAN SUBMITTALS
Plan citation
CAA section
Provision
South Coast
172(c)(3) ........................................
Emission Inventories ....................
110(a), 188(e), and 189(b)(1)(B) ...
Control Measures .........................
172(c)(2), 189(c)(1) ........................
Reasonable Further Progress ......
172(c)(9) ........................................
Contingency Measures .................
189(b)(1)(A) ...................................
Attainment Demonstration ............
176(c)(2)(A) ....................................
Motor Vehicle Emissions Budgets
IV. Administrative Requirements
Under Executive Order 12866 (58 FR
51735, October 4, 1993), this proposed
action is not a ‘‘significant regulatory
action’’ and therefore is not subject to
review by the Office of Management and
Budget. For this reason, this action is
also not subject to Executive Order
13211, ‘‘Actions Concerning Regulations
That Significantly Affect Energy Supply,
Distribution, or Use’’ (66 FR 28355, May
22, 2001). This proposed action merely
proposes to approve state law as
meeting Federal requirements and
imposes no additional requirements
beyond those imposed by state law.
Accordingly, the Administrator certifies
that this proposed rule will not have a
significant economic impact on a
substantial number of small entities
under the Regulatory Flexibility Act (5
U.S.C. 601 et seq.). Because this rule
proposes to approve pre-existing
requirements under state law and does
not impose any additional enforceable
duty beyond that required by state law,
it does not contain any unfunded
mandate or significantly or uniquely
affect small governments, as described
in the Unfunded Mandates Reform Act
of 1995 (Pub. L. 104–4).
This proposed rule also does not have
tribal implications because it will not
have a substantial direct effect on one or
more Indian tribes, on the relationship
between the Federal Government and
Indian tribes, or on the distribution of
power and responsibilities between the
Federal Government and Indian tribes,
as specified by Executive Order 13175
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14:21 Jul 27, 2005
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Coachella Valley
2003 South Coast AQMP, Chapter 3 (Tables 3–1A and 3–3A);
Appendix III (Tables A–1, A–2,
A–3, A–5, and A–7); and Appendix V (Attachment 4).
Table 1 (derived from 2003 South
Coast AQMP, Appendix IV–A)
and Table 2 (derived from 2003
South Coast AQMP, Table 4–
8A).
2003 South Coast AQMP, Table
6–1.
2003 Coachella Valley Plan, Tables 2–2, 2–3, 2–4, and 2–5.
2003 South Coast AQMP, Appendix IV–A, Section 2 (CTY–01,
CTY–04, TCB–01).
2003 South Coast AQMP, Chapter 5; Appendix V, Chapter 2.
Table 6 (derived from ‘‘2003
South Coast AQMP On-Road
Motor Vehicle Emissions Budgets’’).
(65 FR 67249, November 9, 2000). 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
proposes to approve a state rule
implementing a Federal standard, and
does not alter the relationship or the
distribution of power and
responsibilities established in the Clean
Air Act. This proposed rule also is not
subject to Executive Order 13045
‘‘Protection of Children from
Environmental Health Risks and Safety
Risks’’ (62 FR 19885, April 23, 1997),
because it is not economically
significant.
In reviewing SIP submissions, EPA’s
role is to approve state choices,
provided that they meet the criteria of
the Clean Air Act. In this context, in the
absence of a prior existing requirement
for the State to use voluntary consensus
standards (VCS), EPA has no authority
to disapprove a SIP submission for
failure to use VCS. It would thus be
inconsistent with applicable law for
EPA, when it reviews a SIP submission,
to use VCS in place of a SIP submission
that otherwise satisfies the provisions of
the Clean Air Act. Thus, the
requirements of section 12(d) of the
National Technology Transfer and
Advancement Act of 1995 (15 U.S.C.
272 note) do not apply. This proposed
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Sfmt 4702
No new measures.
Table 5 (derived from 2003
Coachella Valley Plan, Tables
2–9 and 2–7).
No new measures.
2003 Coachella Valley Plan,
Chapter 3.
Table 7 (derived from ‘‘2003
Coachella Valley PM–10 SIP
On-Road Motor Vehicle Emissions Budgets’’).
rule does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act of 1995
(44 U.S.C. 3501 et seq.).
List of Subjects in 40 CFR Part 52
Environmental protection, Air
pollution control, Intergovernmental
relations, Nitrogen dioxide, Particulate
matter, Reporting and recordkeeping
requirements, Volatile organic
compounds.
Dated: July 17, 2005.
Wayne Nastri,
Regional Administrator, Region IX.
[FR Doc. 05–14931 Filed 7–27–05; 8:45 am]
BILLING CODE 6560–50–P
DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric
Administration
50 CFR Part 600
[Docket No. 050520139–5139–01; I.D.
030305A]
RIN 0648–AS46
Magnuson-Stevens Act Provisions;
Fishing Capacity Reduction Program;
Bering Sea/Aleutian Islands King and
Tanner Crabs; Industry Fee System for
Fishing Capacity Reduction Loan
National Marine Fisheries
Service (NMFS), National Oceanic and
Atmospheric Administration (NOAA),
Commerce.
AGENCY:
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Agencies
[Federal Register Volume 70, Number 144 (Thursday, July 28, 2005)]
[Proposed Rules]
[Pages 43663-43673]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 05-14931]
=======================================================================
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 52
[CA-314-0483; FRL-7945-4]
Approval and Promulgation of State Implementation Plans for Air
Quality Planning Purposes; California--South Coast and Coachella
AGENCY: Environmental Protection Agency (EPA).
ACTION: Proposed rule.
-----------------------------------------------------------------------
SUMMARY: EPA is proposing to approve state implementation plan (SIP)
revisions submitted by the State of California to provide for
attainment of the particulate matter (PM-10) national ambient air
quality standards (NAAQS) in the Los Angeles-South Coast Air Basin and
the Coachella Valley Area, and to establish emissions budgets for these
areas for purposes of transportation conformity. EPA is also proposing
to approve revisions to fugitive dust regulations and ordinances for
the areas. EPA is proposing to approve these SIP revisions under
provisions of the Clean Air Act (CAA) regarding EPA action on SIP
submittals, SIPs for national primary and secondary ambient air quality
standards, and plan requirements for nonattainment areas.
DATES: Written comments on this proposal must be received by August 29,
2005.
ADDRESSES: Please mail comments to: Dave Jesson (AIR-2), EPA Region IX,
75 Hawthorne Street, San Francisco, CA 94105-3901, or e-mail to
jesson.david@epa.gov. The rulemaking docket for this proposal is
available for public inspection during normal business hours at EPA's
Region IX office. A reasonable fee may be charged for copying parts of
the docket.
Copies of the SIP materials are also available for inspection at
the following locations:
California Air Resources Board, 1001 I Street, Sacramento, California
95812.
South Coast Air Quality Management District, 21865 E. Copley Drive,
Diamond Bar, California 91765.
The 2003 Air Quality Management Plan, which includes the South
Coast PM10 plan, is electronically available at:
[[Page 43664]]
https://www.aqmd.gov/aqmp/AQMD03AQMP.htm.
The 2003 Coachella Valley PM10 State Implementation Plan is at:
https://www.aqmd.gov/aqmp/docs/f2003cvsip.pdf.
The fugitive dust rules are electronically available at: https://
www.aqmd.gov/rules/rulesreg.html.
FOR FURTHER INFORMATION CONTACT: Dave Jesson, EPA Region IX, at (415)
972-3957, or jesson.david@epa.gov.
SUPPLEMENTARY INFORMATION: Throughout this document, ``we,'' ``us,''
and ``our'' refer to EPA.
Table of Contents
I. Background
A. Summary
B. PM-10 Problem in the South Coast and Coachella Valley
C. CAA Planning Provisions
D. Designation and Classification
E. Adoption and Submittal of these Revisions
II. Evaluation of the SIP Submittals
A. Emission Inventories
B. Control Measures
1. Applicable Requirements
2. Description of South Coast Control Measure Commitments
3. Proposed Action on South Coast Control Measures
C. Regulations and Ordinances
1. Description of Regulations and Ordinances
a. SCAQMD Rule 403--Fugitive Dust
b. SCAQMD Rule 403.1--Supplemental Fugitive Dust Control
Requirements for Coachella Valley
c. SCAQMD Rule 1186--PM10 Emissions from Paved and Unpaved
Roads, and Livestock Operations
d. Coachella Valley Local Ordinances
2. Proposed Action on Regulations and Ordinances
D. Contingency Measures
E. Reasonable Further Progress (RFP) and Milestones
1. South Coast
2. Coachella Valley
F. Attainment Demonstrations
1. South Coast
2. Coachella Valley
G. Motor Vehicle Emission Budgets
1. South Coast
2. Coachella Valley
III. Summary of EPA's Proposed Action
IV. Administrative Requirements
I. Background
A. Summary
We are proposing to approve 2003 plan amendments for the South
Coast Air Basin (or ``South Coast''), as the plan amendments pertain to
attainment of the 24-hour and annual PM-10 NAAQS.\1\ We are proposing
to approve revisions to the PM-10 plan for the Coachella Valley
Planning Area (``Coachella Valley'').\2\ We are also proposing to
approve the plans' PM-10 motor vehicle emissions budgets for purposes
of transportation conformity. Finally, we are proposing to approve
revisions to Rules 403, 403.1, and 1186 of the South Coast Air Quality
Management District (SCAQMD) regulating fugitive dust emissions, and
revisions to fugitive dust ordinances for Coachella Valley
jurisdictions. These revisions update, improve, strengthen, and
supplement the approved SIP provisions for control of PM-10 and PM-10
precursors in the two areas.
---------------------------------------------------------------------------
\1\ The nonattainment area includes all of Orange County and the
more populated portions of Los Angeles, San Bernardino, and
Riverside Counties. For a description of the boundaries of the Los
Angeles-South Coast Air Basin Area, see 40 CFR 81.305.
\2\ The Coachella Valley Planning Area is in central Riverside
County in the Salton Sea Basin. The boundary is defined at 40 CFR
81.305.
---------------------------------------------------------------------------
B. PM-10 Problem in the South Coast and Coachella Valley
Although great progress has been made in reducing PM-10
concentrations, the South Coast and Coachella Valley continue to
violate the PM-10 NAAQS, and the State must therefore adopt, submit,
and implement measures and other provisions sufficient to make
expeditious progress and attain the NAAQS by the applicable
deadline.\3\
---------------------------------------------------------------------------
\3\ The health effects from elevated PM-10 concentrations
include lung damage, respiratory and cardio-vascular disease, and
premature death. Children, the elderly, and people suffering from
heart and lung diseases, such as asthma, are especially at risk.
EPA revised the NAAQS for particulate matter on July 1, 1987 (52
FR 24672), replacing standards for total suspended particulates with
new standards applying only to particulate matter up to 10 microns
in diameter (PM-10). At that time, EPA established two PM-10
standards. The annual PM-10 standard is attained when the expected
annual arithmetic mean of the 24-hour samples averaged over a 3-year
period does not exceed 50 micrograms per cubic meter ([mu]g/m\3\).
The 24-hour PM-10 standard of 150 [mu]g/m\3\ is attained if samples
taken for 24-hour periods have no more than one expected exceedance
per year, averaged over 3 years. See 40 CFR 50.6 and 40 CFR part 50,
appendix K.
On July 18, 1997, EPA reaffirmed the annual PM-10 standard, and
slightly revised the 24-hour PM-10 standard (652 FR 38651). In the
same action, EPA also established two new standards for PM, both
applying only to particulate matter up to 2.5 microns in diameter
(PM-2.5).
This SIP submittal addresses the 24-hour and annual PM-10
standards as originally promulgated. An opinion issued by the U.S.
Court of Appeals for the D.C. Circuit in American Trucking Assoc.,
Inc., et al. v. USEPA, No. 97-1440 (May 14, 1999), among other
things, vacated the 1997 standards for PM-10. However, the PM-10
standards promulgated on July 1, 1987 were not an issue in this
litigation, and the Court's decision does not affect the
applicability of those standards in the South Coast and Coachella
Valley areas. Codification of those standards continues to be
recorded at 40 CFR 50.6. See also 69 FR 45592, July 30, 2004.
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The SCAQMD has adopted and the State has submitted PM-10 attainment
plans and regulations for these two areas in past years. In 2003, we
fully approved PM-10 progress and attainment plans for the South Coast
and Coachella Valley as meeting all CAA requirements for serious PM-10
areas, and as part of those actions we also granted attainment date
extensions for the areas for both the 24-hour and annual PM-10 NAAQS,
from December 31, 2001 to December 31, 2006, pursuant to CAA section
188(e). For more information on the currently approved South Coast and
Coachella Valley PM-10 plans (``2002 SIPs''), please see our proposed
and final rulemaking notices. The proposals were issued on December 17,
2002 (67 FR 77212 and 67 FR 77204) and the final approvals were issued
on April 18, 2003 (68 FR 19316 and 68 FR 19318). We have also
previously approved SCAQMD fugitive dust regulations and Coachella
Valley local ordinances for the control of fugitive dust. See approvals
of SCAQMD Rules 403, 403.1, and 1186, and 10 Coachella Valley
ordinances published on December 9, 1998 (63 FR 67784), and again on
February 17, 2000 (65 FR 8057), following SCAQMD adoption of amendments
strengthening Rules 403 and 1186. This proposed action simply addresses
updates and improvements to the 2002 SIPs for the South Coast and
Coachella Valley, the SCAQMD fugitive dust regulations, and the
Coachella Valley ordinances, adopted as part of the attainment plans
for the South Coast and Coachella Valley.
C. CAA Planning Provisions
The Federal CAA was substantially amended in 1990 to establish new
planning requirements and attainment deadlines for the NAAQS. The most
fundamental of these nonattainment area provisions applicable to the
South Coast and Coachella Valley is the requirement that the State
submit a SIP demonstrating attainment of the PM-10 NAAQS. This
demonstration must be based upon enforceable measures to achieve
emission reductions leading to emissions at or below the level
predicted to result in attainment of the NAAQS throughout the
nonattainment area. The measures must meet the standard for Best
Available Control Measures (BACM), and the measures must be implemented
expeditiously and ensure attainment no later than the applicable CAA
deadline. CAA section 189(b). Because the State requested an extension
of the attainment date for the South Coast and Coachella Valley beyond
the applicable deadline of December 31, 2001, under CAA section 188(e)
the State must demonstrate that
[[Page 43665]]
the plans include the most stringent measures (MSM) that are included
in any implementation plan or are achieved in practice, and can
feasibly be implemented in the area.
EPA has issued a ``General Preamble'' describing the Agency's
preliminary views on how EPA intends to act on SIPs submitted under
Title I of the Act. See 57 FR 13498 (April 16, 1992), 57 FR 18070
(April 28, 1992). EPA later issued an Addendum to the General Preamble
providing guidance on SIP requirements for serious PM-10 areas. 59 FR
41998 (August 16, 1994). The reader should refer to these documents for
a more detailed discussion of EPA's preliminary interpretations of
Title I requirements. In this proposed rulemaking action, EPA applies
these policies to the South Coast and Coachella Valley PM-10 SIP
submittals, taking into consideration the specific factual issues
presented.
D. Designation and Classification
On the date of enactment of the 1990 CAA Amendments, PM-10 areas,
including the South Coast and Coachella Valley, meeting the
qualifications of section 107(d)(4)(B) of the amended Act, were
designated nonattainment by operation of law. See 56 FR 11101 (March
15, 1991).
Once an area is designated nonattainment, section 188 of the CAA
outlines the process for classification of the area and establishes the
area's attainment date. In accordance with section 188(a), at the time
of designation, all PM-10 nonattainment areas, including the South
Coast and Coachella Valley, were initially classified as moderate by
operation of law. Section 188(b)(1) of the Act further provides that
moderate areas can subsequently be reclassified as serious before the
applicable moderate area attainment date if at any time EPA determines
that the area cannot ``practicably'' attain the PM-10 NAAQS by this
attainment date.
EPA determined on January 8, 1993, that the South Coast and
Coachella Valley could not practicably attain the PM-10 NAAQS by the
applicable attainment deadline for moderate areas (December 31, 1994,
per section 188(c)(1) of the Act), and reclassified the area as serious
(58 FR 3334). In accordance with section 189(b)(2) of the Act, the
State was required to make the following SIP submittals. First, the
State had to submit by August 8, 1994, a SIP to ensure the
implementation of BACM no later than 4 years after reclassification, as
required by CAA section 189(b)(1)(B). Second, the State had to submit a
SIP by February 8, 1997, providing for progress and expeditious
attainment, as required by CAA section 189(b)(1)(A).
E. Adoption and Submittal of These Revisions
For a description of the history and content of the 2002 SIPs,
rules, and ordinances for the South Coast and Coachella Valley, please
see our proposed and final rules cited above. On August 1, 2003, the
SCAQMD adopted the 2003 South Coast Air Quality Management Plan (``2003
South Coast AQMP'') and the 2003 Coachella Valley PM10 State
Implementation Plan (``2003 Coachella Valley Plan''), including the
motor vehicle emissions budgets for the areas.\4\ The California Air
Resources Board (CARB) approved the plans on October 23, 2003, and
submitted the plans to us on January 9, 2004. We determined that these
submittals were complete on February 18, 2004, pursuant to CAA section
110(k)(1)(B) and 40 CFR part 51, Appendix V.
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\4\ In addition to PM-10, the 2003 South Coast AQMP addressed
the NAAQS for carbon monoxide (CO), ozone, and nitrogen dioxide
(NO2). We will take separate action on the plan with
respect to these standards.
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On April 2, 2004, the SCAQMD adopted revisions to Rules 403, 403.1,
and 1186, and CARB submitted the revisions on July 29, 2004. On August
10, 2004, we determined the submittal to be complete. On November 16,
2004, CARB submitted revised Coachella Valley ordinances, which were
adopted by the local jurisdictions on various dates in 2003 and 2004,
and the implementation handbooks for Rules 403 and 403.1, which were
inadvertently omitted from the April 2, 2004 SIP submittal. On April 6,
2005, we determined the submittal to be complete.
Both the SCAQMD and CARB satisfied applicable statutory and
regulatory requirements for reasonable public notice and hearing prior
to adoption of the SIP revisions. The SCAQMD conducted numerous public
workshops, and properly noticed the public hearings at which the plans
and rules were adopted. The SIP submittals include proof of publication
for notices of the public hearings. The local Coachella Valley
jurisdictions properly noticed and adopted the fugitive dust
ordinances. Therefore, we conclude that the SIP submittals have met the
public notice and involvement requirements of section 110(a)(1) of the
CAA.
II. Evaluation of the SIP Submittals
A. Emission Inventories
CAA section 172(c)(3) requires that all nonattainment area plan
submittals include a comprehensive, accurate, and current inventory of
actual emissions from all sources in the area.
The emission inventories in the 2003 South Coast AQMP and the 2003
Coachella Valley Plan supersede those in the 2002 SIPs for these areas.
The revised 2003 South Coast AQMP includes summary emission inventories
for major source categories in tons per annual average day for VOC,
NOX, CO, SOX, TSP, PM-10, and PM-2.5 for the 1997
base year (Table 3-1A) and the 2006 attainment year (Table 3-3A).
Appendix III (Base and Future Year Emission Inventories) to the 2003
South Coast AQMP provides more detailed emissions inventories for 1995,
1997, 2000, 2002, 2003, 2005, 2006, and various later years. Appendix
IV-A also includes additional emissions data, including control
category baseline emissions for 1997, 2006, and 2010, and estimates of
baseline emissions and emission reductions from each of the 2003 South
Coast AQMP control measures for 2006 and 2010 for primary PM-10 or PM-
10 precursors (NOX, SOX, VOC, and ammonia), as
applicable to the measure. Appendix III documents the source of the
data and references SCAQMD and CARB reports that provide detailed
information on the methodologies used to estimate emissions from area
sources. Finally, Appendix V (Modeling and Attainment Demonstrations)
includes estimated average annual day emission reductions by control
measure for PM-10, VOC, NOX, and SOX in 2006 in
the South Coast.
The 2003 Coachella Valley Plan includes annual average and maximum
24-hour emission inventories for 1995 (Table 2-2), 2000 (Table 2-3),
2003 (Table 2-4), and 2006 (Table 2-5).
The principal emissions inventory enhancements of the revised plans
are the use of more accurate emissions factors and models and updated
activity levels for emissions associated with mobile sources,
including: (1) The use of the latest EPA-approved California motor
vehicle emissions factor model (EMFAC2002) \5\ and the most recent
motor vehicle activity data from the Southern California Association of
Governments (SCAG); (2) an improved methodology for estimating paved
road
[[Page 43666]]
dust emissions \6\; and (3) CARB's new nonroad mobile source model (the
OFFROAD model). The emission inventories for the South Coast Air Basin
also use the results of special studies of aircraft, marine vessels,
composting, and ammonia emissions (see Appendix III of the 2003 South
Coast AQMP, pages III-1-13 to III-1-14), and more accurate emissions
factors for the windblown dust category, based on use of climate, wind
speed, and soil data representative of Southern California.
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\5\ We approved use of EMFAC2002 on April 1, 2003 (68 FR 15722)
for use in SIPs and conformity analyses. EMFAC2002 produces
California-specific emissions for the full range of motor vehicles.
\6\ We recently approved this methodology as part of our
adequacy determination for the motor vehicle emissions budgets in
the revised South Coast and Coachella Valley PM-10 plans. See 58 FR
15326, March 25, 2004. The methodologies are discussed on page III-
1-12 of Appendix III of the 2003 South Coast AQMP.
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The emission inventories in the 2003 South Coast AQMP and 2003
Coachella Valley Plan are complete with respect to sources that have
been found to contribute to PM-10 violations. The inventories employ
activity levels, emission factors, and growth projections that are
current and reflective of the best available emissions information.
Because they are current, accurate, and complete, we propose to
approve as meeting the provisions of CAA section 172(c)(3) the South
Coast emission inventories in Chapter 3 (Tables 3-1A and 3-3A),
Appendix III (Tables A-1, A-2, A-3, A-5, and A-7), and Appendix V of
the 2003 South Coast AQMP (Attachment 4), and the Coachella Valley
emission inventories in Tables 2-2, 2-3, 2-4, and 2-5 of the 2003
Coachella Valley Plan.
B. Control Measures
We recently approved the control measure portions of the 2002 SIPs
for the South Coast and Coachella Valley. The 2003 South Coast AQMP
makes minor modifications to the previously approved SCAQMD commitments
to adopt control measures. Although the 2003 South Coast AQMP includes
changes to the control measure commitments by CARB and SCAG, these new
and amended commitments apply only to the ozone portion of the plan,
and therefore are not part of this proposed action. The 2003 Coachella
Valley Plan includes no changes to the control measure commitments in
the 2002 SIP.
1. Applicable Requirements
Because the South Coast Air Basin and Coachella Valley are
classified as serious for PM-10, the nonattainment plans for these
areas must include measures that reflect a BACM level of control for
each source category that contributes significantly to a violation of
the 24-hour or annual PM-10 NAAQS.\7\ For a discussion of the BACM and
MSM provisions applicable to these areas and our determination that the
2002 SIPs for the South Coast and Coachella Valley fully met these
requirements, see the discussion in the proposed approval of the plans
at 67 FR 77215 and 67 FR 77207 (December 17, 2002).\8\
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\7\ The plans must also satisfy lesser control measure
provisions applicable to moderate areas, Reasonably Available
Control Measures (RACM) for areas sources such as fugitive dust, and
Reasonably Available Control Technology (RACT) for stationary
sources such as commercial and industrial operations. In approving
the 2002 SIPs, we did not make an independent assessment of the
plans' control measures against the RACM and RACT requirements,
since the plans would meet RACM and RACT requirements if they were
found to meet the BACM requirement.
\8\ Our final rules on the 2002 SIPs included our determination
that the CAA provisions relating to BACM (section 189(b)(1)(B)) and
MSM (section 188(e)) were fully met by the South Coast and Coachella
Valley control measures, which consisted of: (1) Enforceable
commitments to adopt and implement regulations; and (2) fully
adopted regulations and ordinances, including those fugitive dust
rules and ordinances we had previously approved (SCAQMD Rules 403,
403.1, and 1186, and Coachella Valley fugitive dust ordinances). See
68 FR 19316 and 68 FR 19318 in the final rules.
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In the 2002 SIPs for the South Coast and Coachella Valley, SCAQMD
determined which source categories are ``significant,'' as part of the
BACM analysis.\9\ Please refer to 67 FR 77215-6 and 67 FR 77207-9
(December 17, 2002) for a summary of the BACM determinations of
significant categories in the 2002 SIPs for South Coast and Coachella
Valley. Updates to the emissions inventories in the 2003 South Coast
AQMP and the 2003 Coachella Valley Plan did not change the
determinations of significant source categories in the 2002 SIPs. As a
result, the revised plans continue the prior determinations of
applicable BACM, which we approved in our April 18, 2003 final rule
(see 68 FR 19316, and 68 FR 19318). The revised plans, rules, and
ordinances strengthen the 2002 SIPs' control requirements for primary
PM and (in the case of the South Coast) the applicable secondary
precursors. Therefore, these plan updates also do not recreate the 2002
SIPs' demonstrations, pursuant to CAA section 188(e), that the plans
include the most stringent measures.\10\
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\9\ By analogy to Title I Part C of the Clean Air Act relating
to Prevention of Significant Deterioration (PSD), EPA interprets
BACM for serious PM-10 areas as generally similar to the definition
of Best Available Control Technology (BACT) for the PSD program. PM-
10 BACM is therefore defined as ``the maximum degree of emissions
reduction of PM-10 and PM-10 precursors from a source * * * which is
determined on a case-by-case basis, taking into account energy,
environmental, and economic impacts and other costs, to be
achievable for such source through application of production
processes and available methods, systems, and techniques for control
of each such pollutant.'' General Preamble Addendum, 59 FR 42010
(August 16, 1994).
EPA exempts from the BACM requirement de minimis source
categories, which do not contribute significantly to nonattainment.
EPA has generally relied on the criteria applied under the new
source permit programs (40 CFR 51.165(b)) and has therefore presumed
that a source category contributes significantly to a violation of
the 24-hour NAAQS if its impact at the location of expected
violation would exceed 5 [mu]g/m3, and would contribute
significantly to a violation of the annual NAAQS if its impact at
the time and location of the expected violation would exceed 1
[mu]g/m3. 59 FR 42011. However, states must also review
the potential to attain earlier through application of controls on
anthropogenic sources below these general levels.
\10\ SCAQMD did, as part of the plan update, review control
measures to confirm that the District's measures and commitments
continue to reflect the best and most stringent control level. See
discussions of each control measure in Appendix IV-A, which
summarizes the results of the District's survey of available control
technologies and techniques, and provides extensive documentation
and references to support the proposed control.
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Finally, the control measures in the serious area plans must be
sufficient to achieve expeditious attainment by the applicable
deadline. As discussed below, the revised SIPs update and improve the
progress and attainment provisions in the 2002 SIPs, and we propose to
conclude that the plans, as revised, continue to meet the requirements
of CAA sections 189(c) and 189(b)(1)(A) for reasonable further progress
and expeditious attainment of the PM-10 NAAQS.
2. Description of South Coast Control Measure Commitments
The South Coast 2003 AQMP relies heavily on existing, fully adopted
SCAQMD regulations to reduce primary PM-10 and secondary precursors as
needed to bring the area into attainment of the 24-hour and annual PM-
10 NAAQS. The secondary precursors in the South Coast are
NOX and, to a lesser extent, SOX, VOC, and
ammonia (NH3). The majority of these control measures have been
approved in prior actions on SCAQMD regulations submitted over the
years.\11\
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\11\ See, for example, our approval of the 1997 ozone plan and
that plan's NOX and VOC control measure commitments, as
amended in 1999 (65 FR 6091, February 8, 2000; 65 FR 18903, April
10, 2000). We have approved the District's NOX and VOC
regulations in separate rulemaking over the years. You may see
copies of the approved rules at: https://www.epa.gov/region09/air/
sips/.
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Although existing controls on primary PM-10 and secondary PM-10
precursors achieve the overwhelming majority of reductions necessary
for attainment, it is still necessary to adopt new regulations or
strengthen existing regulations in order to deliver the small
additional amount of reductions needed for attainment of the PM-10
NAAQS in
[[Page 43667]]
the South Coast. The SCAQMD's commitment to adopt new or strengthened
regulations in the 2003 South Coast AQMP is described at length in
Chapter 4 and in Appendix IV-A (District's Stationary and Mobile Source
Control Measures).
Table 1 below, entitled ``South Coast PM-10 Control Measures,''
lists the target primary PM-10, NH3, VOC, and SOX emission
reductions from each control measure commitment included in the plan.
Certain new SCAQMD control measures in the South Coast 2003 AQMP are
intended to reduce NOX emissions, but the NOX
emission reductions from these measures by 2006 are relatively small
and therefore the new NOX measures and reductions are not
included in Table 1.
Appendix IV-A provides extensive history of the control measures,
including evolution of the measures over time and progress on the
measures since the 2002 SIP. Appendix IV-A also documents the costs of
implementation, discusses technological feasibility issues, explains
the schedule for expeditious implementation, and examines other factors
as part of a comprehensive rationale for the measures.\12\
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\12\ Although the 2003 South Coast AQMP includes new and revised
State control measures in Appendix IV-B (Proposed 2003 State and
Federal Strategy for the California State Implementation Plan) and
new regional transportation strategies in Appendix IV-C (Regional
Transportation Strategy & Control Measures), these control measures
are not part of the revised PM-10 portion of the plan since they are
primarily designed to contribute emission reductions needed for
attainment of the 1-hour ozone NAAQS by 2010. We intend to rule on
these measures when we act on the ozone portion of the South Coast
2003 AQMP.
Table 1.--South Coast PM-10 Control Measures
[Source: South Coast 2003 AQMP, Appendix IV-A]
------------------------------------------------------------------------
2006 reduction
Control measure number Control measure title target in tons
per day
------------------------------------------------------------------------
Remaining 2002 SIP Control Measures
------------------------------------------------------------------------
CMB-07................... Emission Reductions from 2.1
Petroleum Refinery
Flares (SOX).
CMB-09 \1\............... Petroleum Refinery Fluid 0.1, 0
Catalytic Cracking
Units (PM-10, NH3).
WST-01 \1\............... Emission Reductions from 4.2, 8.7
Livestock Waste (VOC,
NH3).
WST-02 \1\............... Emission Reductions from 1.2, 1.9
Composting (VOC, NH3).
PRC-03 (P2).............. Emission Reductions from 0.2
Restaurant Operations
(PM-10).
--------------------------
New Control Measures
------------------------------------------------------------------------
BCM-07 \1\............... Further PM10 Reductions TBD
from Fugitive Dust
Sources (PM-10).
BCM-08 \1\............... Further Emission 0.6
Reductions from
Aggregate and Cement
Manufacturing
Operations (PM-10).
MSC-04................... Miscellaneous Ammonia TBD
Sources (NH3).
MSC-06................... Wood-Burning Fireplaces TBD
and Wood Stoves (PM-10).
TCB-01 \2\............... Transportation 0
Conformity Backstop
Measure (PM-10).
------------------------------------------------------------------------
\1\ These measures have already been adopted by SCAQMD. Revisions to
Rules 403 and 1186 fulfill BCM-07; new Rule 1127 (Emission Reductions
from Livestock Waste, adopted 8/6/04) addresses WST-01; new Rule
1133.2 (Emission Reductions from Co-Composting Operations, adopted 1/
10/03) responds to WST-02 commitments; new Rule 1105.1 (Reduction of
PM10 and Ammonia Emissions from Fluid Catalytic Cracking Units,
adopted 11/7/03) meets the CMB-09 commitment; and new Rule 1157 (PM10
Emissions Reductions from Aggregate and Related Operations, adopted 1/
07/05) fulfills the BCM-08 commitment.
\2\ This measure, which is intended to achieve reductions in PM-10 after
the 2006 attainment date, is discussed below and in Section II.G.,
Motor Vehicle Emission Budgets.
Table 2 below, entitled ``South Coast Emission Reduction
Commitments,'' presents the enforceable SCAQMD commitments to adopt and
implement measures by specific dates to achieve particular emission
reductions. This table is derived from Table 4-8A in the South Coast
2003 AQMP, and includes the commitments for the remaining 3 years of
the South Coast PM-10 attainment demonstration.
Table 2.--South Coast Emission Reduction Commitments Commitments To Adopt and Implement New Measures To Achieve Emission Reductions in Tons per Day From
2010 Planning Inventory
[Source: South Coast 2003 AQMP, Table 4-8A]
--------------------------------------------------------------------------------------------------------------------------------------------------------
VOC PM-10 NOX SOX
Year -------------------------------------------------------------------------------------------------------
Adopt Impl Adopt Impl Adopt Impl Adopt Impl
--------------------------------------------------------------------------------------------------------------------------------------------------------
2004............................................ 2.0 0 1.7 0 3.0 0 2.1 0
2005............................................ 2.0 0 0 0.16 2.1 0 0 2.1
2006............................................ 0 4.8 0 0.86 0 0 0 0
--------------------------------------------------------------------------------------------------------------------------------------------------------
[[Page 43668]]
The emission reduction targets shown in Table 1 and the emission
reduction commitments shown in Table 2 are intended to update and
replace those in the 2002 SIP, reflecting recent progress in the
development of the measures.\13\
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\13\ SCAQMD has now adopted regulations fulfilling the following
commitments in the 2002 SIP: BCM-01, BCM-03, BCM-04, BCM-06, BCM-08,
CMB-09, PRC-01, WST-01, and WST-02. It should be noted that the
NOX reductions from the committal measures in the South
Coast 2003 AQMP, as displayed in Table 2, are not relied on for
progress or attainment, but will contribute to maintenance of the
PM-10 NAAQS in the period after 2006.
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The 2003 South Coast AQMP includes one measure applicable to the
post-2006 period. In order to ensure that growth in transportation
related emissions in future years does not jeopardize continued
attainment of the PM-10 NAAQS, SCAQMD adopted TCB-01--Transportation
Conformity Budget Backstop Measure. This measure consists of a
commitment to adopt further PM-10 controls no later than 2019 to
achieve as much as 9 tons per day of additional PM-10 emission
reductions by 2020, and to adopt still more PM-10 controls no later
than 2029 to achieve as much as 16 tons per day of additional PM-10
emission reductions by 2030. Under the measure, SCAQMD will be
responsible for implementing further fugitive dust rules and SCAG will
be responsible for developing and achieving additional emission
reductions from the Regional Transportation Plan and Transportation
Control Measures. Further details on this committal measure may be
found in Appendix IV-A, pages IV-119 through IV-121.
3. Proposed Action on South Coast Control Measures
Inasmuch as the South Coast 2003 AQMP presents minor updates,
refinements, and enhancements of the South Coast control measures in
the 2002 SIP, we propose to approve them under CAA section 110(k)(3),
as meeting the requirements of CAA sections 110(a), 188(e), and
189(b)(1)(B), and remaining consistent with attainment as expeditiously
as practicable. We are proposing to approve each of the control measure
commitments in Table 1 and the overall SCAQMD commitment in Table 2 to
adopt and implement rules by specified dates to achieve particular
emission reductions. We propose that these updated commitments
supersede and replace the commitments for the same measures in the 2002
SIP for the South Coast.\14\
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\14\ The previously approved commitments for these measures are
shown in Table 1 of our proposed action on the 2002 SIP for PM-10
(67 FR 77216, December 17, 2002) and, for secondary precursors to
PM-10, in Table 2 of our proposed action on the ozone SIP (65 FR
6096, February 8, 2000; final rule 65 FR 18903, April 10, 2000). It
should be noted that the 2003 South Coast AQMP uses updated baseline
and projected emissions inventories and control factors, and so the
emission reductions targets in this new plan are calculated using
different currencies from the approved ozone and PM-10 SIPs.
Moreover, the 2003 South Coast AQMP committal measures reflect in
the baseline and projected emissions inventories all reductions that
have already been accomplished by SCAQMD regulations adopted
subsequent to the submittal of the earlier SIPs.
Commitments approved by EPA under CAA section 110(k)(3) are
enforceable by EPA and citizens under CAA sections 113 and 304,
respectively. In the past, we have approved enforceable commitments
and courts have enforced those actions against states that failed to
comply with their commitments. For further discussion and citation,
please see 69 FR 5427 (February 4, 2004) and 69 FR 30029 (May 26,
2004).
We consider 3 factors in determining whether to approve
enforceable commitments: (a) Whether the commitment addresses a
limited portion of the statutorily-required program; (b) whether the
state is capable of fulfilling its commitment; and (c) whether the
commitment is for a reasonable and appropriate period of time. In
the case of this update to the 2002 SIP for the South Coast, the
number of commitments and the associated emission reductions are
considerably reduced, because of continued successful SCAQMD rule
adoption, leaving relatively few reductions to be accomplished in
future, as shown in Table 2. The commitments represent a small
percent of the required emission reductions from the 1997 base year.
For example, the NOX commitments are not required for
attainment but rather contribute toward post-2006 maintenance of the
PM-10 NAAQS, and the VOC commitments are 1.0% of the VOC emission
reductions achieved from the 1997 base year through the 2006
attainment year. The SCAQMD has demonstrated its diligence in
fulfilling commitments generally and, in the case of the commitments
in this plan, the SCAQMD had adopted in regulatory form 5 of the 10
commitments by August 2004, including all the most significant PM-10
measures. We believe that the schedule for adopting and implementing
the measures is for a reasonable and appropriate period of time,
given the complex and challenging nature of the control measures.
Finally, the adoption and implementation schedule in the commitments
is consistent with the SCAQMD's ability to make expeditious progress
toward attainment of the standards.
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As noted above, the 2003 Coachella Valley Plan contains no new
control measure commitments, but relies on the adopted revisions to
Rules 403 and 403.1 and the local ordinances.
C. Regulations and Ordinances
The principal fugitive dust regulations in the South Coast and
Coachella Valley are two SCAQMD rules: Rule 403--``Fugitive Dust'' and
Rule 1186--``PM10 Emissions from Paved and Unpaved Roads and Livestock
Operations.'' Attainment of the PM-10 NAAQS in Coachella Valley also
depends on emission reductions from SCAQMD Rule 403.1--``Supplemental
Fugitive Dust Control Requirements for Coachella Valley Sources'' and
fugitive dust control ordinances adopted by Riverside County and 9
cities within the Coachella Valley. Attainment of the PM-10 NAAQS in
the South Coast also requires NH3 and VOC reductions from livestock
waste operations, and SCAQMD adopted on August 6, 2004, a new SCAQMD
Rule 1127--``Emission Reductions from Livestock Waste'' to accomplish
these reductions.\15\
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\15\ On July 21, 2004 (69 FR 43518), we approved new SCAQMD
Rules 1133, 1133.1, and 1133.2, adopted on January 10, 2003,
establishing VOC and NH3 controls on composting operations. We
intend to act on Rule 1127 in separate rulemaking, once the rule is
submitted. These rules contribute reductions required as part of the
South Coast PM-10 NAAQS attainment demonstration.
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In this action, we are proposing to approve recently adopted
amendments strengthening Rules 403, 403.1, and 1186, and more stringent
fugitive dust control ordinances adopted by the 10 Coachella Valley
jurisdictions. These regulations and ordinances were adopted in
fulfillment of emission reduction commitments in the 2002 SIPs for the
South Coast and Coachella, and in the 2003 South Coast AQMP.
The docket for this rulemaking includes the complete SIP submittal
package, including the current rule text, strike-out/underline rule
text highlighting rule amendments, and the SCAQMD Staff Report, which
provides information on the regulatory background, rule purpose and
applicability, affected sources, legal authority, changes in the rules
and implementation handbooks, estimation of emissions and emission
reductions, cost and cost-effectiveness estimates, and summary of
public comments and SCAQMD response. The Staff Report and supplementary
materials on revised Rules 403, 403.1, and 1186 may also be found at:
https://www.aqmd.gov/hb/2004/040438a.html.
1. Description of Regulations and Ordinances
a. SCAQMD Rule 403--Fugitive Dust
Rule 403 applies to any land use or activity that has the potential
to generate fugitive dust, including construction and agricultural
activities. SCAQMD originally adopted Rule 403 in 1976, and amended the
rule in 1992, 1993, 1997, and 1998. On February 17, 2000 (65 FR 8057),
we approved Rule 403, including its two handbooks (``Rule 403
Implementation Handbook'' and ``Rule 403 Agricultural Handbook''), as
the rule was last amended in 1998.
On April 2, 2004, the SCAQMD again adopted strengthening and
clarifying amendments to the rule and handbooks, and adopted an
additional handbook--``Rule 403 Coachella Valley Agricultural
[[Page 43669]]
Handbook.'' The more significant changes include: Lowering the
threshold for construction projects subject to additional requirements
for large operations and strengthening those notification and control
requirements; requiring construction sites greater than 5 acres to
install track-out control devices; identifying conservation practices
for Coachella Valley crop producers seeking a Rule 403 exemption;
tightening provisions relating to weed abatement; and adding numerous
provisions to clarify the rule and improve its enforceability.
CARB and SCAQMD requested that we not approve into the SIP the
revised rule provision (h), relating to Ambient Air Analysis Fees.\16\
In the same correspondence, CARB and SCAQMD asked that we approve only
the following sections of the revised 403 Implementation Handbook,
which is incorporated into the rule: (1) Chapter 5--Guidance for Large
Operations; (2) Chapter 7--Test Methods; and (3) Chapter 8--On-Site
Monitoring. SCAQMD asked that we approve the entire Rule 403 Coachella
Valley Agricultural Handbook, just as we have previously approved the
entire 403 Agricultural Handbook applicable to the South Coast area (65
FR 8057).\17\
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\16\ Letter from Michael Scheible, CARB, to Wayne Nastri, USEPA,
dated November 16, 2004, and letter from Elaine Chang, SCAQMD, to
Dave Jesson, USEPA, dated September 17, 2004.
\17\ Letter from Elaine Chang, SCAQMD, to Bob Fletcher, ARB,
dated August 18, 2004.
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b. SCAQMD Rule 403.1--Supplemental Fugitive Dust Control Requirements
for Coachella Valley
SCAQMD Rule 403.1 applies to any land use or activity within the
Coachella Valley that has the potential to generate fugitive dust,
including construction activities.\18\ The rule includes especially
stringent provisions for implementation when wind speeds exceed 25
miles per hour, and the rule also serves as a backstop for local
jurisdictions' enforcement of their fugitive dust ordinances. SCAQMD
originally adopted Rule 403.1 in 1993, and amended the rule in 2000. On
December 9, 1998 (63 FR 67784), we approved Rule 403.1, including the
``403.1 Implementation Handbook,'' as originally adopted in 1993.
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\18\ Rule 403.1 was originally titled ``Wind Entrainment of
Fugitive Dust.'' The amendment adopted this year includes a change
in the rule's title to ``Supplemental Fugitive Dust Control
Requirements for Coachella Valley.''
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On April 2, 2004, the SCAQMD adopted strengthening and clarifying
amendments to the rule and ``Rule 403.1 Implementation Handbook.'' The
more significant changes include: more stringent soil stabilization
requirements for inactive construction sites; addition of a requirement
that sources not subject to a local dust control ordinance submit a
fugitive dust control plan to SCAQMD; and numerous provisions
clarifying the rule and improving its enforceability.
CARB and SCAQMD requested that we not approve into the SIP the
revised rule provision (j), relating to Fees.\19\ SCAQMD also asked
that we approve only the following sections of the revised ``Rule 403.1
Implementation Handbook,'' which is incorporated into the rule: (1)
Chapter 2--Coachella Valley Wind Monitoring; (2) Chapter 3--On-Site
Wind Monitoring Equipment; (3) Chapter 4--Fugitive Dust Control Plan
Guidance; and (4) Chapter 7--Test Methods.\20\
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\19\ Letter from Michael Scheible, CARB, to Wayne Nastri, USEPA,
dated November 16, 2004, and letter from Elaine Chang, SCAQMD, to
Dave Jesson, USEPA, dated September 17, 2004.
\20\ Letter from Elaine Chang, SCAQMD, to Bob Fletcher, ARB,
dated August 18, 2004.
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c. SCAQMD Rule 1186--PM10 Emissions From Paved and Unpaved
Roads, and Livestock Operations
SCAQMD Rule 1186 establishes controls to reduce dust from traffic
on paved and unpaved roads, from hay grinding activities, and from
access connections and feed lane at livestock operations. The rule
includes requirements for purchase of PM10 efficient street
sweepers; removal of material on roadways; curbing; treatment of
medians; and paving, stabilization, and/or speed restrictions for
unpaved roads. SCAQMD originally adopted Rule 1186 in 1997, and amended
the rule in 1998, and 1999. On February 17, 2000 (65 FR 8057), we
approved Rule 1186 as it was last amended in 1998.
On April 2, 2004, the SCAQMD adopted strengthening and clarifying
amendments to the rule. The more significant changes include: extending
street cleaning requirements to Coachella Valley and implementing
requirements for improved road shoulders.
d. Coachella Valley Local Ordinances
On February 16, 1995, the State submitted for SIP approval the
following fugitive dust ordinances adopted by the following Coachella
Valley jurisdictions on the dates shown in parentheses: City of
Cathedral City Ordinance No. 377 (2/18/93), City of Coachella Ordinance
No. 715 (10/6/93), City of Desert Hot Springs Ordinance No. 93-2 (5/18/
93), City of Indian Wells Ordinance No. 313 (2/4/93), City of Indio
Ordinance No. 1138 (3/17/93), City of La Quinta Ordinance No. 219 (12/
15/92), City of Palm Desert Ordinance No. 701 (1/14/93), City of Palm
Springs Ordinance No. 1439 (4/21/93), City of Rancho Mirage Ordinance
No. 575 (8/5/93), and County of Riverside Ordinance No. 742 (1/4/94).
On December 9, 1998 (63 FR 67784), we approved all of these ordinances.
These ordinances were based on a model fugitive dust control
ordinance developed by the Coachella Valley Association of Governments
(CVAG), local governments, and the SCAQMD. The ordinances typically
require: (1) Dust control plans for each construction project needing a
grading permit; (2) plans to pave or chemically treat unpaved surfaces
if daily vehicle trips exceed 150; (3) imposition of 15 mph speed
limits for unpaved surfaces if daily vehicle trips do not exceed 150;
(4) paving or chemical treatment of unpaved parking lots; and (5)
actions to discourage use of unimproved property by off-highway
vehicles.
Again working in cooperation with CVAG and SCAQMD, all of the
jurisdictions recently developed a more stringent model ordinance and
then adopted new replacement ordinances based on the model. The revised
ordinances improve in numerous ways the effectiveness of controls on
construction emissions and enhance the jurisdictions' various programs
for reducing reentrained dust emissions.
On November 16, 2004, CARB submitted the following new and improved
ordinances as replacements for the previously approved SIP provisions:
City of Cathedral City Ordinance No. 583 (adopted 1/14/04), City of
Coachella Ordinance No. 896 (10/8/03), City of Desert Hot Springs
Ordinance No. 2003-16 (10/7/03), City of Indian Wells Ordinance No. 545
(11/6/03), City of Indio Ordinance No. 1357 (12/3/03), City of La
Quinta Ordinance No. 391 (12/2/03), City of Palm Desert Ordinance No.
1056 (11/13/03), City of Palm Springs Ordinance No. 1639 (11/5/03),
City of Rancho Mirage Ordinances No. 855 (12/18/03) and No. 863 (4/29/
04), and County of Riverside Ordinance No. 742.1 (1/13/04).
2. Proposed Action on Regulations and Ordinances
The revisions to Rules 403, 403.1, and 1186 and the Coachella
Valley fugitive dust ordinances strengthen the SIP-approved rules and
ordinances. The rules and ordinances continue to contain adequate
enforcement provisions for ensuring compliance by regulated facilities
and the rules deliver emission reductions consistent with the South
Coast and Coachella Valley
[[Page 43670]]
progress and attainment requirements. Prior versions of these rules and
ordinances were previously determined to meet the BACM and MSM
provisions, and the rules and ordinances, as now strengthened, continue
to meet applicable CAA subpart 2 provisions.
As noted above, the SCAQMD has requested that we not approve
certain provisions of the rules and accompanying handbooks. With these
exceptions, we are proposing to approve SCAQMD Rules 403, 403.1, and
1186, including the rule handbooks (Rule 403 Implementation Handbook,
Rule 403 Coachella Valley Agricultural Handbook, and Rule 403.1
Implementation Handbook), as amended on April 2, 2004, and the
Coachella Valley fugitive dust ordinances under CAA section 110(k)(3),
as submitted on November 16, 2004, as meeting the provisions of CAA
sections 110(a), 188(e), and 189(b)(1)(B).
Finally, we are proposing to conclude that the 2003 South Coast
AQMP and the 2003 Coachella Valley Plan continue to meet BACM and MSM
control measure requirements under CAA sections 188(e) and
189(b)(1)(B), through fully adopted regulations and ordinances and (in
the case of the South Coast) a very limited number of near-term
commitments to adopt additional measures.
D. Contingency Measures
The CAA requires that the SIP include contingency measures to be
implemented if the area fails to meet progress requirements or to
attain the NAAQS by the applicable deadline. In response to this
provision, the 2003 South Coast AQMP includes two updated contingency
measures: CTY-01--Accelerated Implementation of Control Measures, and
CTY-14--Emission Reductions from Miscellaneous Sources (Weed
Abatement). These measures are discussed at length in Appendix IV-A,
Section 2, pages IV-122 through IV-133. CTY-01 includes Table 4 (page
IV-126) displaying the scheduled control measures whose implementation
could be accelerated as part of the contingency measure implementation.
Both measures have the potential to achieve significant further
reductions in PM-10 and its precursors and may be implemented quickly
to cure a SIP shortfall. Upon final federal approval, these contingency
measures would supersede and replace the contingency measures in the
2002 SIP for the South Coast.
In addition to these contingency measures, the 2003 South Coast
AQMP projects a level of excess control for years beyond 2006 for
NOX and VOC, two of the major secondary precursors to PM-10
in the South Coast. This safety margin is due to the future year
benefits of measures already adopted in regulatory form by October 31,
2002, the cutoff date for the inventories in Appendix III, Attachment
A. The extent of this cushion, which is primarily the result of fleet
turnover to meet the State's stringent mobile source emission
standards, is shown below in Table 3--``Emissions of PM-10 Precursors
in the South Coast.''
Table 3.--Emissions of PM-10 Precursors in the South Coast
[Emissions are shown in average annual tons per day]
----------------------------------------------------------------------------------------------------------------
2006 Table A- 2007 Table A- 2008 Table A- 2010 Table A-
Precursor 7 8 9 10
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NOX............................................. 950 912 873 780
VOC............................................. 698 672 658 630
----------------------------------------------------------------------------------------------------------------
Source: 2003 South Coast AQMP, Appendix III, Attachment A.
Assuming that the 2006 levels are consistent with attainment of the PM-
10 NAAQS, the declining total basinwide inventory of NOX and
VOC show additional reductions beyond those needed to maintain the
NAAQS. Thus, for the year 2008, projected emissions of NOX
are 77 tpd below the attainment level, and projected emissions of VOC
are 40 tpd below the attainment level.
We propose to approve the SCAQMD's contingency measure provisions
under CAA section 110(k)(3) as meeting the requirements of CAA section
172(c)(9). Specifically, we are proposing to approve contingency
measures CTY-01--Accelerated Implementation of Control Measures, and
CTY-04--Control of Emissions from Miscellaneous Sources (Weed
Abatement), as set forth in Section 2 of Appendix IV-A to the 2003
South Coast AQMP.
There are no new contingency measures in the 2003 Coachella Valley
Plan. Therefore, the contingency provisions in the 2002 SIP for
Coachella Valley (see 67 FR 77209) remain applicable.
E. Reasonable Further Progress (RFP) and Milestones
The plans must include quantitative milestones which are to be
achieved every 3 years until the areas are redesignated to attainment,
and which demonstrate RFP, as defined in CAA section 171(1), until the
area reaches attainment. CAA sections 172(c)(2) and 189(c).
1. South Coast
The 2003 South Coast AQMP includes projected levels of controlled
emissions, based on fully adopted regulations and enforceable schedules
for implementation of the control measure commitments. The resulting
emissions levels are shown in Table 4--``South Coast PM-10 Reasonable
Further Progress Milestones.'' Using the approaches discussed in
Section II.F.1 below, the SCAQMD modeled the emissions levels for 2006
to demonstrate that both the 24-hour and annual PM-10 NAAQS will be
attained when emissions are reduced to the levels shown for 2006.
Table 4.--South Coast PM-10 Reasonable Further Progress Milestones
[Emissions are shown in average annual tons per day]
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Pollutant 2003 2006
------------------------------------------------------------------------
PM-10......................................... 292 292
NOX........................................... 1,048 935
SOX........................................... 58 57
VOC........................................... 804 673
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Source: 2003 South Coast AQMP, Table 6-1.
We propose to approve this milestone schedule as meeting the
requirements of CAA section 189(c), since the schedule reflects
expeditious implementation of BACM and expeditious attainment of the
24-hour and annual PM-10 NAAQS. These triennial progress milestones are
the principal progress component, but the 2003 South Coast AQMP also
provides additional information regarding interim year reductions. See,
for example, Table 2 above, Table A-6 of Appendix III, and the 2005
milestone year reduction schedule for the 1-hour ozone component of the
plan (Table 6-
[[Page 43671]]
3b). We therefore propose to conclude that the 2003 South Coast AQMP
also meets the RFP provision of CAA section 172(c)(2).
2. Coachella Valley
The 2003 Coachella Valley Plan includes projected levels of
controlled emissions, based on fully adopted regulations and
enforceable schedules for implementation of the 2002 SIP's control
measure commitment. The resulting emissions levels are shown in Table
5--``Coachella Valley PM-10 Reasonable Further Progress Milestones.''
Using the approaches discussed in Section II.F.2 below, the SCAQMD
modeled the emissions levels for 2006 to demonstrate that both the 24-
hour and annual PM-10 NAAQS will be attained when emissions are reduced
to the levels shown for 2006.
Table 5.--Coachella Valley PM-10 Reasonable Further Progress Milestones
[PM-10 emissions are shown in average annual tons per day]
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2003 2006
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30.32...................................................... 29.09
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Source: 2003 Coachella Valley Plan, Tables 2-9 and 2-7.
We propose to approve this schedule as meeting the RFP and
milestone requirements of CAA section 189(c)(1), since the schedule
reflects expeditious implementation of BACM and expeditious attainment
of the 24-hour and annual PM-10 NAAQS. Specifically, we are proposing
to approve the milestone provisions in Tables 2-9 and 2-7 of the 2003
Coachella Valley Plan. Because the reductions needed for attainment
between the 2003 and 2006 milestones are small (1.23 tons per day), we
believe that interim year reduction estimates are not necessary or
meaningful, and we conclude that the plan meets the requirements of CAA
section 172(c)(2) relating to RFP.
F. Attainment Demonstration
The plans must provide detailed demonstrations (including air
quality modeling) that the specified control strategy will reduce PM-10
emissions so that the standards will be attained as soon as practicable
but no later than December 31, 2006. CAA section 189(b)(1)(A). In the
case of the South Coast and Coachella Valley, the attainment
demonstration must analyze both the 24-hour and annual NAAQS, since the
areas have historically violated both NAAQS.
1. South Coast
In the 2003 South Coast AQMP, SCAQMD primarily relied on UAMAERO-LT
modeling approach to assess control scenarios and to determine
attainment of the PM-10 NAAQS. The 2003 South Coast AQMP also employed
linear rollback of speciated particulate at 5 representative sites in
the basin.\21\ Finally, a weight-of-evidence (WOE) assessment was used
for basin grids where high concentrations were predicted. The inputs
and application of the models and the WOE analyses are described in
Chapter 2 of Appendix V (Modeling and Attainment Demonstrations) of the
2003 South Coast AQMP.
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\21\ Under the District's PM10 Technical Enhancement Program
(PTEP), SCAQMD has been measuring speciated particulate matter at
the following sites: Anaheim, Diamond Bar, Fontana, Los Angeles, and
Rubidoux. Information about the PTEP program may be found in
Appendix V to the 1997 South Coast AQMP and 2003 South Coast AQMP.
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The modeling results for 1995, 2006, and 2010 are presented in
Chapter 5 (Figure 5-1 shows maximum annual concentrations and Figure 5-
2 shows maximum 24-hour concentrations), and on pages V-2-49 to V-2-58
of Appendix V. The modeling predicts that the peak annual concentration
in 2006 with implementation of controls will be 50 [mu]g/m\3\, compared
to the 50 [mu]g/m\3\ annual PM-10 NAAQS. The modeling predicts that the
peak 24-hour concentration in 2006 with controls will be 150 [mu]g/
m\3\, compared to the 150 [mu]g/m\3\ 24-hour PM-10 NAAQS.
In contrast to other pollutants, we have not issued detailed
modeling guidelines for PM-10, nor have we established minimum
performance requirements for PM-10 modeling.\22\ We have reviewed the
SCAQMD's modeling approaches for both primary PM-10 and secondary PM-
10, using both receptor modeling and dispersion modeling. We believe
that the modeling in the 2003 South Coast AQMP provides a reasonable
basis for linking emissions with air quality, for identifying an
appropriate control strategy, and for determining whether the strategy
delivers attainment for both the 24-hour and annual PM-10 NAAQS.
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\22\ Over the years, EPA has issued some recommendations on PM-
10 modeling, including those codified at 40 CFR part 51, appendix W,
7.2.1 and 7.2.2, and those set forth in the PM-10 SIP Development
Guideline (USEPA 450/2-860001, 6/87). Although we do not set minimum
performance goals or require model performance evaluation for PM-10
modeling, SCAQMD included a performance evaluation for the UAMAERO-
LT by grid cell and monitoring site and also a performance
evaluation at each of the 5 PTEP sites for sulfate, nitrate,
ammonium, organic carbon, elemental carbon, and primary PM-10
(Appendix V, pages V-2-31 to V-2-47).
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The SCAQMD's modeling shows that the level of emissions after
implementation of the proposed set of control strategies would result
in 2006 ambient concentrations within the South Coast in attainment of
both the 24-hour and annual PM-10 NAAQS. We therefore conclude that the
air quality modeling and attainment demonstration contained in the 2003
South Coast AQMP, Chapter 5 and Appendix V, Chapter 2, are consistent
with existing EPA guidance, and we propose to approve the attainment
demonstration under CAA section 189(b)(1)(A).
2. Coachella Valley
In the 2003 Coachella Valley Plan as with the 2003 South Coast
AQMP, SCAQMD primarily relied on UAMAERO-LT modeling approach to assess
control scenarios and to determine attainment of the annual PM-10
NAAQS. The 2003 Coachella Valley Plan also employed linear rollback of
each of the significant primary source categories as part of the
demonstration of attainment of the 24-hour PM-10 NAAQS. The attainment